ILLINOIS POLLUTION CONTROL BOARD
    October 20, 2005
     
    IN THE MATTER OF: )
    )
    UIC CORRECTIONS, USEPA ) R06-5
    AMENDMENTS January 1, 2005 through ) (Identical-in-Substance Rulemaking -
    June 30, 2005) ) Land)
     
    RCRA SUBTITLE D UPDATE, USEPA ) R06-6
    AMENDMENTS (January 1, 2005 through ) (Identical-in-Substance
    June 30, 2005 and August 1, 2005) ) Rulemaking - Land)
     
    RCRA SUBTITLE C UPDATE, USEPA ) R06-7
    AMENDMENTS (January 1, 2005 through ) (Identical-in-Substance
    June 30, 2005 and August 1, 2005) ) Rulemaking - Land)
    ) (Consolidated)
     
    Proposed Rule. Proposal for Public Comment.
     
    ORDER OF THE BOARD (by G.T. Girard):
     
    SUMMARY OF TODAY’S ACTION
     
    This identical-in-substance rulemaking consists of three separate consolidated dockets.
    The rulemaking would update the Illinois underground injection control, municipal solid waste
    landfill, and hazardous waste regulations to incorporate revisions to the federal regulations. The
    federal amendments that prompted this action were made by the United States Environmental
    Protection Agency (USEPA) during the period of January 1, 2005 through June 30, 2005. This
    proceeding proposes amendments to 35 Ill. Adm. Code 720 through 725, 728, and 738. This
    proposal for public comment would also make a series of non-substantive corrections and
    stylistic revisions to segments of the text that are not otherwise affected by the covered federal
    amendments, principally to the text of 35 Ill. Adm. Code 723 and 738.
     
    This opinion and the related order propose identical-in-substance amendments in three
    distinct program areas:
     
    1. Under Sections 7.2 and 13(c) of the Environmental Protection Act (Act) (415
    ILCS 5/7.2 and 13(c) (2004)), the Board proposes amendments to the Illinois
    regulations that are “identical in substance” to underground injection control
    (UIC) regulations that the USEPA adopted to implement Section 1421 of the
    federal Safe Drinking Water Act (SDWA) (42 U.S.C. § 300h (2003)). The
    federal UIC regulations are found at 40 C.F.R. 144 through 148.
     
    2. Under Sections 7.2 and 22.40(a) of the Act (415 ILCS 5/7.2 and 22.4(a) (2004))
    require the Board to adopt regulations that are “identical in substance” to

     
    2
    municipal solid waste landfill (MSWLF) regulations adopted by the USEPA.
    These USEPA rules implement Subtitle D of the federal Resource Conservation
    and Recovery Act of 1976 (RCRA Subtitle C) (42 U.S.C. §§ 6941
    et seq
    . (2003)).
    The federal RCRA Subtitle D MSWLF regulations are found at 40 C.F.R. 258.
     
    3. Under Sections 7.2 and 22.4(a) of the Act (415 ILCS 5/7.2 and 22.4(a) (2004))
    require the Board to adopt regulations that are “identical in substance” to
    hazardous waste regulations adopted by the USEPA. These USEPA rules
    implement Subtitle C of the federal Resource Conservation and Recovery Act of
    1976 (RCRA Subtitle C) (42 U.S.C. §§ 6921
    et seq
    . (2003)). The federal RCRA
    Subtitle C hazardous waste management regulations are found at 40 C.F.R. 260
    through 266, 268, 270, 271, 273, and 279.
     
    Sections 13(c), 22.40(a), and 22.4(a) also provide that Title VII of the Act and Section 5
    of the Administrative Procedure Act (5 ILCS 100/5-35 and 5-40 (1998)) do not apply to the
    Board’s adoption of identical-in-substance regulations.
     
    This order is supported by an opinion that the Board also adopts today. The Board will
    cause the proposed amendments to be published in the
    Illinois Register
    and will hold the docket
    open to receive public comments for 45 days after the date of publication.
     
    The Clerk is directed to cause publication of the following proposed amendments in the
    Illinois Register
    :
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER b: PERMITS
     
    PART 703
    RCRA PERMIT PROGRAM
     
    SUBPART A: GENERAL PROVISIONS
    Section
    703.100 Scope and Relation to Other Parts
    703.101 Purpose
    703.110 References
     
    SUBPART B: PROHIBITIONS
    Section
    703.120 Prohibitions in General
    703.121 RCRA Permits
    703.122 Specific Inclusions in Permit Program
    703.123 Specific Exclusions from Permit Program
    703.124 Discharges of Hazardous Waste
    703.125 Reapplications

     
    3
    703.126 Initial Applications
    703.127 Federal Permits (Repealed)
     
    SUBPART C: AUTHORIZATION BY RULE AND INTERIM STATUS
    Section
    703.140 Purpose and Scope
    703.141 Permits by Rule
    703.150 Application by Existing HWM Facilities and Interim Status Qualifications
    703.151 Application by New HWM Facilities
    703.152 Amended Part A Application
    703.153 Qualifying for Interim Status
    703.154 Prohibitions During Interim Status
    703.155 Changes During Interim Status
    703.156 Interim Status Standards
    703.157 Grounds for Termination of Interim Status
    703.158 Permits for Less Than an Entire Facility
    703.159 Closure by Removal
    703.160 Procedures for Closure Determination
    703.161 Enforceable Document for Post-Closure Care
     
    SUBPART D: APPLICATIONS
    Section
    703.180 Applications in General
    703.181 Contents of Part A
    703.182 Contents of Part B
    703.183 General Information
    703.184 Facility Location Information
    703.185 Groundwater Protection Information
    703.186 Exposure Information
    703.187 Solid Waste Management Units
    703.188 Other Information
    703.191 Public Participation: Pre-Application Public Notice and Meeting
    703.192 Public Participation: Public Notice of Application
    703.193 Public Participation: Information Repository
    703.200 Specific Part B Application Information
    703.201 Containers
    703.202 Tank Systems
    703.203 Surface Impoundments
    703.204 Waste Piles
    703.205 Incinerators that Burn Hazardous Waste
    703.206 Land Treatment
    703.207 Landfills
    703.208 Boilers and Industrial Furnaces Burning Hazardous Waste
    703.209 Miscellaneous Units
    703.210 Process Vents
    703.211 Equipment

     
    4
    703.212 Drip Pads
    703.213 Air Emission Controls for Tanks, Surface Impoundments, and Containers
    703.214 Post-Closure Care Permits
     
    SUBPART E: SHORT TERM AND PHASED PERMITS
    Section
    703.220 Emergency Permits
    703.221 Alternative Compliance with the Federal NESHAPS
    703.222 Incinerator Conditions Prior to Trial Burn
    703.223 Incinerator Conditions During Trial Burn
    703.224 Incinerator Conditions After Trial Burn
    703.225 Trial Burns for Existing Incinerators
    703.230 Land Treatment Demonstration
    703.231 Research, Development and Demonstration Permits
    703.232 Permits for Boilers and Industrial Furnaces Burning Hazardous Waste
    703.234 Remedial Action Plans
     
    SUBPART F: PERMIT CONDITIONS OR DENIAL
    Section
    703.240 Permit Denial
    703.241 Establishing Permit Conditions
    703.242 Noncompliance Pursuant to Emergency Permit
    703.243 Monitoring
    703.244 Notice of Planned Changes (Repealed)
    703.245 Twenty-four Hour Reporting
    703.246 Reporting Requirements
    703.247 Anticipated Noncompliance
    703.248 Information Repository
     
    SUBPART G: CHANGES TO PERMITS
    Section
    703.260 Transfer
    703.270 Modification
    703.271 Causes for Modification
    703.272 Causes for Modification or Reissuance
    703.273 Facility Siting
    703.280 Permit Modification at the Request of the Permittee
    703.281 Class 1 Modifications
    703.282 Class 2 Modifications
    703.283 Class 3 Modifications
     
    SUBPART H: REMEDIAL ACTION PLANS
    Section
    703.300 Special Regulatory Format
    703.301 General Information
    703.302 Applying for a RAP

     
    5
    703.303 Getting a RAP Approved
    703.304 How a RAP May Be Modified, Revoked and Reissued, or Terminated
    703.305 Operating Under A RAP
    703.306 Obtaining a RAP for an Off-Site Location
     
    SUBPART I: INTEGRATION WITH MAXIMUM ACHIEVABLE CONTROL
    TECHNOLOGY (MACT) STANDARDS
    Section
    703.320 Options for Incinerators and Cement and Lightweight Aggregate Kilns to
    Minimize Emissions from Startup, Shutdown, and Malfunction Events
     
    703.Appendix A Classification of Permit Modifications
     
    AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the
    Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].
     
    SOURCE: Adopted in R82-19 at 7 Ill. Reg. 14289, effective October 12, 1983; amended in
    R83-24 at 8 Ill. Reg. 206, effective December 27, 1983; amended in R84-9 at 9 Ill. Reg. 11899,
    effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 1110, effective January 2, 1986;
    amended in R85-23 at 10 Ill. Reg. 13284, effective July 28, 1986; amended in R86-1 at 10 Ill.
    Reg. 14093, effective August 12, 1986; amended in R86-19 at 10 Ill. Reg. 20702, effective
    December 2, 1986; amended in R86-28 at 11 Ill. Reg. 6121, effective March 24, 1987; amended
    in R86-46 at 11 Ill. Reg. 13543, effective August 4, 1987; amended in R87-5 at 11 Ill. Reg.
    19383, effective November 12, 1987; amended in R87-26 at 12 Ill. Reg. 2584, effective January
    15, 1988; amended in R87-39 at 12 Ill. Reg. 13069, effective July 29, 1988; amended in R88-16
    at 13 Ill. Reg. 447, effective December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18477,
    effective November 13, 1989; amended in R89-9 at 14 Ill. Reg. 6278, effective April 16, 1990;
    amended in R90-2 at 14 Ill. Reg. 14492, effective August 22, 1990; amended in R90-11 at 15 Ill.
    Reg. 9616, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14554, effective September
    30, 1991; amended in R91-13 at 16 Ill. Reg. 9767, effective June 9, 1992; amended in R92-10 at
    17 Ill. Reg. 5774, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20794, effective
    November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6898, effective April 26, 1994; amended
    in R94-7 at 18 Ill. Reg. 12392, effective July 29, 1994; amended in R94-5 at 18 Ill. Reg. 18316,
    effective December 20, 1994; amended in R95-6 at 19 Ill. Reg. 9920, effective June 27, 1995;
    amended in R95-20 at 20 Ill. Reg. 11225, effective August 1, 1996; amended in R96-10/R97-
    3/R97-5 at 22 Ill. Reg. 553, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg.
    7632, effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17930, effective
    September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 2153, effective January 19,
    1999; amended in R99-15 at 23 Ill. Reg. 9381, effective July 26, 1999; amended in R00-13 at 24
    Ill. Reg. 9765, effective June 20, 2000; amended in R01-21/R01-23 at 25 Ill. Reg. 9313,
    effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. 6539, effective April 22,
    2002; amended in R03-7 at 27 Ill. Reg. 3496, effective February 14, 2003; amended in R03-18 at
    27 Ill. Reg. 12683, effective July 17, 2003; amended in R05-8 at 29 Ill. Reg. 5966, effective
    April 13,
    2005; amended in R06-5/R06-6/R06-7 at 30 Ill. Reg. ________, effective
    ______________________.

     
    6
     
    SUBPART C: AUTHORIZATION BY RULE AND INTERIM STATUS
     
    Section 703.140 Purpose and Scope
     
    a) The Sections of this Subpart C are divided into the following two groups:
     
    1) Section 703.141, (Permits by Rule); and
     
    2) Sections 703.151 through 703.158, relating to interim status;
     
    b) The interim status rules correspond to subpart G of 40 CFR 270, Subpart G,
    which relates to interim status. Other portions of the federal rules may be found
    in Subpart B of this Part. The intent is to group the interim status rules so they
    can be more easily ignored by those to whom they do not apply, and so they can
    be conveniently repealed after the interim status period.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.141 Permits by Rule
     
    Notwithstanding any other provision of this Part or 35 Ill. Adm. Code 705, the following must be
    deemed to have a RCRA permit if the conditions listed are met:
     
    a) Ocean disposal barges or vessels. The owner or operator of a barge or other
    vessel that accepts hazardous waste for ocean disposal, if the owner or operator
    does the following:
     
    1) It has a permit for ocean dumping issued by USEPA under 40 CFR 220,
    incorporated by reference in 35 Ill. Adm. Code 720.111;
     
    2) It complies with the conditions of that permit; and
     
    3) It complies with the following hazardous waste regulations, incorporated
    by reference in 35 Ill. Adm. Code 720.111:
     
    A) 40 CFR 264.11, 35 Ill. Adm. Code 724.111 (USEPA Identification
    number Number);
     
    B) 40 CFR 264.71, 35 Ill. Adm. Code 724.171 (Use of manifest
    system Manifest System);
     
    C) 40 CFR 264.72, 35 Ill. Adm. Code 724.172 (Manifest
    discrepancies Discrepancies);
     
    D) 40 CFR 264.73(a) and (b)(1), 35 Ill. Adm. Code 724.173(a) and

     
    7
    (b)(1) (Operating record Record);
     
    E) 40 CFR 264.75, 35 Ill. Adm. Code 724.175 (Biennial report
    Report); and
     
    F) 40 CFR 264.76, 35 Ill. Adm. Code 724.176, (Unmanifested waste
    report Waste Report);
     
    b) Injection wells. The owner or operator of an underground injection well
    disposing of hazardous waste, if the owner or operator fulfills the following
    conditions:
     
    1) It has a permit for underground injection issued under 35 Ill. Adm. Code
    704; and
     
    2) It complies with the conditions of that permit and the requirements of
    Subpart F of 35 Ill. Adm. Code 704 (requirements for wells managing
    hazardous waste); and
     
    3) For UIC permits issued after November 8, 1984, the following:
     
    A) It complies with 35 Ill. Adm. Code 724.201; and
     
    B) Where the UIC well is the only unit at the facility that requires a
    RCRA permit, it complies with Section 703.187.
     
    c) Publicly owned treatment works (POTW). The owner or operator of a POTW
    that accepts for treatment hazardous waste, if the owner or operator fulfills the
    following conditions:
     
    1) It has an NPDES permit;
     
    2) It complies with the conditions of that permit; and
     
    3) It complies with the following regulations:
     
    A) 35 Ill. Adm. Code 724.111, (Identification number Number);
     
    B) 35 Ill. Adm. Code 724.171, (Use of manifest system Manifest
    System);
     
    C) 35 Ill. Adm. Code 724.172, (Manifest discrepencies discrepancies;
     
    D) 35 Ill. Adm. Code 724.173(a) and (b)(1), (Operating record
    Record);
     

     
    8
    E) 35 Ill. Adm. Code 724.175, (Annual report Report);
     
    F) 35 Ill. Adm. Code 724.176, (Unmanifested waste report Waste
    Report); and
     
    G) For NPDES permits issued after November 8, 1984, 35 Ill. Adm.
    Code 724.201 (Corrective Action for Solid Waste Management
    Units); and
     
    4) If the waste meets all federal, it complies with State and local pretreatment
    requirements that would be applicable to the waste if it were being
    discharged into the POTW through a sewer, pipe, or similar conveyance.
     
    BOARD NOTE: Illinois pretreatment requirements are codified in 35 Ill.
    Adm. Code 307 and 310.
     
    BOARD NOTE: See 40 CFR 270.60 (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.153 Qualifying for Interim Status
     
    a) Any person who owns or operates an existing HWM facility or a facility in
    existence on the effective date of statutory or regulatory amendments that render
    the facility subject to the requirement to have a RCRA permit must have interim
    status and must be treated as having been issued a permit to the extent he or she
    has fulfilled the following requirements:
     
    1) Complied
    The owner or operator has complied with the requirements of
    Section 3010(a) of the federal Resource Conservation and Recovery Act
    (42 USC 6930(a)) pertaining to notification of hazardous waste activity;
     
    BOARD NOTE: Some existing facilities may not be required to file a
    notification under Section 3010(a) of the federal Resource Conservation
    and Recovery Act (42 USC 6930(a)). These facilities may qualify for
    interim status by meeting subsection (a)(2).
     
    2) Complied
    The owner or operator has complied with the requirements of
    Sections 703.150 and 703.152 governing submission of Part A
    applications;
     
    b) Failure to qualify for interim status. If the Agency has reason to believe upon
    examination of a Part A application that it the Part A application fails to meet the
    requirements of 35 Ill. Adm. Code 702.123 or 703.181, it must notify the owner
    or operator in writing of the apparent deficiency. Such notice must specify the
    grounds for the Agency’s belief that the application is deficient. The owner or

     
    9
    operator must have 30 days from receipt to respond to such a notification and to
    explain or cure the alleged deficiency in its Part A application. If, after such
    notification and opportunity for response, the Agency determines that the
    application is deficient it may take appropriate enforcement action.
     
    c) Subsection (a) of this Section must not apply to any facility that has been
    previously denied a RCRA permit or if authority to operate the facility under the
    federal Resource Conservation and Recovery Act (42 USC 6901 et seq.) has been
    previously terminated.
     
    BOARD NOTE: Derived from 40 CFR 270.70 (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.155 Changes During Interim Status
     
    a) Except as provided in subsection (b), of this Section the owner or operator of an
    interim status facility may make the following changes at the facility:
     
    1) Treatment, storage, or disposal of new hazardous wastes not previously
    identified in Part A of the permit application (and, in the case of newly
    listed or identified wastes, addition of the units being used to treat, store,
    or dispose of the hazardous wastes on the date of the listing or
    identification) if the owner or operator submits a revised Part A permit
    application prior to such treatment, storage, or disposal;
     
    2) Increases in the design capacity of processes used at the facility if the
    owner or operator submits a revised Part A permit application prior to
    such a change (along with a justification explaining the need for the
    change) and the Agency approves the change because either of the
    following conditions exist:
     
    A) There is a lack of available treatment, storage, or disposal capacity
    at other hazardous waste management facilities; or
     
    B) The change is necessary to comply with a federal, State, or local
    requirement, including 35 Ill. Adm. Code 725, 728, or 729;
     
    3) Changes in the processes for the treatment, storage, or disposal of
    hazardous waste may be made at a facility or addition of processes if the
    owner or operator submits a revised Part A permit application prior to
    such a change (along with a justification explaining the need for change)
    and the Agency approves the change because either of the following
    conditions exist:
     
    A) The change is necessary to prevent a threat to human health or the

     
    10
    environment because of an emergency situation; or
     
    B) The change is necessary to comply with a federal, State, or local
    requirement, including 35 Ill. Adm. Code 725, 728, or 729;
     
    4) Changes in the ownership or operational control of a facility if the new
    owner or operator submits a revised Part A permit application no later
    than 90 days prior to the scheduled change. When a transfer of ownership
    or operational control of a facility occurs, the old owner or operator must
    comply with the requirements of Subpart H of 35 Ill. Adm. Code 725
    (financial requirements), until the new owner or operator has
    demonstrated to the Agency that it is complying with the requirements of
    that Subpart. The new owner or operator must demonstrate compliance
    with the financial assurance requirements within six months after the date
    of the change in the ownership or operational control of the facility. Upon
    demonstration to the Agency by the new owner or operator of compliance
    with the financial assurance requirements, the Agency must notify the old
    owner or operator in writing that the old owner or operator no longer
    needs to comply with Subpart H of 35 Ill. Adm. Code 725 as of the date of
    demonstration. All other interim status duties are transferred effective
    immediately upon the date of the change of ownership or operational
    control of the facility;
     
    5) Changes made in accordance with an interim status corrective action order
    issued by: USEPA under Section 3008(h) of the federal Resource
    Conservation and Recovery Act (42 USC 6901 et seq.) or other federal
    authority; a court pursuant to a judicial action brought USEPA; a court
    pursuant to the Environmental Protection Act; or the Board. Changes
    under this subsection (a)(5) are limited to the treatment, storage, or
    disposal of solid waste from releases that originate within the boundary of
    the facility;
     
    6) Addition of newly regulated units for the treatment, storage, or disposal of
    hazardous waste if the owner or operator submits a revised Part A permit
    application on or before the date on which the unit becomes subject to the
    new requirements.
     
    b) Except as specifically allowed under this subsection (b), changes listed under
    subsection (a) of this Section must not be made if they amount to reconstruction
    of the HWM facility. Reconstruction occurs when the capital investment in the
    changes to the facility exceeds fifty percent of the capital cost of a comparable
    entirely new HWM facility. If all other requirements are met, the following
    changes may be made even if they amount to a reconstruction:
     
    1) Changes made solely for the purpose of complying with requirements of
    35 Ill. Adm. Code 725.293 for tanks and ancillary equipment.

     
    11
     
    2) If necessary to comply with federal, State or local requirements, including
    35 Ill. Adm. Code 725, 728, or 729, changes to an existing unit, changes
    solely involving tanks or containers, or addition of replacement surface
    impoundments that satisfy the statutory standards of Section 35 Ill. Adm.
    Code 728.139.
     
    3) Changes that are necessary to allow an owner or operator to continue
    handling newly listed or identified hazardous wastes that have been
    treated, stored or disposed of at the facility prior to the effective date of
    the rule establishing the new listing or identification.
     
    4) Changes during closure of a facility or of a unit within a facility made in
    accordance with an approved closure plan.
     
    5) Changes necessary to comply with an interim status corrective action
    order issued by: USEPA under Section 3008(h) of the federal Resource
    Conservation and Recovery Act (42 USC 6930(a)) or other federal
    authority; a court pursuant to a judicial action brought by USEPA; a court
    pursuant to the Environmental Protection Act; or the Board. Changes
    under this subsection (b)(5) are limited to the treatment, storage, or
    disposal of solid waste from releases that originate within the boundary of
    the facility.
     
    6) Changes to treat or store, in tanks, containers, or containment buildings,
    hazardous wastes subject to land disposal restrictions imposed in 35 Ill.
    Adm. Code 728, provided that such changes are made solely for the
    purpose of complying with 35 Ill. Adm. Code 728.
     
    7) Addition of newly regulated units under subsection (a)(6) of this Section.
     
    8) Changes necessary to comply with the federal Clean Air Act (CAA)
    Maximum Achievable Control Technology (MACT) emissions standards
    of subpart EEE of 40 CFR 63, Subpart EEE--(National Emission
    Standards for Hazardous Air Pollutants From from Hazardous Waste
    Combustors), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    BOARD NOTE: Derived from 40 CFR 270.72 (2002) (2005). The federal CAA MACT
    standards are directly implemented in Illinois pursuant to Section 39.5 of the Environmental
    Protection Act [415 ILCS 5/39.5].
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    12
    SUBPART D: APPLICATIONS
     
    Section 703.185 Groundwater Protection Information
     
    The following additional information regarding protection of groundwater is required from an
    owner or operator of a hazardous waste facility containing a regulated unit, except as provided in
    35 Ill. Adm. Code 724.190(b):
     
    a) A summary of the groundwater monitoring data obtained during the interim status
    period under 35 Ill. Adm. Code 725.190 through 725.194, where applicable;
     
    b) Identification of the uppermost aquifer and aquifers hydraulically interconnected
    beneath the facility property, including groundwater flow direction and rate, and
    the basis for such identification (i.e., the information obtained from hydrogeologic
    investigations of the facility area);
     
    c) On the topographic map required under Section 703.183(s), a delineation of the
    waste management area, the property boundary, the proposed “point of
    compliance” as defined under 35 Ill. Adm. Code 724.195, the proposed location
    of groundwater monitoring wells as required under 35 Ill. Adm. Code 724.197
    and, to the extent possible, the information required in subsection (b) of this
    Section;
     
    d) A description of any plume of contamination that has entered the groundwater
    from a regulated unit at the time that the application is submitted that does the
    following:
     
    1) It delineates the extent of the plume on the topographic map required
    under Section 703.183(s);
     
    2) It identifies the concentration of each Appendix I to 35 Ill. Adm. Code 724
    constituent throughout the plume or identifies the maximum
    concentrations of each Appendix I to 35 Ill. Adm. Code 724 constituent in
    the plume;
     
    e) Detailed plans and an engineering report describing the proposed groundwater
    monitoring program to be implemented to meet the requirements of 35 Ill. Adm.
    Code 724.197;
     
    f) If the presence of hazardous constituents has not been detected in the groundwater
    at the time of permit application, the owner or operator must submit sufficient
    information, supporting data and analyses to establish a detection monitoring
    program that meets the requirements of 35 Ill. Adm. Code 724.198. This
    submission must address the following items as specified under that Section:
     
    1) A proposed list of indicator parameters, waste constituents or reaction

     
    13
    products that can provide a reliable indication of the presence of
    hazardous constituents in the groundwater;
     
    2) A proposed groundwater monitoring system;
     
    3) Background values for each proposed monitoring parameter or
    constituent, or procedures to calculate such values; and
     
    4) A description of proposed sampling, analysis, and statistical comparison
    procedures to be utilized in evaluating groundwater monitoring data;
     
    g) If the presence of hazardous constituents has been detected in the groundwater at
    the point of compliance at the time of permit application, the owner or operator
    must submit sufficient information, supporting data and analyses to establish a
    compliance monitoring program that meets the requirements of 35 Ill. Adm. Code
    724.199. Except as provided in 35 Ill. Adm. Code 724.198(h)(5), the owner or
    operator must also submit an engineering feasibility plan for a corrective action
    program necessary to meet the requirements of 35 Ill. Adm. Code 724.200, unless
    the owner or operator obtains written authorization in advance from the Agency
    to submit a proposed permit schedule for submittal of such a plan. To
    demonstrate compliance with 35 Ill. Adm. Code 724.199, the owner or operator
    must address the following items:
     
    1) A description of the wastes previously handled at the facility;
     
    2) A characterization of the contaminated groundwater, including
    concentrations of hazardous constituents;
     
    3) A list of hazardous constituents for which compliance monitoring will be
    undertaken in accordance with 35 Ill. Adm. Code 724.197 and 724.199;
     
    4) Proposed concentration limits for each hazardous constituent, based on the
    criteria set forth in 35 Ill. Adm. Code 724.194(a), including a justification
    for establishing any alternate concentration limits;
     
    5) Detailed plans and an engineering report describing the proposed
    groundwater monitoring system, in accordance with the requirements of
    35 Ill. Adm. Code 724.197; and
     
    6) A description of proposed sampling, analysis, and statistical comparison
    procedures to be utilized in evaluating groundwater monitoring data;
     
    h) If hazardous constituents have been measured in the groundwater that exceed the
    concentration limits established under 35 Ill. Adm. Code 724.194, Table 1, or if
    groundwater monitoring conducted at the time of permit application under 35 Ill.
    Adm. Code 725.190 through 725.194 at the waste boundary indicates the

     
    14
    presence of hazardous constituents from the facility in groundwater over
    background concentrations, the owner or operator must submit sufficient
    information, supporting data, and analyses to establish a corrective action
    program that meets the requirements of 35 Ill. Adm. Code 724.200. However, an
    owner or operator is not required to submit information to establish a corrective
    action program if it demonstrates to the Agency that alternate concentration limits
    will protect human health and the environment after considering the criteria listed
    in 35 Ill. Adm. Code 724.194(b). An owner or operator who is not required to
    establish a corrective action program for this reason must instead submit
    sufficient information to establish a compliance monitoring program that meets
    the requirements of subsection (f) and 35 Ill. Adm. Code 724.199. To
    demonstrate compliance with 35 Ill. Adm. Code 724.200, the owner or operator
    must address, at a minimum, the following items:
     
    1) A characterization of the contaminated groundwater, including
    concentrations of hazardous constituents;
     
    2) The concentration limit for each hazardous constituent found in the
    groundwater, as set forth in 35 Ill. Adm. Code 724.194;
     
    3) Detailed plans and an engineering report describing the corrective action
    to be taken; and
     
    4) A description of how the groundwater monitoring program will assess the
    adequacy of the corrective action.
     
    5) The permit may contain a schedule for submittal of the information
    required in subsections (h)(3) and (h)(4) of this Section, provided the
    owner or operator obtains written authorization from the Agency prior to
    submittal of the complete permit application.
     
    BOARD NOTE: See Derived from 40 CFR 270.14(c) (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.204 Waste Piles
     
    For a facility that stores or treats hazardous waste in waste piles, except as otherwise provided in
    35 Ill. Adm. Code 724.101, the Part B application must include the following:
     
    a) A list of hazardous wastes placed or to be placed in each waste pile;
     
    b) If an exemption is sought to 35 Ill. Adm Adm. Code 724.351 and Subpart F of 35
    Ill. Adm. Code 724, as provided by 35 Ill. Adm. Code 724.350(c) or
    724.190(b)(2), an explanation of how the requirements of 35 Ill. Adm. Code
    724.350(c) will be complied with or detailed plans and an engineering report

     
    15
    describing how the requirements of 35 Ill. Adm. Code 724.190(b)(2) will be met;
     
    c) Detailed plans and an engineering report describing how the pile is designed and
    is or will be constructed, operated and maintained to meet the requirements of 35
    Ill. Adm. Code 724.119, 724.351, 724.352, and 724.353, addressing the following
    items:
     
    1) Liner, leak detection, and removal system.
     
    A) The liner system (except for an existing portion of a waste pile), if
    the waste pile must meet the requirements of 35 Ill. Adm. Code
    724.351(a). If an exemption from the requirement for a liner is
    sought, as provided by 35 Ill. Adm. Code 724.351(b), the owner or
    operator must submit a copy of the Board order granting an
    adjusted standard pursuant to 35 Ill. Adm. Code 724.351(b);
     
    B) The double liner and leak (leachate) detection, collection and
    removal system, if the waste pile must meet the requirements of 35
    Ill. Adm. Code 724.351(c). If an exemption from the requirements
    for double liners and a leak detection, collection, and removal
    system or alternative design is sought as provided by 35 Ill. Adm.
    Code 724.351(d), (e), or (f), submit appropriate information;
     
    C) If the leak detection system is located in a saturated zone, submit
    detailed plans and an engineering report explaining the leak
    detection system design and operation, and the location of the
    saturated zone in relation to the leak detection system;
     
    D) The CQA plan, if required under 35 Ill. Adm. Code 724.119;
     
    E) Proposed action leakage rate, with rationale, if required under 35
    Ill. Adm. Code 724.352, and response action plan, if required
    under 35 Ill. Adm. Code 724.353;
     
    2) Control of run-on;
     
    3) Control of run-off;
     
    4) Management of collection and holding units associated with run-on and
    run-off control systems; and
     
    5) Control of wind dispersal of particulate matter, where applicable;
     
    d) A description of how each waste pile, including the double liner system, leachate
    collection and removal system, leak detection system, cover system, and
    appurtenances for control of run-on and run-off, will be inspected in order to meet

     
    16
    the requirements of 35 Ill. Adm. Code 724.354(a), (b), and (c). This information
    must be included in the inspection plan submitted under Section 703.183(e).
    e) If the treatment is carried out on or in the pile, details about the process and
    equipment used, and the nature and quality of the residuals;
     
    f) If ignitable or reactive wastes are to be placed in a waste pile, an explanation of
    how the requirements of 35 Ill. Adm. Code 724.356 will be complied with;
     
    g) If incompatible wastes, or incompatible wastes and materials, will be placed in a
    waste pile, an explanation of how 35 Ill. Adm. Code 724.357 will be complied
    with;
     
    h) A description of how hazardous waste residues and contaminated materials will
    be removed from the waste pile at closure, as required under 35 Ill. Adm. Code
    724.358(a). For any waste not to be removed from the waste pile upon closure,
    the owner or operator must submit detailed plans and an engineering report
    describing how 35 Ill. Adm. Code 724.410(a) and (b) will be complied with. This
    information must be included in the closure plan and, where applicable, the post-
    closure plan submitted under Section 703.183(m); and
     
    i) A waste management plan for hazardous waste numbers F020, F021, F022, F023,
    F026, and F027 describing how the surface impoundment is or will be designed,
    constructed, operated, and maintained to meet the requirements of 35 Ill. Adm.
    Code 724.359. This submission must address the following items as specified in
    that Section:
     
    1) The volume, physical, and chemical characteristics of the wastes,
    including their potential to migrate through soil or to volatilize or escape
    into the atmosphere;
     
    2) The attenuative properties of underlying and surrounding soils or other
    materials;
     
    3) The mobilizing properties of other materials co-disposed with these
    wastes; and
     
    4) The effectiveness of additional treatment, design, or monitoring
    techniques.
     
    BOARD NOTE: Derived from 40 CFR 270.18 (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.205 Incinerators that Burn Hazardous Waste
     
    For a facility that incinerates hazardous waste, except as 35 Ill. Adm. Code 724.440 and

     
    17
    subsection (e) of this Section provide otherwise, the applicant must fulfill the requirements of
    subsection (a), (b), or (c) of this Section in completing the Part B application.
     
    a) When seeking exemption under 35 Ill. Adm. Code 724.440(b) or (c) (ignitable,
    corrosive, or reactive wastes only), the following requirements:
     
    1) Documentation that the waste is listed as a hazardous waste in Subpart D
    of 35 Ill. Adm. Code 721 solely because it is ignitable (Hazard Code I),
    corrosive (Hazard Code C), or both;
     
    2) Documentation that the waste is listed as a hazardous waste in Subpart D
    of 35 Ill. Adm. Code 721 solely because it is reactive (Hazard Code R) for
    characteristics other than those listed in 35 Ill. Adm. Code 721.123(a)(4)
    and (a)(5) and will not be burned when other hazardous wastes are present
    in the combustion zone;
     
    3) Documentation that the waste is a hazardous waste solely because it
    possesses the characteristic of ignitability or corrosivity, or both, as
    determined by the tests for characteristics of hazardous wastes under
    Subpart C of 35 Ill. Adm. Code 721; or
     
    4) Documentation that the waste is a hazardous waste solely because it
    possesses the reactivity characteristics listed in 35 Ill. Adm. Code
    721.123(a)(1) through (a)(3) or (a)(6) through (a)(8), and that it will not be
    burned when other hazardous wastes are present in the combustion zone.
     
    b) Submit a trial burn plan or the results of a trial burn, including all required
    determinations, in accordance with Section 703.222 et seq.
     
    c) In lieu of a trial burn, the applicant may submit the following information:
     
    1) An analysis of each waste or mixture of wastes to be burned including the
    following:
     
    A) Heat value of the waste in the form and composition in which it
    will be burned;
     
    B) Viscosity (if applicable) or description of physical form of the
    waste;
     
    C) An identification of any hazardous organic constituents listed in
    Appendix H to 35 Ill. Adm. Code 721 that are present in the waste
    to be burned, except that the applicant need not analyze for
    constituents listed in Appendix H to 35 Ill. Adm. Code 721 that
    would reasonably not be expected to be found in the waste. The
    constituents excluded from analysis must be identified and the

     
    18
    basis for their exclusion stated. The waste analysis must rely on
    appropriate analytical techniques specified in “Test Methods for
    the Evaluation of Solid Waste, Physical/Chemical Methods,”
    USEPA Publication SW-846, as incorporated by reference at 35 Ill.
    Adm. Code 720.111, or their equivalent;
     
    D) An approximate quantification of the hazardous constituents
    identified in the waste, within the precision produced by the
    appropriate analytical methods specified in “Test Methods for the
    Evaluation of Solid Waste, Physical/Chemical Methods,” USEPA
    Publication SW-846, as incorporated by reference at 35 Ill. Adm.
    Code 720.111; and
     
    E) A quantification of those hazardous constituents in the waste that
    may be designated as POHCs based on data submitted from other
    trial or operational burns that demonstrate compliance with the
    performance standard in 35 Ill. Adm. Code 724.443;
     
    2) A detailed engineering description of the incinerator, including the
    following:
     
    A) Manufacturer’s name and model number of incinerator;
     
    B) Type of incinerator;
     
    C) Linear dimension of incinerator unit including cross sectional area
    of combustion chamber;
     
    D) Description of auxiliary fuel system (type/feed);
     
    E) Capacity of prime mover;
     
    F) Description of automatic waste feed cutoff systems;
     
    G) Stack gas monitoring and pollution control monitoring system;
     
    H) Nozzle and burner design;
     
    I) Construction materials; and
     
    J) Location and description of temperature, pressure and flow
    indicating devices and control devices;
     
    3) A description and analysis of the waste to be burned compared with the
    waste for which data from operational or trial burns are provided to
    support the contention that a trial burn is not needed. The data should

     
    19
    include those items listed in subsection (c)(1) of this Section. This
    analysis should specify the POHCs that the applicant has identified in the
    waste for which a permit is sought, and any differences from the POHCs
    in the waste for which burn data are provided;
     
    4) The design and operating conditions of the incinerator unit to be used,
    compared with that for which comparative burn data are available;
     
    5) A description of the results submitted from any previously conducted trial
    burns, including the following:
     
    A) Sampling and analysis techniques used to calculate performance
    standards in 35 Ill. Adm. Code 724.443;
     
    B) Methods and results of monitoring temperatures, waste feed rates,
    carbon monoxide, and an appropriate indicator of combustion gas
    velocity (including a statement concerning the precision and
    accuracy of this measurement); and
     
    C) The certification and results required by subsection (b) of this
    Section;
     
    6) The expected incinerator operation information to demonstrate compliance
    with 35 Ill. Adm. Code 724.443 and 724.445, including the following:
     
    A) Expected carbon monoxide (CO) level in the stack exhaust gas;
     
    B) Waste feed rate;
     
    C) Combustion zone temperature;
     
    D) Indication of combustion gas velocity;
     
    E) Expected stack gas volume, flow rate, and temperature;
     
    F) Computed residence time for waste in the combustion zone;
     
    G) Expected hydrochloric acid removal efficiency;
     
    H) Expected fugitive emissions and their control procedures; and
     
    I) Proposed waste feed cut-off limits based on the identified
    significant operating parameters;
     
    7) The Agency may, pursuant to 35 Ill. Adm. Code 705.122, request such
    additional information as may be necessary for the Agency to determine

     
    20
    whether the incinerator meets the requirements of Subpart O of 35 Ill.
    Adm. Code 724 and what conditions are required by that Subpart and
    Section 39(d) of the Environmental Protection Act [415 ILCS 5/39(d)];
    and
     
    8) Waste analysis data, including that submitted in subsection (c)(1) of this
    Section, sufficient to allow the Agency to specify as permit Principal
    Organic Hazardous Constituents (permit POHCs) those constituents for
    which destruction and removal efficiencies will be required.
     
    d) The Agency must approve a permit application without a trial burn if it finds the
    following:
     
    1) The wastes are sufficiently similar; and
     
    2) The incinerator units are sufficiently similar, and the data from other trial
    burns are adequate to specify (under 35 Ill. Adm. Code 724.445) operating
    conditions that will ensure that the performance standards in 35 Ill. Adm.
    Code 724.443 will be met by the incinerator.
     
    e) When an owner or operator demonstrates compliance with the air emission
    standards and limitations of the federal National Emission Standards for
    Hazardous Air Pollutants (NESHAPs) in subpart EEE of 40 CFR 63, subpart EEE
    (National Emission Standards for Hazardous Air Pollutants from Hazardous
    Waste Combustors), incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(b) (i.e., by conducting a comprehensive performance test and submitting
    a Notification of Compliance under 40 CFR 63.1207(j) and 63.1210(b)
    documenting compliance with all applicable requirements of subpart EEE of 40
    CFR 63, subpart EEE), the requirements of this Section do not apply, except those
    provisions that the Agency determines are necessary to ensure compliance with
    35 Ill. Adm. Code 724.445(a) and (c) if the owner or operator elects to comply
    with Section 703.320(a)(1)(A) to minimize emissions of toxic compounds from
    startup, shutdown, and malfunction events. Nevertheless, the Agency may apply
    the provisions of this Section, on a case-by-case basis, for purposes of
    information collection in accordance with Sections 703.188 and 703.241(b)(2).
     
    BOARD NOTE: Operating conditions used to determine effective treatment of
    hazardous waste remain effective after the owner or operator demonstrates
    compliance with the standards of subpart EEE of 40 CFR 63, subpart EEE.
     
    BOARD NOTE: Derived from 40 CFR 270.19 (2002), as amended at 67 Fed. Reg. 77687
    (December 19, 2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    21
    Section 703.208 Boilers and Industrial Furnaces Burning Hazardous Waste
     
    When the owner or operator of a cement or lightweight aggregate kiln demonstrates compliance
    with the air emission standards and limitations of the federal National Emission Standards for
    Hazardous Air Pollutants (NESHAPs) in subpart EEE of 40 CFR 63, subpart EEE (National
    Emission Standards for Hazardous Air Pollutants from Hazardous Waste Combustors),
    incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(b) (i.e., by conducting a
    comprehensive performance test and submitting a Notification of Compliance under 40 CFR
    63.1207(j) and 63.1210(b) documenting compliance with all applicable requirements of subpart
    EEE of 40 CFR 63, subpart EEE), the requirements of this Section do not apply, except those
    provisions that the Agency determines are necessary to ensure compliance with 35 Ill. Adm.
    Code 726.202(e)(1) and (e)(2)(C) if the owner or operator elects to comply with Section
    703.310(a)(1)(A) to minimize emissions of toxic compounds from startup, shutdown, and
    malfunction events. Nevertheless, the Agency may apply the provisions of this Section, on a
    case-by-case basis, for purposes of information collection in accordance with Sections 703.188
    and 703.241(a)(2).
     
    a) Trial burns.
     
    1) General. Except as provided below, an owner or operator that is subject to
    the standards to control organic emissions provided by 35 Ill. Adm. Code
    726.204, standards to control particulate matter provided by 35 Ill. Adm.
    Code 726.205, standards to control metals emissions provided by 35 Ill.
    Adm. Code 726.206, or standards to control hydrogen chloride (HCl) or
    chlorine gas emissions provided by 35 Ill. Adm. Code 726.207 must
    conduct a trial burn to demonstrate conformance with those standards and
    must submit a trial burn plan or the results of a trial burn, including all
    required determinations, in accordance with Section 703.232.
     
    A) Under subsections (a)(2) through (a)(5) of this Section and 35 Ill.
    Adm. Code 726.204 through 726.207, the Agency may waive a
    trial burn to demonstrate conformance with a particular emission
    standard; and
     
    B) The owner or operator may submit data in lieu of a trial burn, as
    prescribed in subsection (a)(6) of this Section.
     
    2) Waiver of trial burn of DRE (destruction removal efficiency).
     
    A) Boilers operated under special operating requirements. When
    seeking to be permitted under 35 Ill. Adm. Code 726.204(a)(4) and
    726.210, which automatically waive the DRE trial burn, the owner
    or operator of a boiler must submit documentation that the boiler
    operates under the special operating requirements provided by 35
    Ill. Adm. Code 726.210.
     

     
    22
    B) Boilers and industrial furnaces burning low risk waste. When
    seeking to be permitted under the provisions for low risk waste
    provided by 35 Ill. Adm. Code 726.204(a)(5) and 726.209(a),
    which waive the DRE trial burn, the owner or operator must
    submit the following:
     
    i) Documentation that the device is operated in conformance
    with the requirements of 35 Ill. Adm. Code 726.209(a)(1).
     
    ii) Results of analyses of each waste to be burned,
    documenting the concentrations of nonmetal compounds
    listed in Appendix H to 35 Ill. Adm. Code 721, except for
    those constituents that would reasonably not be expected to
    be in the waste. The constituents excluded from analysis
    must be identified and the basis for their exclusion
    explained. The analysis must rely on approriate analytical
    techniques specified in Test Methods for the Evaluation of
    Solid Waste, Physical/Chemical Methods, incorporated by
    reference in 35 Ill. Adm. Code 720.111.
     
    iii) Documentation of hazardous waste firing rates and
    calculations of reasonable, worst-case emission rates of
    each constituent identified in subsection (a)(2)(B)(ii) of this
    Section using procedures provided by 35 Ill. Adm. Code
    726.209(a)(2)(B).
     
    iv) Results of emissions dispersion modeling for emissions
    identified in subsection (a)(2)(B)(iii) of this Section using
    modeling procedures prescribed by 35 Ill. Adm. Code
    726.206(h). The Agency must review the emission
    modeling conducted by the applicant to determine
    conformance with these procedures. The Agency must
    either approve the modeling or determine that alternate or
    supplementary modeling is appropriate.
     
    v) Documentation that the maximum annual average ground
    level concentration of each constituent identified in
    subsection (a)(2)(B)(ii) of this Section quantified in
    conformance with subsection (a)(2)(B)(iv) of this Section
    does not exceed the allowable ambient level established in
    Appendix D or E to 35 Ill. Adm. Code 726. The acceptable
    ambient concentration for emitted constituents for which a
    specific reference air concentration has not been
    established in Appendix D to 35 Ill. Adm. Code 726 or
    risk-specific doses has not been established in Appendix E
    to 35 Ill. Adm. Code 726 is 0.1 micrograms per cubic

     
    23
    meter, as noted in the footnote to Appendix D to 35 Ill.
    Adm. Code 726.
     
    3) Waiver of trial burn for metals. When seeking to be permitted under the
    Tier I (or adjusted Tier I) metals feed rate screening limits provided by 35
    Ill. Adm. Code 726.206(b) and (e) that control metals emissions without
    requiring a trial burn, the owner or operator must submit the following:
     
    A) Documentation of the feed rate of hazardous waste, other fuels,
    and industrial furnace feed stocks;
     
    B) Documentation of the concentration of each metal controlled by 35
    Ill. Adm. Code 726.206(b) or (c) in the hazardous waste, other
    fuels and industrial furnace feedstocks, and calculations of the total
    feed rate of each metal;
     
    C) Documentation of how the applicant will ensure that the Tier I feed
    rate screening limits provided by 35 Ill. Adm. Code 726.206(b) or
    (e) will not be exceeded during the averaging period provided by
    that subsection;
     
    D) Documentation to support the determination of the TESH (terrain-
    adjusted effective stack height), good engineering practice stack
    height, terrain type, and land use, as provided by 35 Ill. Adm. Code
    726.206(b)(3) through (5);
     
    E) Documentation of compliance with the provisions of 35 Ill. Adm.
    Code 726.206(b)(6), if applicable, for facilities with multiple
    stacks;
     
    F) Documentation that the facility does not fail the criteria provided
    by 35 Ill. Adm. Code 726.206(b)(7) for eligibility to comply with
    the screening limits; and
     
    G) Proposed sampling and metals analysis plan for the hazardous
    waste, other fuels, and industrial furnace feed stocks.
     
    4) Waiver of trial burn for PM (particulate matter). When seeking to be
    permitted under the low risk waste provisions of 35 Ill. Adm. Code
    726.209(b), which waives the particulate standard (and trial burn to
    demonstrate conformance with the particulate standard), applicants must
    submit documentation supporting conformance with subsections (a)(2)(B)
    and (a)(3) of this Section.
     
    5) Waiver of trial burn for HCl and chlorine gas. When seeking to be
    permitted under the Tier I (or adjusted Tier I) feed rate screening limits for

     
    24
    total chlorine and chloride provided by 35 Ill. Adm. Code 726.207(b)(1)
    and (e) that control emissions of HCl and chlorine gas without requiring a
    trial burn, the owner or operator must submit the following:
     
    A) Documentation of the feed rate of hazardous waste, other fuels,
    and industrial furnace feed stocks;
     
    B) Documentation of the levels of total chlorine and chloride in the
    hazardous waste, other fuels and industrial furnace feedstocks, and
    calculations of the total feed rate of total chlorine and chloride;
     
    C) Documentation of how the applicant will ensure that the Tier I (or
    adjusted Tier I) feed rate screening limits provided by 35 Ill. Adm.
    Code 726.207(b)(1) or (e) will not be exceeded during the
    averaging period provided by that subsection;
     
    D) Documentation to support the determination of the TESH, good
    engineering practice stack height, terrain type and land use as
    provided by 35 Ill. Adm. Code 726.207(b)(3);
     
    E) Documentation of compliance with the provisions of 35 Ill. Adm.
    Code 726.207(b)(4), if applicable, for facilities with multiple
    stacks;
     
    F) Documentation that the facility does not fail the criteria provided
    by 35 Ill. Adm. Code 726.207(b)(3) for eligibility to comply with
    the screening limits; and
     
    G) Proposed sampling and analysis plan for total chlorine and
    chloride for the hazardous waste, other fuels, and industrial
    furnace feedstocks.
     
    6) Data in lieu of trial burn. The owner or operator may seek an exemption
    from the trial burn requirements to demonstrate conformance with Section
    703.232 and 35 Ill. Adm. Code 726.204 through 726.207 by providing the
    information required by Section 703.232 from previous compliance testing
    of the device in conformance with 35 Ill. Adm. Code 726.203 or from
    compliance testing or trial or operational burns of similar boilers or
    industrial furnaces burning similar hazardous wastes under similar
    conditions. If data from a similar device is used to support a trial burn
    waiver, the design and operating information required by Section 703.232
    must be provided for both the similar device and the device to which the
    data is to be applied, and a comparison of the design and operating
    information must be provided. The Agency must approve a permit
    application without a trial burn if the Agency finds that the hazardous
    wastes are sufficiently similar, the devices are sufficiently similar, the

     
    25
    operating conditions are sufficiently similar, and the data from other
    compliance tests, trial burns, or operational burns are adequate to specify
    (under 35 Ill. Adm. Code 726.102) operating conditions that will ensure
    conformance with 35 Ill. Adm. Code 726.102(c). In addition, the
    following information must be submitted:
     
    A) For a waiver from any trial burn, the following:
     
    i) A description and analysis of the hazardous waste to be
    burned compared with the hazardous waste for which data
    from compliance testing or operational or trial burns are
    provided to support the contention that a trial burn is not
    needed;
     
    ii) The design and operating conditions of the boiler or
    industrial furnace to be used, compared with that for which
    comparative burn data are available; and
     
    iii) Such supplemental information as the Agency finds
    necessary to achieve the purposes of this subsection (a).
     
    B) For a waiver of the DRE trial burn, the basis for selection of
    POHCs (principal organic hazardous constituents) used in the
    other trial or operational burns that demonstrate compliance with
    the DRE performance standard in 35 Ill. Adm. Code 726.204(a).
    This analysis should specify the constituents in Appendix H to 35
    Ill. Adm. Code 721 that the applicant has identified in the
    hazardous waste for which a permit is sought and any differences
    from the POHCs in the hazardous waste for which burn data are
    provided.
     
    b) Alternative HC limit for industrial furnaces with organic matter in raw materials.
    An owner or operator of industrial furnaces requesting an alternative HC limit
    under 35 Ill. Adm. Code 726.204(f) must submit the following information at a
    minimum:
     
    1) Documentation that the furnace is designed and operated to minimize HC
    emissions from fuels and raw materials;
     
    2) Documentation of the proposed baseline flue gas HC (and CO)
    concentration, including data on HC (and CO) levels during tests when the
    facility produced normal products under normal operating conditions from
    normal raw materials while burning normal fuels and when not burning
    hazardous waste;
     
    3) Test burn protocol to confirm the baseline HC (and CO) level including

     
    26
    information on the type and flow rate of all feedstreams, point of
    introduction of all feedstreams, total organic carbon content (or other
    appropriate measure of organic content) of all nonfuel feedstreams, and
    operating conditions that affect combustion of fuels and destruction of
    hydrocarbon emissions from nonfuel sources;
     
    4) Trial burn plan to do the following:
     
    A) To demonstrate when burning hazardous waste that flue gas HC
    (and CO) concentrations do not exceed the baseline HC (and CO)
    level; and
     
    B) To identify, in conformance with Section 703.232(d), the types and
    concentrations of organic compounds listed in Appendix H to 35
    Ill. Adm. Code 721 that are emitted when burning hazardous
    waste;
     
    5) Implementation plan to monitor over time changes in the operation of the
    facility that could reduce the baseline HC level and procedures to
    periodically confirm the baseline HC level; and
     
    6) Such other information as the Agency finds necessary to achieve the
    purposes of this subsection (b).
     
    c) Alternative metals implementation approach. When seeking to be permitted
    under an alternative metals implementation approach under 35 Ill. Adm. Code
    726.206(f), the owner or operator must submit documentation specifying how the
    approach ensures compliance with the metals emissions standards of 35 Ill. Adm.
    Code 726.106(c) or (d) and how the approach can be effectively implemented and
    monitored. Further, the owner or operator must provide such other information
    that the Agency finds necessary to achieve the purposes of this subsection (c).
     
    d) Automatic waste feed cutoff system. An owner or operator must submit
    information describing the automatic waste feed cutoff system, including any pre-
    alarm systems that may be used.
     
    e) Direct transfer. An owner or operator that uses direct transfer operations to feed
    hazardous waste from transport vehicles (containers, as defined in 35 Ill. Adm.
    Code 726.211) directly to the boiler or industrial furnace must submit information
    supporting conformance with the standards for direct transfer provided by 35 Ill.
    Adm. Code 726.211.
     
    f) Residues. An owner or operator that claims that its residues are excluded from
    regulation under the provisions of 35 Ill. Adm. Code 726.212 must submit
    information adequate to demonstrate conformance with those provisions.
     

     
    27
    BOARD NOTE: Derived from 40 CFR 270.22 (2002), as amended at 67 Fed. Reg. 77687
    (December 19, 2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.210 Process Vents
     
    Except as otherwise provided in 35 Ill. Adm. Code 724.101, the owner or operator of a facility
    that has process vents to which Subpart AA of 35 Ill. Adm. Code 724 applies must provide the
    following additional information:
     
    a) For facilities that cannot install a closed-vent system and control device to comply
    with Subpart AA of 35 Ill. Adm. Code 724 on the effective date on which the
    facility becomes subject to that Subpart or Subpart AA of 35 Ill. Adm. Code 725,
    an implementation schedule, as specified in 35 Ill. Adm. Code 724.933(a)(2).
     
    b) Documentation of compliance with the process vent standards in 35 Ill. Adm.
    Code 724.932, including the following:
     
    1) Information and data identifying all affected process vents, annual
    throughput and operating hours of each affected unit, estimated emission
    rates for the affected vent and for the overall facility (i.e., the total
    emissions for all affected vents at the facility), and the approximate
    location within the facility of each affected unit (e.g., identify the
    hazardous waste management units on a facility plot plan);
     
    2) Information and data supporting estimates of vent emissions and emission
    reduction achieved by add-on control devices based on engineering
    calculations or source tests. For the purpose of determining compliance,
    estimates of vent emissions and emission reductions must be made using
    operating parameter values (e.g., temperatures, flow rates, or
    concentrations) that represent the conditions that exist when the waste
    management unit is operating at the highest load or capacity level
    reasonably expected to occur; and
     
    3) Information and data used to determine whether or not a process vent is
    subject to 35 Ill. Adm. Code 724.932.
     
    c) Where an owner or operator applies for permission to use a control device other
    than a thermal vapor incinerator, catalytic vapor incinerator, flare, boiler, process
    heater, condenser, or carbon adsorption system to comply with 35 Ill. Adm. Code
    724.932, and chooses to use test data to determine the organic removal efficiency
    or the total organic compound concentration achieved by the control device, a
    performance test plan as specified in 35 Ill. Adm. Code 724.935(b)(3).
     
    d) Documentation of compliance with 35 Ill. Adm. Code 724.933, including the

     
    28
    following:
     
    1) A list of all information references and sources used in preparing the
    documentation.
     
    2) Records, including the dates of each compliance test required by 35 Ill.
    Adm. Code 724.933(k).
     
    3) A design analysis, specifications, drawings, schematics, piping, and
    instrumentation diagrams based on the appropriate sections of “APTI
    Course 415: Control of Gaseous Emissions,” USEPA publication number
    450/2-81-005, incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(a), or other engineering texts approved by the Agency that
    present basic control device design information. The design analysis must
    address the vent stream characteristics and control device parameters as
    specified in 35 Ill. Adm. Code 724.935(b)(4)(C).
     
    4) A statement signed and dated by the owner or operator certifying that the
    operating parameters used in the design analysis reasonably represent the
    conditions that exist when the hazardous waste management unit is or
    would be operating at the highest load or capacity level reasonably
    expected to occur.
     
    5) A statement signed and dated by the owner or operator certifying that the
    control device is designed to operate at an efficiency of 95 weight percent
    or greater, unless the total organic emission limits of 35 Ill. Adm. Code
    724.932(a) for affected process vents at the facility can be attained by a
    control device involving vapor recovery at an efficiency less than 95
    weight percent.
     
    BOARD NOTE: Derived from 40 CFR 270.24 (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.211 Equipment
     
    Except as otherwise provided in 35 Ill. Adm. Code 724.101, the owner or operator of a facility
    that has equipment to which Subpart BB of 35 Ill. Adm. Code 724 applies must provide the
    following additional information:
     
    a) For each piece of equipment to which Subpart BB of 35 Ill. Adm. Code 724
    applies, the following:
     
    1) Equipment identification number and hazardous waste management unit
    identification;
     

     
    29
    2) Approximate locations within the facility (e.g., identify the hazardous
    waste management unit on a facility plot plan);
     
    3) Type of equipment (e.g., a pump or pipeline valve);
     
    4) Percent by weight total organics in the hazardous wastestream at the
    equipment;
     
    5) Hazardous waste state at the equipment (e.g., gas/vapor or liquid); and
     
    6) Method of compliance with the standard (e.g., “monthly leak detection
    and repair” or “equipped with dual mechanical seals”).
     
    b) For facilities that cannot install a closed-vent system and control device to comply
    with Subpart BB of 35 Ill. Adm. Code 724 on the effective date that facility
    becomes subject to this Subpart or Subpart BB of 35 Ill. Adm. Code 724, an
    implementation schedule as specified in 35 Ill. Adm. Code 724.933(a)(2).
     
    c) Where an owner or operator applies for permission to use a control device other
    than a thermal vapor incinerator, catalytic vapor incinerator, flare, boiler, process
    heater, condenser, or carbon adsorption system and chooses to use test data to
    determine the organic removal efficiency or the total organic compound
    concentration achieved by the control device, a performance test plan as specified
    in 35 Ill. Adm. Code 724.935(b)(3).
     
    d) Documentation that demonstrates compliance with the equipment standards in 35
    Ill. Adm. Code 724.952 or 724.959. This documentation must contain the records
    required under 35 Ill. Adm. Code 724.964. The Agency must request further
    documentation if necessary to demonstrate compliance. Documentation to
    demonstrate compliance with 35 Ill. Adm. Code 724.960 must include the
    following information:
     
    1) A list of all information references and sources used in preparing the
    documentation;
     
    2) Records, including the dates of each compliance test required by 35 Ill.
    Adm. Code 724.933(j);
     
    3) A design analysis, specifications, drawings, schematics, and piping and
    instrumentation diagrams based on the appropriate sections of “APTI
    Course 415: Control of Gaseous Emissions,” USEPA publication number
    450/2-81-005, incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(a), or other engineering texts approved by the Agency that
    present basic control device design information. The design analysis must
    address the vent stream characteristics and control device parameters as
    specified in 35 Ill. Adm. Code 724.935(b)(4)(C);

     
    30
     
    4) A statement signed and dated by the owner or operator certifying that the
    operating parameters used in the design analysis reasonably represent the
    conditions that exist when the hazardous waste management unit is or
    would be operating at the highest load or capacity level reasonably
    expected to occur; and
     
    5) A statement signed and dated by the owner or operator certifying that the
    control device is designed to operate at an efficiency of 95 weight percent
    or greater.
     
    BOARD NOTE: Derived from 40 CFR 270.25 (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.213 Air Emission Controls for Tanks, Surface Impoundments, and Containers
     
    Except as otherwise provided in 35 Ill. Adm. Code 724.101, the owner or operator of a tank, a
    surface impoundment, or a container that uses air emission controls in accordance with the
    requirements of Subpart CC of 35 Ill. Adm. Code 724 must provide the following additional
    information:
     
    a) Documentation for each floating roof cover installed on a tank subject to 35 Ill.
    Adm. Code 724.984(d)(1) or (d)(2) that includes information prepared by the
    owner or operator or provided by the cover manufacturer or vendor describing the
    cover design, and certification by the owner or operator that the cover meets the
    applicable design specifications, as listed in 35 Ill. Adm. Code 725.991(e)(1) or
    (f)(1).
     
    b) Identification of each container area subject to the requirements of Subpart CC of
    35 Ill. Adm. Code 724 and certification by the owner or operator that the
    requirements of this Subpart D are met.
     
    c) Documentation for each enclosure used to control air pollutant emissions from
    containers in accordance with the requirements of 35 Ill. Adm. Code
    724.984(d)(5) or 724.986(e)(1)(ii) that includes records for the most recent set of
    calculations and measurements performed by the owner or operator to verify that
    the enclosure meets the criteria of a permanent total enclosure, as specified in
    “Procedure T--Criteria for and Verification of a Permanent or Temporary Total
    Enclosure,” under in appendix B to 40 CFR 52.741, appendix B (VOM
    Measurement Techniques for Capture Efficiency), incorporated by reference in 35
    Ill. Adm. Code 720.111 720.111(b).
     
    d) Documentation for each floating membrane cover installed on a surface
    impoundment in accordance with the requirements of 35 Ill. Adm. Code
    724.985(c) that includes information prepared by the owner or operator or

     
    31
    provided by the cover manufacturer or vendor describing the cover design, and
    certification by the owner or operator that the cover meets the specifications listed
    in 35 Ill. Adm. Code 724.985(c)(1).
     
    e) Documentation for each closed-vent system and control device installed in
    accordance with the requirements of 35 Ill. Adm. Code 724.987 that includes
    design and performance information, as specified in Section 703.124(c) and (d).
     
    f) An emission monitoring plan for both Method 21 (Determination of Volatile
    Organic Compound Leaks) in appendix A to 40 CFR 60, appendix A (Test
    Methods), incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(b),
    and control device monitoring methods. This plan must include the following
    information: monitoring points, monitoring methods for control devices,
    monitoring frequency, procedures for documenting exceedances exceedences, and
    procedures for mitigating noncompliances.
     
    g) When an owner or operator of a facility subject to Subpart CC of 35 Ill. Adm.
    Code 725 cannot comply with Subpart CC of 35 Ill. Adm. Code 724 by the date
    of permit issuance, the schedule of implementation required under 35 Ill. Adm.
    Code 725.982.
     
    BOARD NOTE: Derived from 40 CFR 270.27(a) (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART E: SHORT TERM AND PHASED PERMITS
     
    Section 703.221 Alternative Compliance with the Federal NESHAPS
     
    When an owner or operator demonstrates compliance with the air emission standards and
    limitations of the federal National Emission Standards for Hazardous Air Pollutants (NESHAPs)
    in subpart EEE of 40 CFR 63, subpart EEE (National Emission Standards for Hazardous Air
    Pollutants from Hazardous Waste Combustors), incorporated by reference in 35 Ill. Adm. Code
    720.111 720.111(b) (i.e., by conducting a comprehensive performance test and submitting a
    Notification of Compliance under 40 CFR 63.1207(j) and 63.1210(b) documenting compliance
    with all applicable requirements of subpart EEE to 40 CFR 63, subpart EEE), the requirements
    of Sections 703.221 through 703.225 do not apply, except those provisions that the Agency
    determines are necessary to ensure compliance with 35 Ill. Adm. Code 724.445(a) and (c) if the
    owner or operator elects to comply with Section 703.310(a)(1)(A) to minimize emissions of
    toxic compounds from startup, shutdown, and malfunction events. Nevertheless, the Agency
    may apply the provisions of Sections 703.221 through 703.225, on a case-by-case basis, for
    purposes of information collection in accordance with Sections 703.188 and 703.241(a)(2).
     
    BOARD NOTE: Derived from 40 CFR 270.62 preamble (2002), as amended at 67 Fed. Reg.
    77687 (December 19, 2002) (2005).
     

     
    32
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.223 Incinerator Conditions During Trial Burn
     
    For the purposes of determining feasibility of compliance with the performance standards of 35
    Ill. Adm. Code 724.443 and of determining adequate operating conditions under 35 Ill. Adm.
    Code 724.445, the Agency must establish conditions in the permit to a new hazardous waste
    incinerator to be effective during the trial burn.
     
    a) Applicants must propose a trial burn plan, prepared under subsection (b) of this
    Section with Part B of the permit application;
     
    b) The trial burn plan must include the following information:
     
    1) An analysis of each waste or mixture of wastes to be burned that includes
    the following:
     
    A) Heat value of the waste in the form and composition in which it
    will be burned;
     
    B) Viscosity (if applicable), or description of physical form of the
    waste;
     
    C) An identification of any hazardous organic constituents listed in
    Appendix H to 35 Ill. Adm. Code 721, that are present in the waste
    to be burned, except that the applicant need not analyze for
    constituents listed in Appendix H to 35 Ill. Adm. Code 721 that
    would reasonably not be expected to be found in the waste. The
    constituents excluded from analysis must be identified, and the
    basis for their exclusion stated. The waste analysis must rely on
    appropriate analytical techniques specified in “Test Methods for
    the Evaluation of Solid Waste, Physical/Chemical Methods,”
    USEPA Publication SW-846, as incorporated by reference at 35
    Ill. Adm. Code 720.111 and Section 703.110, or their equivalent;
    and
     
    D) An approximate quantification of the hazardous constituents
    identified in the waste, within the precision produced by the
    appropriate analytical methods specified in “Test Methods for the
    Evaluation of Solid Waste, Physical/Chemical Methods,” USEPA
    Publication SW-846, as incorporated by reference at 35 Ill. Adm.
    Code 720.111 and Section 703.110, or their equivalent;
     
    2) A detailed engineering description of the incinerator for which the permit
    is sought including the following:
     

     
    33
    A) Manufacturer’s name and model number of incinerator (if
    available);
     
    B) Type of incinerator;
     
    C) Linear dimensions of the incinerator unit including the cross
    sectional area of combustion chamber;
     
    D) Description of the auxiliary fuel system (type/feed);
     
    E) Capacity of prime mover;
     
    F) Description of automatic waste feed cut-off systems;
     
    G) Stack gas monitoring and pollution control equipment;
     
    H) Nozzle and burner design;
     
    I) Construction materials;
     
    J) Location and description of temperature-, pressure-, and flow-
    indicating and control devices;
     
    3) A detailed description of sampling and monitoring procedures, including
    sampling and monitoring locations in the system, the equipment to be
    used, sampling and monitoring frequency, and planned analytical
    procedures for sample analysis;
     
    4) A detailed test schedule for each waste for which the trial burn is planned
    including dates, duration, quantity of waste to be burned, and other factors
    relevant to the Agency’s decision under subsection (e) of this Section;
     
    5) A detailed test protocol, including, for each waste identified, the ranges of
    temperature, waste feed rate, combustion gas velocity, use of auxiliary
    fuel, and any other relevant parameters that will be varied to affect the
    destruction and removal efficiency of the incinerator;
     
    6) A description of, and planned operating conditions for, any emission
    control equipment that will be used;
     
    7) Procedures for rapidly stopping waste feed, shutting down the incinerator,
    and controlling emissions in the event of an equipment malfunction;
     
    8) Such other information as the Agency reasonably finds necessary to
    determine whether to approve the trial burn plan in light of the purposes of
    this subsection (b) and the criteria in subsection (e) of this Section. Such

     
    34
    information must be requested by the Agency pursuant to 35 Ill. Adm.
    Code 705.123;
     
    c) The Agency, in reviewing the trial burn plan, must evaluate the sufficiency of the
    information provided and must require the applicant, pursuant to 35 Ill. Adm.
    Code 705.123, to supplement this information, if necessary, to achieve the
    purposes of this Section;
     
    d) Based on the waste analysis data in the trial burn plan, the Agency must specify
    as trial Principal Organic Hazardous Constituents (POHCs), those constituents for
    which destruction and removal efficiencies must be calculated during the trial
    burn. These trial POHCs must be specified by the Agency based on its estimate
    of the difficulty of incineration of the constituents identified in the waste analysis,
    their concentration or mass in the waste feed, and, for wastes listed in Subpart D
    of 35 Ill. Adm. Code 721, the hazardous waste organic constituent of constituents
    identified in Appendix G or H to 35 Ill. Adm. Code 721 as the basis for listing;
     
    e) The Agency must approve a trial burn plan if it finds the following:
     
    1) That the trial burn is likely to determine whether the incinerator
    performance standard required by 35 Ill. Adm. Code 724.443 can be met;
     
    2) That the trial burn itself will not present an imminent hazard to human
    health or the environment;
     
    3) That the trial burn will help the Agency to determine operating
    requirements to be specified under 35 Ill. Adm. Code 724.445; and
     
    4) That the information sought in subsections (e)(1) and (e)(3) of this Section
    cannot reasonably be developed through other means;
     
    f) The Agency must send a notice to all persons on the facility mailing list, as set
    forth in 35 Ill. Adm. Code 705.161(a), and to the appropriate units of State and
    local government, as set forth in 35 Ill. Adm. Code 705.163(a)(5), announcing the
    scheduled commencement and completion dates for the trial burn. The applicant
    may not commence the trial burn until after the Agency has issued such notice.
     
    1) This notice must be mailed within a reasonable time period before the
    scheduled trial burn. An additional notice is not required if the trial burn
    is delayed due to circumstances beyond the control of the facility or the
    Agency.
     
    2) This notice must contain the following:
     
    A) The name and telephone number of the applicant’s contact person;
     

     
    35
    B) The name and telephone number of the Agency regional office
    appropriate for the facility;
     
    C) The location where the approved trial burn plan and any
    supporting documents can be reviewed and copied; and
     
    D) An expected time period for commencement and completion of the
    trial burn;
     
    g) During each approved trial burn (or as soon after the burn as is practicable), the
    applicant must make the following determinations:
     
    1) A quantitative analysis of the trial POHCs, in the waste feed to the
    incinerator;
     
    2) A quantitative analysis of the exhaust gas for the concentration and mass
    emissions of the trial POHCs, molecular oxygen, and hydrogen chloride
    (HCl);
     
    3) A quantitative analysis of the scrubber water (if any), ash residues, and
    other residues, for the purpose of estimating the fate of the trial POHCs;
     
    4) A computation of destruction and removal efficiency (DRE), in
    accordance with the DRE formula specified in 35 Ill. Adm. Code
    724.443(a);
     
    5) If the HCl (hydrogen chloride) emission rate exceeds 1.8 kilograms of
    HCl per hour (4 pounds per hour), a computation of HCl removal
    efficiency, in accordance with 35 Ill. Adm. Code 724.443(b);
     
    6) A computation of particulate emissions, in accordance with 35 Ill. Adm.
    Code 724.443(c);
     
    7) An identification of sources of fugitive emissions and their means of
    control;
     
    8) A measurement of average, maximum and minimum temperatures, and
    combustion gas velocity;
     
    9) A continuous measurement of carbon monoxide (CO) in the exhaust gas;
     
    10) Such other information as the Agency specifies as necessary to ensure that
    the trial burn will determine compliance with the performance standards in
    35 Ill. Adm. Code 724.443 and to establish the operating conditions
    required by 35 Ill. Adm. Code 724.445 as necessary to meet that
    performance standard;

     
    36
     
    h) The applicant must submit to the Agency a certification that the trial burn has
    been carried out in accordance with the approved trial burn plan, and must submit
    the results of all the determinations required in subsection (g) of this Section.
    This submission must be made within 90 days after completion of the trial burn,
    or later, if approved by the Agency;
     
    i) All data collected during any trial burn must be submitted to the Agency
    following the completion of the trial burn;
     
    j) All submissions required by this Section must be certified on behalf of the
    applicant by the signature of a person authorized to sign a permit application or a
    report under 35 Ill. Adm. Code 702.126;
     
    k) Based on the results of the trial burn, the Agency must set the operating
    requirements in the final permit according to 35 Ill. Adm. Code 724.445. The
    permit modification must proceed as a minor modification according to Section
    703.280.
     
    BOARD NOTE: Derived from 40 CFR 270.62(b) (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.232 Permits for Boilers and Industrial Furnaces Burning Hazardous Waste
     
    When the owner or operator of a cement or lightweight aggregate kiln demonstrates compliance
    with the air emission standards and limitations of the federal National Emission Standards for
    Hazardous Air Pollutants (NESHAPs) in subpart EEE of 40 CFR 63, subpart EEE (National
    Emission Standards for Hazardous Air Pollutants from Hazardous Waste Combustors),
    incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(b) (i.e., by conducting a
    comprehensive performance test and submitting a Notification of Compliance under 40 CFR
    63.1207(j) and 63.1210(b) documenting compliance with all applicable requirements of subpart
    EEE of 40 CFR 63, subpart EEE), the requirements of this Section do not apply, except those
    provisions that the Agency determines are necessary to ensure compliance with 35 Ill. Adm.
    Code 726.202(e)(1) and (e)(2)(C) if the owner or operator elects to comply with Section
    703.310(a)(1)(A) to minimize emissions of toxic compounds from startup, shutdown, and
    malfunction events. Nevertheless, the Agency may apply the provisions of this Section, on a
    case-by-case basis, for purposes of information collection in accordance with Sections 703.188
    and 703.241(a)(2).
     
    a) General. The owner or operator of a new boiler or industrial furnace (one not
    operating under the interim status standards of 35 Ill. Adm. Code 726.203) is
    subject to subsections (b) through (f) of this Section. A boiler or industrial
    furnace operating under the interim status standards of 35 Ill. Adm. Code 726.203
    is subject to subsection (g) of this Section.
     

     
    37
    b) Permit operating periods for a new boiler or industrial furnace. A permit for a
    new boiler or industrial furnace must specify appropriate conditions for the
    following operating periods:
     
    1) Pretrial burn period. For the period beginning with initial introduction of
    hazardous waste and ending with initiation of the trial burn, and only for
    the minimum time required to bring the boiler or industrial furnace to a
    point of operation readiness to conduct a trial burn, not to exceed 720
    hours operating time when burning hazardous waste, the Agency must
    establish permit conditions in the pretrial burn period, including but not
    limited to allowable hazardous waste feed rates and operating conditions.
    The Agency must extend the duration of this operational period once, for
    up to 720 additional hours, at the request of the applicant when good cause
    is shown. The permit must be modified to reflect the extension according
    to Sections 703.280 through 703.283.
     
    A) Applicants must submit a statement, with Part B of the permit
    application, that suggests the conditions necessary to operate in
    compliance with the standards of 35 Ill. Adm. Code 726.204
    through 726.207 during this period. This statement should include,
    at a minimum, restrictions on the applicable operating
    requirements identified in 35 Ill. Adm. Code 726.202 (e).
     
    B) The Agency must review this statement and any other relevant
    information submitted with Part B of the permit application and
    specify requirements for this period sufficient to meet the
    performance standards of 35 Ill. Adm. Code 726.204 through
    726.207 based on the Agency’s engineering judgment.
     
    2) Trial burn period. For the duration of the trial burn, the Agency must
    establish conditions in the permit for the purposes of determining
    feasibility of compliance with the performance standards of 35 Ill. Adm.
    Code 726.204 through 726.207 and determining adequate operating
    conditions under 35 Ill. Adm. Code 726.202(e). Applicants must propose
    a trial burn plan, prepared under subsection (c) of this Section, to be
    submitted with Part B of the permit application.
     
    3) Post-trial burn period.
     
    A) For the period immediately following completion of the trial burn,
    and only for the minimum period sufficient to allow sample
    analysis, data computation and submission of the trial burn results
    by the applicant, and review of the trial burn results and
    modification of the facility permit by the Agency to reflect the trial
    burn results, the Agency must establish the operating requirements
    most likely to ensure compliance with the performance standards

     
    38
    of 35 Ill. Adm. Code 726.204 through 726.207 based on the
    Agency’s engineering judgment.
     
    B) Applicants must submit a statement, with Part B of the application,
    that identifies the conditions necessary to operate during this
    period in compliance with the performance standards of 35 Ill.
    Adm. Code 726.204 through 726.207. This statement should
    include, at a minimum, restrictions on the operating requirements
    provided by 35 Ill. Adm. Code 726.202 (e).
     
    C) The Agency must review this statement and any other relevant
    information submitted with Part B of the permit application and
    specify requirements of this period sufficient to meet the
    performance standards of 35 Ill. Adm. Code 726.204 through
    726.207 based on the Agency’s engineering judgment.
     
    4) Final permit period. For the final period of operation the Agency must
    develop operating requirements in conformance with 35 Ill. Adm. Code
    726.202(e) that reflect conditions in the trial burn plan and are likely to
    ensure compliance with the performance standards of 35 Ill. Adm. Code
    726.204 through 726.207. Based on the trial burn results, the Agency
    must make any necessary modifications to the operating requirements to
    ensure compliance with the performance standards. The permit
    modification must proceed according to Sections 703.280 through
    703.283.
     
    c) Requirements for trial burn plans. The trial burn plan must include the following
    information. The Agency, in reviewing the trial burn plan, must evaluate the
    sufficiency of the information provided and may require the applicant to
    supplement this information, if necessary, to achieve the purposes of this
    subsection (c).
     
    1) An analysis of each feed stream, including hazardous waste, other fuels,
    and industrial furnace feed stocks, as fired, that includes the following:
     
    A) Heating value, levels of antimony, arsenic, barium, beryllium,
    cadmium, chromium, lead, mercury, silver, thallium, total chlorine
    and chloride, and ash; and
     
    B) Viscosity or description of the physical form of the feed stream.
     
    2) An analysis of each hazardous waste, as fired, including the following:
     
    A) An identification of any hazardous organic constituents listed in
    Appendix H to 35 Ill. Adm. Code 721 that are present in the feed
    stream, except that the applicant need not analyze for constituents

     
    39
    listed in Appendix H that would reasonably not be expected to be
    found in the hazardous waste. The constituents excluded from
    analysis must be identified and the basis for this exclusion
    explained. The analysis must be conducted in accordance with
    appropriate analytical techniques specified in “Test Methods for
    the Evaluation of Solid Waste, Physical/Chemical Methods,”
    USEPA Publication SW-846, as incorporated by reference at 35
    Ill. Adm. Code 720.111 and Section 703.110, or their equivalent;
     
    B) An approximate quantification of the hazardous constituents
    identified in the hazardous waste, within the precision produced by
    the appropriate analytical methods specified in “Test Methods for
    the Evaluation of Solid Waste, Physical/Chemical Methods,”
    USEPA Publication SW-846, as incorporated by reference at 35
    Ill. Adm. Code 720.111 and Section 703.110, or other equivalent;
    and
     
    C) A description of blending procedures, if applicable, prior to firing
    the hazardous waste, including a detailed analysis of the hazardous
    waste prior to blending, an analysis of the material with which the
    hazardous waste is blended, and blending ratios.
     
    3) A detailed engineering description of the boiler or industrial furnace,
    including the following:
     
    A) Manufacturer’s name and model number of the boiler or industrial
    furnace;
     
    B) Type of boiler or industrial furnace;
     
    C) Maximum design capacity in appropriate units;
     
    D) Description of the feed system for the hazardous waste and, as
    appropriate, other fuels and industrial furnace feedstocks;
     
    E) Capacity of hazardous waste feed system;
     
    F) Description of automatic hazardous waste feed cutoff systems;
     
    G) Description of any pollution control system; and
     
    H) Description of stack gas monitoring and any pollution control
    monitoring systems.
     
    4) A detailed description of sampling and monitoring procedures, including
    sampling and monitoring locations in the system, the equipment to be

     
    40
    used, sampling and monitoring frequency, and sample analysis.
     
    5) A detailed test schedule for each hazardous waste for which the trial burn
    is planned, including dates, duration, quantity of hazardous waste to be
    burned, and other factors relevant to the Agency’s decision under
    subsection (b)(2) of this Section.
     
    6) A detailed test protocol, including, for each hazardous waste identified,
    the ranges of hazardous waste feed rate, and, as appropriate, the feed rates
    of other fuels and industrial furnace feedstocks, and any other relevant
    parameters that may affect the ability of the boiler or industrial furnace to
    meet the performance standards in 35 Ill. Adm. Code 726.204 through
    726.207.
     
    7) A description of and planned operating conditions for any emission
    control equipment that will be used.
     
    8) Procedures for rapidly stopping the hazardous waste feed and controlling
    emissions in the event of an equipment malfunction.
     
    9) Such other information as the Agency finds necessary to determine
    whether to approve the trial burn plan in light of the purposes of this
    subsection (c) and the criteria in subsection (b)(2) of this Section.
     
    d) Trial burn procedures.
     
    1) A trial burn must be conducted to demonstrate conformance with the
    standards of 35 Ill. Adm. Code 726.104 through 726.107.
     
    2) The Agency must approve a trial burn plan if the Agency finds as follows:
     
    A) That the trial burn is likely to determine whether the boiler or
    industrial furnace can meet the performance standards of 35 Ill.
    Adm. Code 726.104 through 726.107;
     
    B) That the trial burn itself will not present an imminent hazard to
    human health and the environment;
     
    C) That the trial burn will help the Agency to determine operating
    requirements to be specified under 35 Ill. Adm. Code 726.102(e);
    and
     
    D) That the information sought in the trial burn cannot reasonably be
    developed through other means.
     
    3) The Agency must send a notice to all persons on the facility mailing list,

     
    41
    as set forth in 35 Ill. Adm. Code 705.161(a), and to the appropriate units
    of State and local government, as set forth in 35 Ill. Adm. Code
    705.163(a)(5), announcing the scheduled commencement and completion
    dates for the trial burn. The applicant may not commence the trial burn
    until after the Agency has issued such notice.
     
    A) This notice must be mailed within a reasonable time period before
    the trial burn. An additional notice is not required if the trial burn
    is delayed due to circumstances beyond the control of the facility
    or the Agency.
     
    B) This notice must contain the following:
     
    i) The name and telephone number of applicant’s contact
    person;
     
    ii) The name and telephone number of the Agency regional
    office appropriate for the facility;
     
    iii) The location where the approved trial burn plan and any
    supporting documents can be reviewed and copied; and
     
    iv) An expected time period for commencement and
    completion of the trial burn.
     
    4) The applicant must submit to the Agency a certification that the trial burn
    has been carried out in accordance with the approved trial burn plan, and
    submit the results of all the determinations required in subsection (c) of
    this Section. The Agency must, in the trial burn plan, require that the
    submission be made within 90 days after completion of the trial burn, or
    later if the Agency determines that a later date is acceptable.
     
    5) All data collected during any trial burn must be submitted to the Agency
    following completion of the trial burn.
     
    6) All submissions required by this subsection (d) must be certified on behalf
    of the applicant by the signature of a person authorized to sign a permit
    application or a report under 35 Ill. Adm. Code 702.126.
     
    e) Special procedures for DRE trial burns. When a DRE trial burn is required under
    35 Ill. Adm. Code 726.104, the Agency must specify (based on the hazardous
    waste analysis data and other information in the trial burn plan) as trial Principal
    Organic Hazardous Constituents (POHCs) those compounds for which
    destruction and removal efficiencies must be calculated during the trial burn.
    These trial POHCs will be specified by the Agency based on information
    including the Agency’s estimate of the difficulty of destroying the constituents

     
    42
    identified in the hazardous waste analysis, their concentrations or mass in the
    hazardous waste feed, and, for hazardous waste containing or derived from wastes
    listed in Subpart D of 35 Ill. Adm. Code 721, the hazardous waste organic
    constituents identified in Appendix G to 35 Ill. Adm. Code 721 as the basis for
    listing.
     
    f) Determinations based on trial burn. During each approved trial burn (or as soon
    after the burn as is practicable), the applicant must make the following
    determinations:
     
    1) A quantitative analysis of the levels of antimony, arsenic, barium,
    beryllium, cadmium, chromium, lead, mercury, thallium, silver, and
    chlorine/chloride in the feed streams (hazardous waste, other fuels, and
    industrial furnace feedstocks);
     
    2) When a DRE trial burn is required under 35 Ill. Adm. Code 726.204(a),
    the following determinations:
     
    A) A quantitative analysis of the trial POHCs in the hazardous waste
    feed;
     
    B) A quantitative analysis of the stack gas for the concentration and
    mass emissions of the trial POHCs; and
     
    C) A computation of destruction and removal efficiency (DRE), in
    accordance with the DRE formula specified in 35 Ill. Adm. Code
    726.204(a);
     
    3) When a trial burn for chlorinated dioxins and furans is required under 35
    Ill. Adm. Code 726.204(e), a quantitative analysis of the stack gas for the
    concentration and mass emission rate of the 2,3,7,8-chlorinated tetra-
    through octa-congeners of chlorinated dibenzo-p-dioxins and furans, and a
    computation showing conformance with the emission standard;
     
    4) When a trial burn for PM, metals, or HCl and chlorine gas is required
    under 35 Ill. Adm. Code 726.205, 726.206(c) or (d), or 726.207(b)(2) or
    (c), a quantitative analysis of the stack gas for the concentrations and mass
    emissions of PM, metals, or HCl and chlorine gas, and computations
    showing conformance with the applicable emission performance
    standards;
     
    5) When a trial burn for DRE, metals, and HCl and chlorine gas is required
    under 35 Ill. Adm. Code 726.204(a), 726.206(c) or (d), or 726.207(b)(2)
    or (c), a quantitative analysis of the scrubber water (if any), ash residues,
    other residues, and products for the purpose of estimating the fate of the
    trial POHCs, metals, and chlorine and chloride;

     
    43
     
    6) An identification of sources of fugitive emissions and their means of
    control;
     
    7) A continuous measurement of carbon monoxide (CO), oxygen, and, where
    required, hydrocarbons (HC) in the stack gas; and
     
    8) Such other information as the Agency specifies as necessary to ensure that
    the trial burn will determine compliance with the performance standards
    35 Ill. Adm. Code 726.204 through 726.207 and to establish the operating
    conditions required by 35 Ill. Adm. Code 726.204 through 726.207 and of
    determining adequate operating conditions under 35 Ill. Adm. Code
    726.203, and to establish the operating conditions required by 35 Ill. Adm.
    Code 726.202(e) as necessary to meet those performance standards.
     
    g) Interim status boilers and industrial furnaces. For the purpose of determining
    feasibility of compliance with the performance standards of 35 Ill. Adm. Code
    726.204 through 726.207 and of determining adequate operating conditions under
    35 Ill. Adm. Code 726.203, an applicant that owns or operates an existing boiler
    or industrial furnace which is operated under the interim status standards of 35 Ill.
    Adm. Code 726.203 must either prepare and submit a trial burn plan and perform
    a trial burn in accordance with the requirements of this Section or submit other
    information as specified in Section 703.208(a)(6). The Agency must announce its
    intention to approve of the trial burn plan in accordance with the timing and
    distribution requirements of subsection (d)(3) of this Section. The contents of the
    notice must include all of the following information: the name and telephone
    number of a contact person at the facility; the name and telephone number of the
    Agency regional office appropriate for the facility; the location where the trial
    burn plan and any supporting documents can be reviewed and copied; and a
    schedule of the activities that are required prior to permit issuance, including the
    anticipated time schedule for Agency approval of the plan, and the time periods
    during which the trial burn would be conducted. Applicants that submit a trial
    burn plan and receive approval before submission of the Part B permit application
    must complete the trial burn and submit the results specified in subsection (f) of
    this Section with the Part B permit application. If completion of this process
    conflicts with the date set for submission of the Part B application, the applicant
    must contact the Agency to establish a later date for submission of the Part B
    application or the trial burn results. If the applicant submits a trial burn plan with
    Part B of the permit application, the trial burn must be conducted and the results
    submitted within a time period prior to permit issuance to be specified by the
    Agency.
     
    BOARD NOTE: Derived from 40 CFR 270.66 (2002), as amended at 67 Fed. Reg. 77687
    (December 19, 2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)

     
    44
     
    SUBPART H: REMEDIAL ACTION PLANS
     
    Section 703.300 Special Regulatory Format
     
    USEPA wrote the federal counterpart to this Subpart H, subpart H of 40 CFR 270, Subpart H, in a
    special format to make it easier to understand the regulatory requirements. The Board has adapted
    the substance of the corresponding federal regulations in this Subpart H to use a more conventional
    regulatory format, rather than the question-and-answer format used by USEPA.
     
    BOARD NOTE: Derived from 40 CFR 270.79 (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.305 Operating Under a RAP
     
    a) The records an owner or operator must maintain concerning its RAP. An owner or
    operator is required to keep records of the following:
     
    1) All data used to complete RAP applications and any supplemental
    information that an owner or operator submits for a period of at least three
    years from the date the application is signed; and
     
    2) Any operating or other records the Agency requires an owner or operator to
    maintain as a condition of the RAP.
     
    BOARD NOTE: Subsection (a) is derived from 40 CFR 270.210 (2002).
     
    b) How time periods in the requirements in Subpart H of this Part and the RAP are
    computed.
     
    1) Any time period scheduled to begin on the occurrence of an act or event
    must begin on the day after the act or event. (For example, if a RAP
    specifies that the owner or operator must close a staging pile within 180
    days after the operating term for that staging pile expires, and the operating
    term expires on June 1, then June 2 counts as day one of the 180 days, and
    the owner or operator would have to complete closure by November 28.)
     
    2) Any time period scheduled to begin before the occurrence of an act or event
    must be computed so that the period ends on the day before the act or event.
    (For example, if an owner or operator is transferring ownership or
    operational control of its site, and the owner or operator wishes to transfer
    its RAP, the new owner or operator must submit a revised RAP application
    no later than 90 days before the scheduled change. Therefore, if an owner
    or operator plans to change ownership on January 1, the new owner or
    operator must submit the revised RAP application no later than October 3,

     
    45
    so that the 90th day would be December 31.)
     
    3) If the final day of any time period falls on a weekend or legal holiday, the
    time period must be extended to the next working day. (For example, if an
    owner or operator wishes to appeal the Agency’s decision to modify its
    RAP, then an owner or operator must petition the Board within 35 days after
    the Agency has issued the final RAP decision. If the 35th day falls on
    Sunday, then the owner or operator may submit its appeal by the Monday
    after. If the 35th day falls on July 4th, then the owner or operator may
    submit its appeal by July 5th.)
     
    4) Whenever a party or interested person has the right to or is required to act
    within a prescribed period after the service of notice or other paper upon
    him by mail, four days may not be added to the prescribed term. (For
    example, if an owner or operator wishes to appeal the Agency’s decision to
    modify its RAP, then the owner or operator must petition the Board within
    35 days after the Agency has issued the final RAP decision.)
     
    BOARD NOTE: Subsection (b) is derived from 40 CFR 270.215 (2002). Federal
    subsections (c) and (d) provide that a RAP is effective 30 days after the Agency
    notice of approval. The Board has used 35 days to be consistent with the 35 days
    within which a permit appeal must be filed under Section 40(a)(1) of the Act [415
    ILCS 5/40(a)(1)]. Further, federal subsection (d) provides three days for
    completion of service by mail. The addition of four days (see procedural rule 35 Ill.
    Adm. Code 101.144(c)) to be consistent with 40 CFR 270.215(d) would exceed the
    35 days allowed under Section 40(a)(1) of the Act [415 ILCS 5/40(a)(1)].
     
    c) How an owner or operator may transfer its RAP to a new owner or operator.
     
    1) If an owner or operator wishes to transfer its RAP to a new owner or
    operator, the owner or operator must follow the requirements specified in its
    RAP for RAP modification to identify the new owner or operator, and
    incorporate any other necessary requirements. These modifications do not
    constitute “significant” modifications for purposes of Section 703.304(a).
    The new owner or operator must submit a revised RAP application no later
    than 90 days before the scheduled change along with a written agreement
    containing a specific date for transfer of RAP responsibility between the
    owner or operator and the new permittees.
     
    2) When a transfer of ownership or operational control occurs, the old owner
    or operator must comply with the applicable requirements in Subpart H of
    35 Ill. Adm. Code 724 (Financial Requirements) until the new owner or
    operator has demonstrated that it is complying with the requirements in that
    Subpart. The new owner or operator must demonstrate compliance with
    Subpart H of 35 Ill. Adm. Code 724 within six months after the date of the
    change in ownership or operational control of the facility or remediation

     
    46
    waste management site. When the new owner or operator demonstrates
    compliance with Subpart H of 35 Ill. Adm. Code 724 to the Agency, the
    Agency must notify the former owner or operator that it no longer needs to
    comply with Subpart H of 35 Ill. Adm. Code 724 as of the date of
    demonstration.
     
    BOARD NOTE: Subsection (c) is derived from 40 CFR 270.220 (2002).
     
    d) What the Agency must report about noncompliance with RAPs. The Agency must
    report noncompliance with RAPs according to the provisions of 40 CFR 270.5
    (Noncompliance and Program Reporting by the Director), incorporated by
    reference in 35 Ill. Adm. Code 720.111 720.111(b).
     
    BOARD NOTE: Subsection (d) is derived from 40 CFR 270.225 (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.306 Obtaining a RAP for an Off-Site Location
     
    An owner or operator may perform remediation waste management activities under a RAP at a
    location removed from the area where the remediation wastes originated.
     
    a) An owner or operator may request a RAP for remediation waste management
    activities at a location removed from the area where the remediation wastes
    originated if the owner or operator believes such a location would be more
    protective than the contaminated area or areas in close proximity.
     
    b) If the Agency determines that an alternative location, removed from the area where
    the remediation waste originated, is more protective than managing remediation
    waste at the area of contamination or areas in close proximity, then the Agency
    must approve a RAP for this alternative location.
     
    c) An owner or operator must request the RAP, and the Agency must approve or deny
    the RAP, according to the procedures and requirements in this Subpart H.
     
    d) A RAP for an alternative location must also meet the following requirements, which
    the Agency must include in the RAP for such locations:
     
    1) The RAP for the alternative location must be issued to the person
    responsible for the cleanup from which the remediation wastes originated;
     
    2) The RAP is subject to the expanded public participation requirements in
    Sections 703.191, 703.192, and 703.193;
     
    3) The RAP is subject to the public notice requirements in 35 Ill. Adm. Code
    705.163;

     
    47
     
    4) The site permitted in the RAP may not be located within 61 meters or 200
    feet of a fault that has had displacement in the Holocene time. (The owner
    or operator must demonstrate compliance with this standard through the
    requirements in Section 703.183(k).) (See the definitions of terms in 35 Ill.
    Adm. Code 724.118(a).)
     
    BOARD NOTE: Sites in Illinois are assumed to be in compliance with the
    requirement of subsection (d)(4) of this Section, since they are not listed in
    appendix VI to 40 CFR 264, Appendix VI (Political Jurisdictions in Which
    Compliance with§ 264.18(a) Must Be Demonstrated).
     
    e) These alternative locations are remediation waste management sites, and retain the
    following benefits of remediation waste management sites:
     
    1) Exclusion from facility-wide corrective action under 35 Ill. Adm. Code
    724.201; and
     
    2) Application of 35 Ill. Adm. Code 724.101(j) in lieu of Subparts B, C, and D
    of 35 Ill. Adm. Code 724.
     
    BOARD NOTE: Derived from 40 CFR 270.230 (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART I: INTEGRATION WITH MAXIMUM ACHIEVABLE CONTROL
    TECHNOLOGY (MACT) STANDARDS
     
    Section 703.320 Options for Incinerators and Cement and Lightweight Aggregate Kilns to
    Minimize Emissions from Startup, Shutdown, and Malfunction Events
     
    a) Facilities with existing permits.
     
    1) Revisions to permit conditions after documenting compliance with
    MACT. The owner or operator of a RCRA-permitted incinerator, cement
    kiln, or lightweight aggregate kiln, when requesting removal of permit
    conditions that are no longer applicable according to 35 Ill. Adm. Code
    724.440(b) and 726.200(b), may request that the Agency address permit
    conditions that minimize emissions from startup, shutdown, and
    malfunction events under any of the following options:
     
    A) Retain relevant permit conditions. Under this option, the Agency
    must do the following:
     
    i) Retain permit conditions that address releases during
    startup, shutdown, and malfunction events, including

     
    48
    releases from emergency safety vents, as these events are
    defined in the facility’s startup, shutdown, and malfunction
    plan required under 40 CFR 63.1206(c)(2) (When and How
    Must You Comply with the Standards and Operating
    Requirements?), incorporated by reference in 35 Ill. Adm.
    Code 720.111 720.111(b); and
     
    ii) Limit applicability of those permit conditions only to when
    the facility is operating under its startup, shutdown, and
    malfunction plan.
     
    B) Revise relevant permit conditions. Under this option, the Agency
    must do the following:
     
    i) Identify a subset of relevant existing permit requirements,
    or develop alternative permit requirements, that ensure
    emissions of toxic compounds are minimized from startup,
    shutdown, and malfunction events, including releases from
    emergency safety vents, based on review of information
    including the source’s startup, shutdown, and malfunction
    plan, design, and operating history; and
     
    ii) Retain or add these permit requirements to the permit to
    apply only when the facility is operating under its startup,
    shutdown, and malfunction plan.
     
    iii) The owner or operator must comply with subsection (a)(3)
    of this Section.
     
    BOARD NOTE: The Board found it necessary to deviate from the
    structure of corresponding 40 CFR 270.235(a)(1)(ii) in this
    subsection (a)(1)(B) in order to comport with Illinois
    Adminisrative Administrative Code codification requirements.
    The substance of 40 CFR 270.235(a)(1)(ii)(A), (a)(1)(ii)(A)(
    1
    ),
    and (a)(1)(ii)(A)(
    2
    ) appear as subsections (a)(1)(B), (a)(1)(B)(i),
    and (a)(1)(B)(ii). The substance of 40 CFR 270.235(a)(1)(ii)(B)
    has been codified as subsection (a)(3) of this Section. Subsection
    (a)(1)(B)(iii) of this Section was added to direct attention to
    subsection (a)(3).
     
    C) Remove permit conditions. Under this option the following are
    required:
     
    i) The owner or operator must document that the startup,
    shutdown, and malfunction plan required under 40 CFR
    63.1206(c)(2), incorporated by reference in 35 Ill. Adm.

     
    49
    Code 720.111, has been approved by the Administrator
    under 40 CFR 63.1206(c)(2)(ii)(B), incorporated by
    reference in 35 Ill. Adm. Code 720.111; and
     
    ii) The Agency must remove permit conditions that are no
    longer applicable according to 35 Ill. Adm. Code
    724.440(b) and 726.200(b).
     
    2) Addressing permit conditions upon permit reissuance. The owner or
    operator of an incinerator, cement kiln, or lightweight aggregate kiln that
    has conducted a comprehensive performance test and submitted to the
    Agency a Notification of Compliance documenting compliance with the
    standards of subpart EEE of 40 CFR 63, subpart EEE (National Emission
    Standards for Hazardous Air Pollutants from Hazardous Waste
    Combustors), incorporated by reference in 35 Ill. Adm. Code 720.111§
    720.111(b), may request in the application to reissue the permit for the
    combustion unit that the Agency control emissions from startup,
    shutdown, and malfunction events under any of the following options:
     
    A) RCRA option A. Under this option, the Agency must do the
    following:
     
    i) Include, in the permit, conditions that ensure compliance
    with 35 Ill. Adm. Code 724.445(a) and (c) or 726.202(e)(1)
    and (e)(2)(C) to minimize emissions of toxic compounds
    from startup, shutdown, and malfunction events, including
    releases from emergency safety vents; and
     
    ii) Specify that these permit requirements apply only when the
    facility is operating under its startup, shutdown, and
    malfunction plan; or
     
    BOARD NOTE: The Board found it necessary to deviate from the
    structure of corresponding 40 CFR 270.235(a)(2)(i) in this
    subsection (a)(2)(A) in order to comport with Illinois
    Adminisrative Administrative Code codification requirements.
    The substance of 40 CFR 270.235(a)(2)(i)(A), (a)(2)(i)(A)(
    1
    ), and
    (a)(2)(i)(A)(
    2
    ) appear as subsections (a)(2)(A), (a)(2)(A)(i), and
    (a)(2)(A)(ii).
     
    B) RCRA option B. Under this option, the Agency must:
     
    i) Include, in the permit, conditions that ensure emissions of
    toxic compounds are minimized from startup, shutdown,
    and malfunction events, including releases from emergency
    safety vents, based on review of information including the

     
    50
    source’s startup, shutdown, and malfunction plan, design,
    and operating history; and
     
    ii) Specify that these permit requirements apply only when the
    facility is operating under its startup, shutdown, and
    malfunction plan.
     
    iii) The owner or operator must comply with subsection (a)(3)
    of this Section.
     
    BOARD NOTE: The Board found it necessary to deviate from the
    structure of corresponding 40 CFR 270.235(a)(2)(ii) in this
    subsection (a)(2)(B) in order to comport with Illinois
    Adminisrative Administrative Code codification requirements.
    The substance of 40 CFR 270.235(a)(2)(ii)(A), (a)(2)(ii)(A)(
    1
    ),
    and (a)(2)(ii)(A)(
    2
    ) appear as subsections (a)(2)(B), (a)(2)(B)(i),
    and (a)(2)(B)(ii). The substance of 40 CFR 270.235(a)(2)(ii)(B)
    has been codified as subsection (a)(3) of this Section. Subsection
    (a)(2)(B)(iii) of this Section was added to direct attention to
    subsection (a)(3).
     
    C) CAA option. Under this option the following are required:
     
    i) The owner or operator must document that the startup,
    shutdown, and malfunction plan required under 40 CFR
    63.1206(c)(2), incorporated by reference in 35 Ill. Adm.
    Code 720.111, has been approved by the Agency under 40
    CFR 63.1206(c)(2)(ii)(B), incorporated by reference in 35
    Ill. Adm. Code 720.111; and
     
    ii) The Agency must omit from the permit conditions that are
    not applicable under 35 Ill. Adm. Code 724.440(b) and
    726.200(b).
     
    3) Changes that may significantly increase emissions.
     
    A) The owner or operator must notify the Agency in writing of
    changes to the startup, shutdown, and malfunction plan or changes
    to the design of the source that may significantly increase
    emissions of toxic compounds from startup, shutdown, or
    malfunction events, including releases from emergency safety
    vents. The owner or operator must notify the Agency of such
    changes within five days of making such changes. The owner or
    operator must identify in the notification recommended revisions
    to permit conditions necessary as a result of the changes to ensure
    that emissions of toxic compounds are minimized during these

     
    51
    events.
     
    B) The Agency may revise permit conditions as a result of these
    changes to ensure that emissions of toxic compounds are
    minimized during startup, shutdown, or malfunction events,
    including releases from emergency safety vents in either of the
    following ways:
     
    i) Upon permit renewal; or;
     
    ii) If warranted, by modifying the permit under §§ 270.41(a)
    or 270.42 Sections 703.270 or 703.280 though 703.283.
     
    BOARD NOTE: The substance of 40 CFR 270.235(a)(1)(ii)(B) and (a)(2)(ii)(B)
    has been codified as this subsection (a)(3).
     
    b) Interim status facilities.
     
    1) Interim status operations. In compliance with 35 Ill. Adm. Code 725.440
    and 726.200(b), the owner or operator of an incinerator, cement kiln, or
    lightweight aggregate kiln that is operating under the interim status
    standards of 35 Ill. Adm. Code 725 or 726 may control emissions of toxic
    compounds during startup, shutdown, and malfunction events under either
    of the following options after conducting a comprehensive performance
    test and submitting to the Agency a Notification of Compliance
    documenting compliance with the standards of subpart EEE of 40 CFR 63,
    subpart EEE, incorporated by reference in 35 Ill. Adm. Code 720.111:
     
    A) RCRA option. Under this option, the owner or operator must
    continue to comply with the interim status emission standards and
    operating requirements of 35 Ill. Adm. Code 725 or 726 relevant to
    control of emissions from startup, shutdown, and malfunction
    events. Those standards and requirements apply only during
    startup, shutdown, and malfunction events; or
     
    B) CAA option. Under this option, the owner or operator is exempt
    from the interim status standards of 35 Ill. Adm. Code 725 or 726
    relevant to control of emissions of toxic compounds during startup,
    shutdown, and malfunction events upon submission of written
    notification and documentation to the Agency that the startup,
    shutdown, and malfunction plan required under 40 CFR
    63.1206(c)(2), incorporated by reference in 35 Ill. Adm. Code
    720.111, has been approved by the Agency under 40 CFR
    63.1206(c)(2)(ii)(B), incorporated by reference in 35 Ill. Adm.
    Code 720.111.
     

     
    52
    2) Operations under a subsequent RCRA permit. When an owner or operator
    of an incinerator, cement kiln, or lightweight aggregate kiln that is
    operating under the interim status standards of 35 Ill. Adm. Code 725 or
    726 submits a RCRA permit application, the owner or operator may
    request that the Agency control emissions from startup, shutdown, and
    malfunction events under any of the options provided by subsection
    (a)(2)(A), (a)(2)(B), or (a)(2)(C) of this Section.
     
    BOARD NOTE: Derived from 40 CFR 270.235 (2002) (2005). Operating conditions used to
    determine effective treatment of hazardous waste remain effective after the owner or operator
    demonstrates compliance with the standards of subpart EEE of 40 CFR 63, subpart EEE.
     
    (Source: Added at 30 Ill. Reg. ________, effective ______________________)
     
    Section 703.Appendix A Classification of Permit Modifications
     
    Class Modifications
     
      
    A. General Permit Provisions
     
      
    1 1. Administrative and informational changes.
     
      
    1 2. Correction of typographical errors.
     
      
    1 3. Equipment replacement or upgrading with functionally equivalent
    components (e.g., pipes, valves, pumps, conveyors, controls).
     
      
    4. Changes in the frequency of or procedures for monitoring, reporting,
    sampling, or maintenance activities by the permittee:
     
      
    1 a. To provide for more frequent monitoring, reporting, or
    maintenance.
     
      
    2 b. Other changes.
     
      
    5. Schedule of compliance:
     
      
    1* a. Changes in interim compliance dates, with prior approval of the
    Agency.
     
      
    3 b. Extension of final compliance date.
     
      
    1* 6. Changes in expiration date of permit to allow earlier permit termination,
    with prior approval of the Agency.
     
      

     
    53
    1* 7. Changes in ownership or operational control of a facility, provided the
    procedures of Section 703.260(b) are followed.
     
      
    1* 8. Changes to remove permit conditions that are no longer applicable (i.e.,
    because the standards upon which they are based are no longer
    applicable to the facility).
     
      
    B. General Facility Standards
     
      
    1. Changes to waste sampling or analysis methods:
     
      
    1 a. To conform with Agency guidance or Board regulations.
     
      
    1* b. To incorporate changes associated with F039 (multi-source
    leachate) sampling or analysis methods.
     
      
    1* c. To incorporate changes associated with underlying hazardous
    constituents in ignitable or corrosive wastes.
     
      
    2 d. Other changes.
     
      
    2. Changes to analytical quality assurance or quality control plan:
     
      
    1 a. To conform with agency guidance or regulations.
      
      
    2 b. Other changes.
     
      
    1 3. Changes in procedures for maintaining the operating record.
     
      
    2 4. Changes in frequency or content of inspection schedules.
     
      
    5. Changes in the training plan:
     
      
    2 a. That affect the type or decrease the amount of training given to
    employees.
     
      
    1 b. Other changes.
     
      
    6. Contingency plan:
     
      
    2 a. Changes in emergency procedures (i.e., spill or release response
    procedures).
     
      
    1 b. Replacement with functionally equivalent equipment, upgrade,
    or relocate emergency equipment listed.
     
      

     
    54
    2 c. Removal of equipment from emergency equipment list.
     
      
    1 d. Changes in name, address, or phone number of coordinators or
    other persons or agencies identified in the plan.
     
      
    Note: When a permit modification (such as introduction of a new unit)
    requires a change in facility plans or other general facility standards,
    that change must be reviewed under the same procedures as the permit
    modification.
     
      
    7. CQA plan:
     
      
    1 a. Changes that the CQA officer certifies in the operating record
    will provide equivalent or better certainty that the unit
    components meet the design specifications.
     
      
    2 b. Other changes.
     
      
    Note: When a permit modification (such as introduction of a new unit)
    requires a change in facility plans or other general facility standards,
    that change must be reviewed under the same procedures as a permit
    modification.
     
      
    C. Groundwater Protection
     
      
    1. Changes to wells:
     
      
    2 a. Changes in the number, location, depth, or design of upgradient
    or downgradient wells of permitted groundwater monitoring
    system.
     
      
    1 b. Replacement of an existing well that has been damaged or
    rendered inoperable, without change to location, design, or
    depth of the well.
     
      
    1* 2. Changes in groundwater sampling or analysis procedures or monitoring
    schedule, with prior approval of the Agency.
     
      
    1* 3. Changes in statistical procedure for determining whether a statistically
    significant change in groundwater quality between upgradient and
    downgradient wells has occurred, with prior approval of the Agency.
     
      
    2* 4. Changes in point of compliance.
      
      

     
    55
    5. Changes in indicator parameters, hazardous constituents, or
    concentration limits (including ACLs (Alternate Concentration
    Limits)):
     
      
    3 a. As specified in the groundwater protection standard.
     
      
    2 b. As specified in the detection monitoring program.
     
      
    2 6. Changes to a detection monitoring program as required by 35 Ill. Adm.
    Code 724.198(j), unless otherwise specified in this Appendix.
     
      
    7. Compliance monitoring program:
     
      
    3 a. Addition of compliance monitoring program as required by 35
    Ill. Adm. Code 724.198(h)(4) and 724.199.
     
      
    2 b. Changes to a compliance monitoring program as required by 35
    Ill. Adm. Code 724.199(k), unless otherwise specified in this
    Appendix.
     
      
    8. Corrective action program:
     
      
    3 a. Addition of a corrective action program as required by 35 Ill.
    Adm. Code 724.199(i)(2) and 724.200.
     
      
    2 b. Changes to a corrective action program as required by 35 Ill.
    Adm. Code 724.200(h), unless otherwise specified in this
    Appendix.
     
      
    D. Closure
     
      
    1. Changes to the closure plan:
     
      
    1* a. Changes in estimate of maximum extent of operations or
    maximum inventory of waste on-site at any time during the
    active life of the facility, with prior approval of the Agency.
     
      
    1* b. Changes in the closure schedule for any unit, changes in the
    final closure schedule for the facility or extension of the closure
    period, with prior approval of the Agency.
     
      
    1* c. Changes in the expected year of final closure, where other
    permit conditions are not changed, with prior approval of the
    Agency.
     
      

     
    56
    1* d. Changes in procedures for decontamination of facility
    equipment or structures, with prior approval of the Agency.
     
      
    2 e. Changes in approved closure plan resulting from unexpected
    events occurring during partial or final closure, unless otherwise
    specified in this Appendix.
     
      
    2 f. Extension of the closure period to allow a landfill, surface
    impoundment, or land treatment unit to receive non-hazardous
    wastes after final receipt of hazardous wastes under 35 Ill. Adm.
    Code 724.213(d) or (e).
     
      
    3 2. Creation of a new landfill unit as part of closure.
     
      
    3. Addition of the following new units to be used temporarily for closure
    activities:
     
      
    3 a. Surface impoundments.
     
      
    3 b. Incinerators.
     
      
    3 c. Waste piles that do not comply with 35 Ill. Adm. Code
    724.350(c).
     
      
    2 d. Waste piles that comply with 35 Ill. Adm. Code 724.350(c).
     
      
    2 e. Tanks or containers (other than specified in paragraph D(3)(f)
    below).
     
      
    1* f. Tanks used for neutralization, dewatering, phase separation, or
    component separation, with prior approval of the Agency.
     
      
    2 g. Staging piles.
     
      
    E. Post-Closure
     
      
    1 1. Changes in name, address, or phone number of contact in post-closure
    plan.
     
      
    2 2. Extension of post-closure care period.
     
      
    3 3. Reduction in the post-closure care period.
     
      
    1 4. Changes to the expected year of final closure, where other permit
    conditions are not changed.
     
      

     
    57
    2 5. Changes in post-closure plan necessitated by events occurring during
    the active life of the facility, including partial and final closure.
     
      
    F. Containers
     
      
    1. Modification or addition of container units:
     
      
    3 a. Resulting in greater than 25 percent increase in the facility’s
    container storage capacity, except as provided in F(1)(c) and
    F(4)(a).
     
      
    2 b. Resulting in up to 25 percent increase in the facility’s container
    storage capacity, except as provided in F(1)(c) and F(4)(a).
     
      
    1 c. Modification or addition of container units or treatment
    processes necessary to treat wastes that are restricted from land
    disposal to meet some or all of the applicable treatment
    standards, with prior approval of the Agency. This modification
    may also involve the addition of new waste codes or narrative
    description of wastes. It is not applicable to dioxin-containing
    wastes (F020, F021, F022, F023, F026, F027, and F028).
     
      
    2. Modification of container units without an increased capacity or
    alteration of the system:
     
      
    2 a. Modification of a container unit without increasing the capacity
    of the unit.
     
      
    1 b. Addition of a roof to a container unit without alteration of the
    containment system.
     
      
    3. Storage of different wastes in containers, except as provided in F(4):
     
      
    3 a. That require additional or different management practices from
    those authorized in the permit.
     
      
    2 b. That do not require additional or different management practices
    from those authorized in the permit.
     
      
    Note: See Section 703.280(g) for modification procedures to be
    used for the management of newly listed or identified wastes.
     
      
    4. Storage or treatment of different wastes in containers:
     
      

     
    58
    2 a. That require addition of units or change in treatment process or
    management standards, provided that the wastes are restricted
    from land disposal and are to be treated to meet some or all of
    the applicable treatment standards. It is not applicable to
    dioxin-containing wastes (F020, F021, F022, F023, F026, F027,
    and F028).
     
      
    1* b. That do not require the addition of units or a change in the
    treatment process or management standards, and provided that
    the units have previously received wastes of the same type (e.g.,
    incinerator scrubber water). This modification is not applicable
    to dioxin-containing wastes (F020, F021, F022, F023, F026,
    F027, and F028).
     
      
    G. Tanks
     
      
    1.
     
      
    3 a. Modification or addition of tank units resulting in greater than
    25 percent increase in the facility’s tank capacity, except as
    provided in paragraphs G(1)(c), G(1)(d), and G(1)(e).
     
      
    2 b. Modification or addition of tank units resulting in up to 25
    percent increase in the facility’s tank capacity, except as
    provided in paragraphs G(1)(d) and G(1)(e).
     
      
    2 c. Addition of a new tank that will operate for more than 90 days
    using any of the following physical or chemical treatment
    technologies: neutralization, dewatering, phase separation, or
    component separation.
     
      
    1* d. After prior approval of the Agency, addition of a new tank that
    will operate for up to 90 days using any of the following
    physical or chemical treatment technologies: neutralization,
    dewatering, phase separation, or component separation.
     
      
    1* e. Modification or addition of tank units or treatment processes
    that are necessary to treat wastes that are restricted from land
    disposal to meet some or all of the applicable treatment
    standards, with prior approval of the Agency. This modification
    may also involve the addition of new waste codes. It is not
    applicable to dioxin-containing wastes (F020, F021, F022,
    F023, F026, F027, and F028).
     
      
    2 2. Modification of a tank unit or secondary containment system without
    increasing the capacity of the unit.

     
    59
     
      
    1 3. Replacement of a tank with a tank that meets the same design standards
    and has a capacity within
    ±
    10 percent of the replaced tank provided:
     
      
    a. The capacity difference is no more than 1500 gallons,
     
      
    b. The facility’s permitted tank capacity is not increased, and
     
      
    c. The replacement tank meets the same conditions in the permit.
     
      
    2 4. Modification of a tank management practice.
     
      
    5. Management of different wastes in tanks:
     
      
    3 a. That require additional or different management practices, tank
    design, different fire protection specifications or significantly
    different tank treatment process from that authorized in the
    permit, except as provided in paragraph G(5)(c).
     
      
    2 b. That do not require additional or different management practices
    or tank design, different fire protection specification, or
    significantly different tank treatment process than authorized in
    the permit, except as provided in paragraph G(5)(d).
     
      
    Note: See Section 703.280(g) for modification procedures to be
    used for the management of newly listed or identified wastes.
     
      
    1* c. That require addition of units or change in treatment processes
    or management standards, provided that the wastes are restricted
    from land disposal and are to be treated to meet some or all of
    the applicable treatment standards. The modification is not
    applicable to dioxin-containing wastes (F020, F021, F022,
    F023, F026, F027, and F028).
     
      
    1 d. That do not require the addition of units or a change in the
    treatment process or management standards, and provided that
    the units have previously received wastes of the same type (e.g.,
    incinerator scrubber water). This modification is not applicable
    to dioxin-containing wastes (F020, F021, F022, F023, F026,
    F027, and F028).
     
      
    Note: See Section 703.280(g) for modification procedures to be
    used for the management of newly listed or identified wastes.
     
      
    H. Surface Impoundments
     
      

     
    60
    3 1. Modification or addition of surface impoundment units that result in
    increasing the facility’s surface impoundment storage or treatment
    capacity.
     
      
    3 2. Replacement of a surface impoundment unit.
     
      
    2 3. Modification of a surface impoundment unit without increasing the
    facility’s surface impoundment storage or treatment capacity and
    without modifying the unit’s liner, leak detection system, or leachate
    collection system.
     
      
    2 4. Modification of a surface impoundment management practice.
      
      
    5. Treatment, storage, or disposal of different wastes in surface
    impoundments:
     
      
    3 a. That require additional or different management practices or
    different design of the liner or leak detection system than
    authorized in the permit.
     
      
    2 b. That do not require additional or different management practices
    or different design of the liner or leak detection system than
    authorized in the permit.
     
      
    Note: See Section 703.280(g) for modification procedures to be
    used for the management of newly listed or identified wastes.
     
      
    1 c. That are wastes restricted from land disposal that meet the
    applicable treatment standards. This modification is not
    applicable to dioxin-containing wastes (F020, F021, F022,
    F023, F026, F027, and F028).
     
      
    1 d. That are residues from wastewater treatment or incineration,
    provided the disposal occurs in a unit that meets the minimum
    technological requirements stated in 40 CFR 268.5(h)(2)
    (Procedures for Case-by-Case Extensions to an Effective Date),
    incorporated by reference in 35 Ill. Adm. Code 728.105
    720.111(b), and provided further that the surface impoundment
    has previously received wastes of the same type (for example,
    incinerator scrubber water). This modification is not applicable
    to dioxin-containing wastes (F020, F021, F022, F023, F026,
    F027, and F028).
     
      
    1* 6. Modifications of unconstructed units to comply with 35 Ill. Adm. Code
    724.321(c), 724.322, 724.323, and 724.326(d).
     
      

     
    61
    7. Changes in response action plan:
     
      
    3 a. Increase in action leakage rate.
     
      
    3 b. Change in a specific response reducing its frequency or
    effectiveness.
     
      
    2 c. Other changes.
     
      
    Note: See Section 703.280(g) for modification procedures to be
    used for the management of newly listed or identified wastes.
     
      
    I. Enclosed Waste Piles. For all waste piles, except those complying with 35 Ill.
    Adm. Code 724.350(c), modifications are treated the same as for a landfill.
    The following modifications are applicable only to waste piles complying with
    35 Ill. Adm. Code 724.350(c).
     
      
    1. Modification or addition of waste pile units:
     
      
    3 a. Resulting in greater than 25 percent increase in the facility’s
    waste pile storage or treatment capacity.
     
      
    2 b. Resulting in up to 25 percent increase in the facility’s waste pile
    storage or treatment capacity.
      
      
    2 2. Modification of waste pile unit without increasing the capacity of the
    unit.
     
      
    1 3. Replacement of a waste pile unit with another waste pile unit of the
    same design and capacity and meeting all waste pile conditions in the
    permit.
     
      
    2 4. Modification of a waste pile management practice.
     
      
    5. Storage or treatment of different wastes in waste piles:
     
      
    3 a. That require additional or different management practices or
    different design of the unit.
     
      
    2 b. That do not require additional or different management practices
    or different design of the unit.
     
      
    Note: See Section 703.280(g) for modification procedures to be
    used for the management of newly listed or identified wastes.
     
      
    2 6. Conversion of an enclosed waste pile to a containment building unit.

     
    62
     
      
    Note: See Section 703.280(g) for modification procedures to be used
    for the management of newly listed or identified wastes.
     
      
    J. Landfills and Unenclosed Waste Piles
     
      
    3 1. Modification or addition of landfill units that result in increasing the
    facility’s disposal capacity.
     
      
    3 2. Replacement of a landfill.
     
      
    3 3. Addition or modification of a liner, leachate collection system, leachate
    detection system, runoff control, or final cover system.
     
      
    2 4. Modification of a landfill unit without changing a liner, leachate
    collection system, leachate detection system, runoff control, or final
    cover system.
     
      
    2 5. Modification of a landfill management practice.
     
      
    6. Landfill different wastes:
     
      
    3 a. That require additional or different management practices,
    different design of the liner, leachate collection system, or
    leachate detection system.
     
      
    2 b. That do not require additional or different management
    practices, different design of the liner, leachate collection
    system, or leachate detection system.
     
      
    Note: See Section 703.280(g) for modification procedures to be
    used for the management of newly listed or identified wastes.
     
      
    1 c. That are wastes restricted from land disposal that meet the
    applicable treatment standards. This modification is not
    applicable to dioxin-containing wastes (F020, F021, F022,
    F023, F026, F027, and F028).
     
      

     
    63
    1 d. That are residues from wastewater treatment or incineration,
    provided the disposal occurs in a landfill unit that meets the
    minimum technological requirements stated in 40 CFR
    268.5(h)(2) (Procedures for Case-by-Case Extensions to an
    Effective Date), incorporated by reference in 35 Ill. Adm. Code
    728.105 720.111(b), and provided further that the landfill has
    previously received wastes of the same type (for example,
    incinerator ash). This modification is not applicable to dioxin-
    containing wastes (F020, F021, F022, F023, F026, F027, and
    F028).
     
      
    1* 7. Modification of unconstructed units to comply with 35 Ill. Adm. Code
    724.351(c), 724.352, 724.353, 724.354(c), 724.401(c), 724.402,
    724.403(c), and 724.404.
     
      
    8. Changes in response action plan:
     
      
    3 a. Increase in action leakage rate.
     
      
    3 b. Change in a specific response reducing its frequency or
    effectiveness.
     
      
    2 c. Other changes.
     
      
    Note: See Section 703.280(g) for modification procedures to be
    used for the management of newly listed or identified wastes.
     
      
    K. Land Treatment
     
      
    3 1. Lateral expansion of or other modification of a land treatment unit to
    increase area extent.
     
      
    2 2. Modification of runon control system.
     
      
    3 3. Modify runoff control system.
     
      
    2 4. Other modification of land treatment unit component specifications or
    standards required in permit.
     
      
    5. Management of different wastes in land treatment units:
     
      
    3 a. That require a change in permit operating conditions or unit
    design specifications.
     
      
    2 b. That do not require a change in permit operating conditions or
    unit design specifications.

     
    64
     
      
    Note: See Section 703.280(g) for modification procedures to be
    used for the management of newly listed or identified wastes.
     
      
    6. Modification of a land treatment unit management practice to:
     
      
    3 a. Increase rate or change method of waste application.
     
      
    1 b. Decrease rate of waste application.
     
      
    2 7. Modification of a land treatment unit management practice to change
    measures of pH or moisture content or to enhance microbial or
    chemical reactions.
     
      
    3 8. Modification of a land treatment unit management practice to grow
    food chain crops, to add to or replace existing permitted crops with
    different food chain crops or to modify operating plans for distribution
    of animal feeds resulting from such crops.
     
      
    3 9. Modification of operating practice due to detection of releases from the
    land treatment unit pursuant to 35 Ill. Adm. Code 724.378(g)(2).
     
      
    3 10. Changes in the unsaturated zone monitoring system that result in a
    change to the location, depth, or number of sampling points or which
    replace unsaturated zone monitoring devices or components of devices
    with devices or components that have specifications different from
    permit requirements.
     
      
    2 11. Changes in the unsaturated zone monitoring system that do not result in
    a change to the location, depth, or number of sampling points or which
    replace unsaturated zone monitoring devices or components of devices
    with devices or components having specifications different from permit
    requirements.
     
      
    2 12. Changes in background values for hazardous constituents in soil and
    soil-pore liquid.
     
      
    2 13. Changes in sampling, analysis, or statistical procedure.
     
      
    2 14. Changes in land treatment demonstration program prior to or during the
    demonstration.
     
      
    1* 15. Changes in any condition specified in the permit for a land treatment
    unit to reflect results of the land treatment demonstration, provided
    performance standards are met, and the Agency’s prior approval has
    been received.

     
    65
     
      
    1* 16. Changes to allow a second land treatment demonstration to be
    conducted when the results of the first demonstration have not shown
    the conditions under which the wastes can be treated completely,
    provided the conditions for the second demonstration are substantially
    the same as the conditions for the first demonstration and have received
    the prior approval of the Agency.
     
      
    3 17. Changes to allow a second land treatment demonstration to be
    conducted when the results of the first demonstration have not shown
    the conditions under which the wastes can be treated completely, where
    the conditions for the second demonstration are not substantially the
    same as the conditions for the first demonstration.
     
      
    2 18. Changes in vegetative cover requirements for closure.
     
      
    L. Incinerators, Boilers and Industrial Furnaces
     
      
    3 1. Changes to increase by more than 25 percent any of the following limits
    authorized in the permit: A thermal feed rate limit, a feedstream feed
    rate limit, a chlorine/chloride feed rate limit, a metal feed rate limit, or
    an ash feed rate limit. The Agency must require a new trial burn to
    substantiate compliance with the regulatory performance standards
    unless this demonstration can be made through other means.
     
      
    2 2. Changes to increase by up to 25 percent any of the following limits
    authorized in the permit: A thermal feed rate limit, a feedstream feed
    rate limit, a chlorine/chloride feed rate limit, a metal feed rate limit, or
    an ash feed rate limit. The Agency must require a new trial burn to
    substantiate compliance with the regulatory performance standards
    unless this demonstration can be made through other means.
     
      
    3 3. Modification of an incinerator, boiler, or industrial furnace unit by
    changing the internal size or geometry of the primary or secondary
    combustion units; by adding a primary or secondary combustion unit;
    by substantially changing the design of any component used to remove
    HCl/Cl2, metals, or particulate from the combustion gases; or by
    changing other features of the incinerator, boiler, or industrial furnace
    that could affect its capability to meet the regulatory performance
    standards. The Agency must require a new trial burn to substantiate
    compliance with the regulatory performance standards, unless this
    demonstration can be made through other means.
     
      

     
    66
    2 4. Modification of an incinerator, boiler, or industrial furnace unit in a
    manner that will not likely affect the capability of the unit to meet the
    regulatory performance standards but which will change the operating
    conditions or monitoring requirements specified in the permit. The
    Agency may require a new trial burn to demonstrate compliance with
    the regulatory performance standards.
     
      
    5. Operating requirements:
     
      
    3 a. Modification of the limits specified in the permit for minimum
    or maximum combustion gas temperature, minimum combustion
    gas residence time, oxygen concentration in the secondary
    combustion chamber, flue gas carbon monoxide or hydrocarbon
    concentration, maximum temperature at the inlet to the PM
    emission control system, or operating parameters for the air
    pollution control system. The Agency must require a new trial
    burn to substantiate compliance with the regulatory performance
    standards unless this demonstration can be made through other
    means.
     
      
    3 b. Modification of any stack gas emission limits specified in the
    permit, or modification of any conditions in the permit
    concerning emergency shutdown or automatic waste feed cutoff
    procedures or controls.
     
      
    2 c. Modification of any other operating condition or any inspection
    or recordkeeping requirement specified in the permit.
     
      
    6. Burning different wastes:
     
      
    3 a. If the waste contains a POHC that is more difficult to burn than
    authorized by the permit or if burning of the waste requires
    compliance with different regulatory performance standards
    than specified in the permit, the Agency must require a new trial
    burn to substantiate compliance with the regulatory performance
    standards, unless this demonstration can be made through other
    means.
     
      
    2 b. If the waste does not contain a POHC that is more difficult to
    burn than authorized by the permit and if burning of the waste
    does not require compliance with different regulatory
    performance standards than specified in the permit.
     
      
    Note: See Section 703.280(g) for modification procedures to be
    used for the management of newly listed or identified wastes.
     
      

     
    67
    7. Shakedown and trial burn:
     
      
    2 a. Modification of the trial burn plan or any of the permit
    conditions applicable during the shakedown period for
    determining operational readiness after construction, the trial
    burn period or the period immediately following the trial burn.
     
      
    1* b. Authorization of up to an additional 720 hours of waste burning
    during the shakedown period for determining operational
    readiness after construction, with the prior approval of the
    Agency.
     
      
    1* c. Changes in the operating requirements set in the permit for
    conducting a trial burn, provided the change is minor and has
    received the prior approval of the Agency.
     
      
    1* d. Changes in the ranges of the operating requirements set in the
    permit to reflect the results of the trial burn, provided the change
    is minor and has received the prior approval of the Agency.
     
      
    1 8. Substitution of an alternative type of non-hazardous waste fuel that is
    not specified in the permit.
     
      
    1* 9. Technology changes needed to meet standards under federal subpart
    EEE of 40 CFR 63 (subpart EEE--National Emission Standards for
    Hazardous Air Pollutants From from Hazardous Waste Combustors),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b), provided
    the procedures of Section 703.280(j) are followed.
     
      
    M. Containment Buildings
     
      
    1. Modification or addition of containment building units:
     
      
    3 a. Resulting in greater than 25 percent increase in the facility’s
    containment building storage or treatment capacity.
     
      
    2 b. Resulting in up to 25 percent increase in the facility’s
    containment building storage or treatment capacity.
     
      
    2 2. Modification of a containment building unit or secondary containment
    system without increasing the capacity of the unit.
     
      
    3. Replacement of a containment building with a containment building
    that meets the same design standards provided:
     
      
    1 a. The unit capacity is not increased.

     
    68
     
      
    1 b. The replacement containment building meets the same
    conditions in the permit.
     
      
    2 4. Modification of a containment building management practice.
     
      
    5. Storage or treatment of different wastes in containment buildings:
     
      
    3 a. That require additional or different management practices.
     
      
    2 b. That do not require additional or different management
    practices.
     
      
    N. Corrective Action
     
      
    3 1. Approval of a corrective action management unit pursuant to 35 Ill.
    Adm. Code 724.652.
     
      
    2 2. Approval of a temporary unit or time extension pursuant to 35 Ill. Adm.
    Code 724.653.
     
      
    2 3. Approval of a staging pile or staging pile operating term extension
    pursuant to 35 Ill. Adm. Code 724.654.
     
      
    Note: * indicates modifications requiring prior Agency approval.
     
    BOARD NOTE: Derived from appendix I to 40 CFR 270.42, Appendix I (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
     
    PART 720
    HAZARDOUS WASTE MANAGEMENT SYSTEM: GENERAL
     
    SUBPART A: GENERAL PROVISIONS
    Section
    720.101 Purpose, Scope, and Applicability
    720.102 Availability of Information; Confidentiality of Information
    720.103 Use of Number and Gender
     

     
    69
    SUBPART B: DEFINITIONS AND REFERENCES
    Section
    720.110 Definitions
    720.111 References
     
    SUBPART C: RULEMAKING PETITIONS AND OTHER PROCEDURES
    Section
    720.120 Rulemaking
    720.121 Alternative Equivalent Testing Methods
    720.122 Waste Delisting
    720.123 Petitions for Regulation as Universal Waste
    720.130 Procedures for Solid Waste Determinations
    720.131 Solid Waste Determinations
    720.132 Boiler Determinations
    720.133 Procedures for Determinations
    720.140 Additional Regulation of Certain Hazardous Waste Recycling Activities on a
    Case-by-Case Basis
    720.141 Procedures for Case-by-Case Regulation of Hazardous Waste Recycling
    Activities
     
    720.Appendix A Overview of 40 CFR, Federal RCRA Subtitle C (Hazardous Waste)
    Regulations
     
    AUTHORITY: Implementing Sections 7.2, 13, and 22.4 and authorized by Section 27 of the
    Environmental Protection Act [415 ILCS 5/7.2, 13, 22.4, and 27].
     
    SOURCE: Adopted in R81-22 at 5 Ill. Reg. 9781, effective May 17, 1982; amended and
    codified in R81-22 at 6 Ill. Reg. 4828, effective May 17, 1982; amended in R82-19 at 7 Ill. Reg.
    14015, effective October 12, 1983; amended in R84-9 at 9 Ill. Reg. 11819, effective July 24,
    1985; amended in R85-22 at 10 Ill. Reg. 968, effective January 2, 1986; amended in R86-1 at 10
    Ill. Reg. 13998, effective August 12, 1986; amended in R86-19 at 10 Ill. Reg. 20630, effective
    December 2, 1986; amended in R86-28 at 11 Ill. Reg. 6017, effective March 24, 1987; amended
    in R86-46 at 11 Ill. Reg. 13435, effective August 4, 1987; amended in R87-5 at 11 Ill. Reg.
    19280, effective November 12, 1987; amended in R87-26 at 12 Ill. Reg. 2450, effective January
    15, 1988; amended in R87-39 at 12 Ill. Reg. 12999, effective July 29, 1988; amended in R88-16
    at 13 Ill. Reg. 362, effective December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18278,
    effective November 13, 1989; amended in R89-2 at 14 Ill. Reg. 3075, effective February 20,
    1990; amended in R89-9 at 14 Ill. Reg. 6225, effective April 16, 1990; amended in R90-10 at 14
    Ill. Reg. 16450, effective September 25, 1990; amended in R90-17 at 15 Ill. Reg. 7934, effective
    May 9, 1991; amended in R90-11 at 15 Ill. Reg. 9323, effective June 17, 1991; amended in R91-
    1 at 15 Ill. Reg. 14446, effective September 30, 1991; amended in R91-13 at 16 Ill. Reg. 9489,
    effective June 9, 1992; amended in R92-1 at 16 Ill. Reg. 17636, effective November 6, 1992;
    amended in R92-10 at 17 Ill. Reg. 5625, effective March 26, 1993; amended in R93-4 at 17 Ill.
    Reg. 20545, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6720, effective
    April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12160, effective July 29, 1994; amended in
    R94-17 at 18 Ill. Reg. 17480, effective November 23, 1994; amended in R95-6 at 19 Ill. Reg.

     
    70
    9508, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 10929, effective August 1,
    1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 256, effective December 16, 1997;
    amended in R98-12 at 22 Ill. Reg. 7590, effective April 15, 1998; amended in R97-21/R98-
    3/R98-5 at 22 Ill. Reg. 17496, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at
    23 Ill. Reg. 1704, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9094, effective
    July 26, 1999; amended in R00-5 at 24 Ill. Reg. 1063, effective January 6, 2000; amended in
    R00-13 at 24 Ill. Reg. 9443, effective June 20, 2000; amended in R01-3 at 25 Ill. Reg. 1266,
    effective January 11, 2001; amended in R01-21/R01-23 at 25 Ill. Reg. 9168, effective July 9,
    2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. 6550, effective April 22, 2002; amended
    in R03-7 at 27 Ill. Reg. 3712, effective February 14, 2003; amended in R03-18 at 27 Ill. Reg.
    12713, effective July 17, 2003; amended in R05-8 at 29 Ill. Reg. 5974, effective April 13, 2005;
    amended in R05-2 at 29 Ill. Reg. 6290, effective April 22, 2005; amended in R06-5/R06-6/R06-7
    at 30 Ill. Reg. ________, effective ______________________.
     
    SUBPART B: DEFINITIONS AND REFERENCES
     
    Section 720.110 Definitions
     
    When used in 35 Ill. Adm. Code 720 through 726, 728, 733, and 739 only, the following terms have
    the meanings given below:
     
    “Aboveground tank” means a device meeting the definition of tank that is situated in
    such a way that the entire surface area of the tank is completely above the plane of
    the adjacent surrounding surface and the entire surface area of the tank (including the
    tank bottom) is able to be visually inspected.
     
    “Active life” of a facility means the period from the initial receipt of hazardous waste
    at the facility until the Agency receives certification of final closure.
     
    “Active portion” means that portion of a facility where treatment, storage, or disposal
    operations are being or have been conducted after May 19, 1980, and which is not a
    closed portion. (See also “closed portion” and “inactive portion.”)
     
    “Administrator” means the Administrator of the United States Environmental
    Protection Agency or the Administrator’s designee.
     
    “Agency” means the Illinois Environmental Protection Agency.
     
    “Ancillary equipment” means any device, including, but not limited to, such devices
    as piping, fittings, flanges, valves, and pumps, that is used to distribute, meter, or
    control the flow of hazardous waste from its point of generation to storage or
    treatment tanks, between hazardous waste storage and treatment tanks to a point of
    disposal onsite, or to a point of shipment for disposal off-site.
     
    “Aquifer” means a geologic formation, group of formations, or part of a formation
    capable of yielding a significant amount of groundwater to wells or springs.

     
    71
     
    “Authorized representative” means the person responsible for the overall operation
    of a facility or an operational unit (i.e., part of a facility), e.g., the plant manager,
    superintendent, or person of equivalent responsibility.
     
    “Battery” means a device that consists of one or more electrically connected
    electrochemical cells which is designed to receive, store, and deliver electric energy.
    An electrochemical cell is a system consisting of an anode, cathode, and an
    electrolyte, plus such connections (electrical and mechanical) as may be needed to
    allow the cell to deliver or receive electrical energy. The term battery also includes
    an intact, unbroken battery from which the electrolyte has been removed.
     
    “Board” means the Illinois Pollution Control Board.
     
    “Boiler” means an enclosed device using controlled flame combustion and having
    the following characteristics:
     
    Boiler physical characteristics.
     
    The unit must have physical provisions for recovering and exporting
    thermal energy in the form of steam, heated fluids, or heated gases;
    and the unit’s combustion chamber and primary energy recovery
    sections must be of integral design. To be of integral design, the
    combustion chamber and the primary energy recovery sections (such
    as waterwalls and superheaters) must be physically formed into one
    manufactured or assembled unit. A unit in which the combustion
    chamber and the primary energy recovery sections are joined only by
    ducts or connections carrying flue gas is not integrally designed;
    however, secondary energy recovery equipment (such as
    economizers or air preheaters) need not be physically formed into the
    same unit as the combustion chamber and the primary energy
    recovery section. The following units are not precluded from being
    boilers solely because they are not of integral design: process heaters
    (units that transfer energy directly to a process stream) and fluidized
    bed combustion units; and
     
    While in operation, the unit must maintain a thermal energy recovery
    efficiency of at least 60 percent, calculated in terms of the recovered
    energy compared with the thermal value of the fuel; and
     
    The unit must export and utilize at least 75 percent of the recovered
    energy, calculated on an annual basis. In this calculation, no credit
    may be given for recovered heat used internally in the same unit.
    (Examples of internal use are the preheating of fuel or combustion
    air, and the driving of induced or forced draft fans or feedwater
    pumps.); or

     
    72
     
    Boiler by designation. The unit is one that the Board has determined, on a
    case-by-case basis, to be a boiler, after considering the standards in Section
    720.132.
     
    “Carbon regeneration unit” means any enclosed thermal treatment device used to
    regenerate spent activated carbon.
     
    “Certification” means a statement of professional opinion based upon knowledge and
    belief.
     
    “Closed portion” means that portion of a facility that an owner or operator has closed
    in accordance with the approved facility closure plan and all applicable closure
    requirements. (See also “active portion” and “inactive portion.”)
     
    “Component” means either the tank or ancillary equipment of a tank system.
     
    “Confined aquifer” means an aquifer bounded above and below by impermeable
    beds or by beds of distinctly lower permeability than that of the aquifer itself; an
    aquifer containing confined groundwater.
     
    “Container” means any portable device in which a material is stored, transported,
    treated, disposed of, or otherwise handled.
     
    “Containment building” means a hazardous waste management unit that is used to
    store or treat hazardous waste under the provisions of Subpart DD of 35 Ill. Adm.
    Code 724 and Subpart DD of 35 Ill. Adm. Code 725.
     
    “Contingency plan” means a document setting out an organized, planned and
    coordinated course of action to be followed in case of a fire, explosion, or release of
    hazardous waste or hazardous waste constituents that could threaten human health or
    the environment.
     
    “Corrosion expert” means a person who, by reason of knowledge of the physical
    sciences and the principles of engineering and mathematics, acquired by a
    professional education and related practical experience, is qualified to engage in the
    practice of corrosion control on buried or submerged metal piping systems and metal
    tanks. Such a person must be certified as being qualified by the National Association
    of Corrosion Engineers (NACE) or be a registered professional engineer who has
    certification or licensing that includes education and experience in corrosion control
    on buried or submerged metal piping systems and metal tanks.
     
    “Designated facility” means a hazardous waste treatment, storage, or disposal
    facility, either of the following entities:
     
    Of A hazardous waste treatment, storage, or disposal facility that has been

     
    73
    designated on the manifest by the generator, pursuant to 35 Ill. Adm. Code
    722.120, of which any of the following is true:
     
    The facility has received a RCRA permit (or interim status) pursuant
    to 35 Ill. Adm. Code 702, 703, and 705;
     
    The facility has received a RCRA permit from USEPA pursuant to 40
    CFR 124 and 270 (2002) (2005);
     
    The facility has received a RCRA permit from a state authorized by
    USEPA pursuant to 40 CFR 271 (2002) (2005); or
     
    The facility is regulated under 35 Ill. Adm. Code 721.106(c)(2) or
    Subpart F of 35 Ill. Adm. Code 266; and or
     
    The facility has been designated on the manifest by the generator pursuant
    to 35 Ill. Adm. Code 722.120.
     
    Effective September 5, 2006, a generator site designated by the hazardous
    waste generator on the manifest to receive back its own waste as a return
    shipment from a designated hazardous waste treatment, storage, or
    disposal facility that has rejected the waste in accordance with 35 Ill.
    Adm. Code 724.172(f) or 725.172(f).
     
    If a waste is destined to a facility in a state other than Illinois that has been
    authorized by USEPA pursuant to 40 CFR 271, but which has not yet
    obtained authorization to regulate that waste as hazardous, then the
    designated facility must be a facility allowed by the receiving state to accept
    such waste.
     
    “Destination facility” means a facility that treats, disposes of, or recycles a particular
    category of universal waste, except those management activities described in 35 Ill.
    Adm. Code 733.113(a) and (c) and 733.133(a) and (c). A facility at which a
    particular category of universal waste is only accumulated is not a destination facility
    for the purposes of managing that category of universal waste.
     
    “Dike” means an embankment or ridge of either natural or manmade materials used
    to prevent the movement of liquids, sludges, solids, or other materials.
     
    “Dioxins and furans” or “D/F” means tetra, penta-, hexa-, hepta-, and octa-
    chlorinated dibenzo dioxins and furans.
     
    “Director” means the Director of the Illinois Environmental Protection Agency.
     
    “Discharge” or “hazardous waste discharge” means the accidental or intentional
    spilling, leaking, pumping, pouring, emitting, emptying, or dumping of hazardous

     
    74
    waste into or on any land or water.
     
    “Disposal” means the discharge, deposit, injection, dumping, spilling, leaking, or
    placing of any solid waste or hazardous waste into or on any land or water so that
    such solid waste or hazardous waste or any constituent thereof may enter the
    environment or be emitted into the air or discharged into any waters, including
    groundwaters.
     
    “Disposal facility” means a facility or part of a facility at which hazardous waste is
    intentionally placed into or on any land or water and at which waste will remain after
    closure. The term disposal facility does not include a corrective action management
    unit (CAMU) into which remediation wastes are placed.
     
    “Drip pad” means an engineered structure consisting of a curbed, free-draining base,
    constructed of non-earthen materials and designed to convey preservative kick-back
    or drippage from treated wood, precipitation and surface water runon to an
    associated collection system at wood preserving plants.
     
    “Elementary neutralization unit” means a device of which the following is true:
     
    It is used for neutralizing wastes that are hazardous only because they exhibit
    the corrosivity characteristic defined in 35 Ill. Adm. Code 721.122 or which
    are listed in Subpart D of 35 Ill. Adm. Code 721 only for this reason; and
     
    It meets the definition of tank, tank system, container, transport vehicle, or
    vessel in this Section.
     
    “EPA hazardous waste number” or “USEPA hazardous waste number” means the
    number assigned by USEPA to each hazardous waste listed in Subpart D of 35 Ill.
    Adm. Code 721 and to each characteristic identified in Subpart C of 35 Ill. Adm.
    Code 721.
     
    “EPA identification number” or “USEPA identification number” means the number
    assigned by USEPA pursuant to 35 Ill. Adm. Code 722 through 725 to each
    generator; transporter; and treatment, storage, or disposal facility.
     
    “EPA region” or “USEPA region” means the states and territories found in any one
    of the following ten regions:
     
    Region I: Maine, Vermont, New Hampshire, Massachusetts, Connecticut,
    and Rhode Island
     
    Region II: New York, New Jersey, Commonwealth of Puerto Rico, and the
    U.S. Virgin Islands
     
    Region III: Pennsylvania, Delaware, Maryland, West Virginia, Virginia, and

     
    75
    the District of Columbia
     
    Region IV: Kentucky, Tennessee, North Carolina, Mississippi, Alabama,
    Georgia, South Carolina, and Florida
     
    Region V: Minnesota, Wisconsin, Illinois, Michigan, Indiana, and Ohio
     
    Region VI: New Mexico, Oklahoma, Arkansas, Louisiana, and Texas
     
    Region VII: Nebraska, Kansas, Missouri, and Iowa
     
    Region VIII: Montana, Wyoming, North Dakota, South Dakota, Utah, and
    Colorado
     
    Region IX: California, Nevada, Arizona, Hawaii, Guam, American Samoa,
    and Commonwealth of the Northern Mariana Islands
     
    Region X: Washington, Oregon, Idaho, and Alaska
     
    “Equivalent method” means any testing or analytical method approved by the Board
    pursuant to Section 720.120.
     
    “Existing hazardous waste management (HWM) facility” or “existing facility”
    means a facility that was in operation or for which construction commenced on or
    before November 19, 1980. A facility had commenced construction if the owner or
    operator had obtained the federal, State, and local approvals or permits necessary to
    begin physical construction and either of the following had occurred:
     
    A continuous on-site, physical construction program had begun; or
     
    The owner or operator had entered into contractual obligations that could not
    be canceled or modified without substantial loss for physical construction of
    the facility to be completed within a reasonable time.
     
    “Existing portion” means that land surface area of an existing waste management
    unit, included in the original Part A permit application, on which wastes have been
    placed prior to the issuance of a permit.
     
    “Existing tank system” or “existing component” means a tank system or component
    that is used for the storage or treatment of hazardous waste and which was in
    operation, or for which installation was commenced, on or prior to July 14, 1986.
    Installation will be considered to have commenced if the owner or operator has
    obtained all federal, State, and local approvals or permits necessary to begin physical
    construction of the site or installation of the tank system and if either of the following
    is true:
     

     
    76
    A continuous on-site physical construction or installation program has begun;
    or
     
    The owner or operator has entered into contractual obligations that cannot be
    canceled or modified without substantial loss for physical construction of the
    site or installation of the tank system to be completed within a reasonable
    time.
     
    “Explosives or munitions emergency” means a situation involving the suspected
    or detected presence of unexploded ordnance (UXO), damaged or deteriorated
    explosives or munitions, an improvised explosive device (IED), other potentially
    explosive material or device, or other potentially harmful military chemical
    munitions or device, that creates an actual or potential imminent threat to human
    health, including safety, or the environment, including property, as determined by
    an explosives or munitions emergency response specialist. Such situations may
    require immediate and expeditious action by an explosives or munitions
    emergency response specialist to control, mitigate, or eliminate the threat.
     
    “Explosives or munitions emergency response” means all immediate response
    activities by an explosives and munitions emergency response specialist to
    control, mitigate, or eliminate the actual or potential threat encountered during an
    explosives or munitions emergency. An explosives or munitions emergency
    response may include in-place render-safe procedures, treatment, or destruction of
    the explosives or munitions or transporting those items to another location to be
    rendered safe, treated, or destroyed. Any reasonable delay in the completion of
    an explosives or munitions emergency response caused by a necessary,
    unforeseen, or uncontrollable circumstance will not terminate the explosives or
    munitions emergency. Explosives and munitions emergency responses can occur
    on either public or private lands and are not limited to responses at RCRA
    facilities.
     
    “Explosives or munitions emergency response specialist” means an individual
    trained in chemical or conventional munitions or explosives handling,
    transportation, render-safe procedures, or destruction techniques. Explosives or
    munitions emergency response specialists include United States Department of
    Defense (USDOD) emergency explosive ordnance disposal (EOD), technical
    escort unit (TEU), and USDOD-certified civilian or contractor personnel and
    other federal, State, or local government or civilian personnel who are similarly
    trained in explosives or munitions emergency responses.
     
    “Facility” means the following:
     
    All contiguous land and structures, other appurtenances, and improvements
    on the land used for treating, storing, or disposing of hazardous waste. A
    facility may consist of several treatment, storage, or disposal operational
    units (e.g., one or more landfills, surface impoundments, or combinations of

     
    77
    them).
     
    For the purpose of implementing corrective action under 35 Ill. Adm. Code
    724.201, all contiguous property under the control of the owner or operator
    seeking a permit under Subtitle C of RCRA. This definition also applies to
    facilities implementing corrective action under RCRA section 3008(h).
     
    Notwithstanding the immediately-preceding paragraph of this definition, a
    remediation waste management site is not a facility that is subject to 35 Ill.
    Adm. Code 724.201, but a facility that is subject to corrective action
    requirements if the site is located within such a facility.
     
    “Federal agency” means any department, agency, or other instrumentality of the
    federal government, any independent agency or establishment of the federal
    government, including any government corporation and the Government Printing
    Office.
     
    “Federal, State, and local approvals or permits necessary to begin physical
    construction” means permits and approvals required under federal, State, or local
    hazardous waste control statutes, regulations, or ordinances.
     
    “Final closure” means the closure of all hazardous waste management units at the
    facility in accordance with all applicable closure requirements so that hazardous
    waste management activities under 35 Ill. Adm. Code 724 and 725 are no longer
    conducted at the facility unless subject to the provisions of 35 Ill. Adm. Code
    722.134.
     
    “Food-chain crops” means tobacco, crops grown for human consumption, and crops
    grown for feed for animals whose products are consumed by humans.
     
    “Freeboard” means the vertical distance between the top of a tank or surface
    impoundment dike and the surface of the waste contained therein.
     
    “Free liquids” means liquids that readily separate from the solid portion of a waste
    under ambient temperature and pressure.
     
    “Generator” means any person, by site, whose act or process produces hazardous
    waste identified or listed in 35 Ill. Adm. Code 721 or whose act first causes a
    hazardous waste to become subject to regulation.
     
    “Groundwater” means water below the land surface in a zone of saturation.
     
    “Hazardous waste” means a hazardous waste as defined in 35 Ill. Adm. Code
    721.103.
     
    “Hazardous waste constituent” means a constituent that caused the hazardous waste

     
    78
    to be listed in Subpart D of 35 Ill. Adm. Code 721, or a constituent listed in 35 Ill.
    Adm. Code 721.124.
     
    “Hazardous waste management unit” is a contiguous area of land on or in which
    hazardous waste is placed, or the largest area in which there is significant likelihood
    of mixing hazardous waste constituents in the same area. Examples of hazardous
    waste management units include a surface impoundment, a waste pile, a land
    treatment area, a landfill cell, an incinerator, a tank and its associated piping and
    underlying containment system, and a container storage area. A container alone does
    not constitute a unit; the unit includes containers, and the land or pad upon which
    they are placed.
     
    “Inactive portion” means that portion of a facility that is not operated after November
    19, 1980. (See also “active portion” and “closed portion.”)
     
    “Incinerator” means any enclosed device of which the following is true:
     
    The facility uses controlled flame combustion, and both of the following are
    true of the facility:
     
    The facility does not meet the criteria for classification as a boiler,
    sludge dryer, or carbon regeneration unit, nor
     
    The facility is not listed as an industrial furnace; or
     
    The facility meets the definition of infrared incinerator or plasma arc
    incinerator.
     
    “Incompatible waste” means a hazardous waste that is unsuitable for the following:
     
    Placement in a particular device or facility because it may cause corrosion or
    decay of containment materials (e.g., container inner liners or tank walls); or
     
    Commingling with another waste or material under uncontrolled conditions
    because the commingling might produce heat or pressure, fire, or explosion,
    violent reaction, toxic dusts, mists, fumes or gases, or flammable fumes or
    gases.
     
    (See Appendix E to 35 Ill. Adm. Code 725 for examples.)
     
    “Industrial furnace” means any of the following enclosed devices that are integral
    components of manufacturing processes and that use thermal treatment to
    accomplish recovery of materials or energy:
     
    Cement kilns;
     

     
    79
    Lime kilns;
     
    Aggregate kilns;
     
    Phosphate kilns;
     
    Coke ovens;
     
    Blast furnaces;
     
    Smelting, melting and refining furnaces (including pyrometallurgical devices
    such as cupolas, reverberator furnaces, sintering machines, roasters, and
    foundry furnaces);
     
    Titanium dioxide chloride process oxidation reactors;
     
    Methane reforming furnaces;
     
    Pulping liquor recovery furnaces;
     
    Combustion devices used in the recovery of sulfur values from spent sulfuric
    acid;
     
    Halogen acid furnaces (HAFs) for the production of acid from halogenated
    hazardous waste generated by chemical production facilities where the
    furnace is located on the site of a chemical production facility, the acid
    product has a halogen acid content of at least three percent, the acid product
    is used in a manufacturing process, and, except for hazardous waste burned
    as fuel, hazardous waste fed to the furnace has a minimum halogen content of
    20 percent, as generated; and
     
    Any other such device as the Agency determines to be an industrial furnace
    on the basis of one or more of the following factors:
     
    The design and use of the device primarily to accomplish recovery of
    material products;
     
    The use of the device to burn or reduce raw materials to make a
    material product;
     
    The use of the device to burn or reduce secondary materials as
    effective substitutes for raw materials, in processes using raw
    materials as principal feedstocks;
     
    The use of the device to burn or reduce secondary materials as
    ingredients in an industrial process to make a material product;

     
    80
     
    The use of the device in common industrial practice to produce a
    material product; and
     
    Other relevant factors.
     
    “Individual generation site” means the contiguous site at or on which one or more
    hazardous wastes are generated. An individual generation site, such as a large
    manufacturing plant, may have one or more sources of hazardous waste but is
    considered a single or individual generation site if the site or property is contiguous.
     
    “Infrared incinerator” means any enclosed device that uses electric powered
    resistance heaters as a source of radiant heat followed by an afterburner using
    controlled flame combustion and which is not listed as an industrial furnace.
     
    “Inground tank” means a device meeting the definition of tank whereby a portion of
    the tank wall is situated to any degree within the ground, thereby preventing visual
    inspection of that external surface area of the tank that is in the ground.
     
    “In operation” refers to a facility that is treating, storing, or disposing of hazardous
    waste.
     
    “Injection well” means a well into which fluids are being injected. (See also
    “underground injection.”)
     
    “Inner liner” means a continuous layer of material placed inside a tank or container
    that protects the construction materials of the tank or container from the contained
    waste or reagents used to treat the waste.
     
    “Installation inspector” means a person who, by reason of knowledge of the physical
    sciences and the principles of engineering, acquired by a professional education and
    related practical experience, is qualified to supervise the installation of tank systems.
     
    “International shipment” means the transportation of hazardous waste into or out of
    the jurisdiction of the United States.
     
    “Lamp” or “universal waste lamp” means the bulb or tube portion of an electric
    lighting device. A lamp is specifically designed to produce radiant energy, most
    often in the ultraviolet, visible, or infrared regions of the electromagnetic spectrum.
    Examples of common universal waste lamps include, but are not limited to,
    fluorescent, high intensity discharge, neon, mercury vapor, high-pressure sodium,
    and metal halide lamps.
     
    “Land treatment facility” means a facility or part of a facility at which hazardous
    waste is applied onto or incorporated into the soil surface; such facilities are disposal
    facilities if the waste will remain after closure.

     
    81
     
    “Landfill” means a disposal facility or part of a facility where hazardous waste is
    placed in or on land and which is not a pile, a land treatment facility, a surface
    impoundment, an underground injection well, a salt dome formation, a salt bed
    formation, an underground mine, a cave, or a corrective action management unit
    (CAMU).
     
    “Landfill cell” means a discrete volume of a hazardous waste landfill that uses a liner
    to provide isolation of wastes from adjacent cells or wastes. Examples of landfill
    cells are trenches and pits.
     
    “LDS” means leak detection system.
     
    “Leachate” means any liquid, including any suspended components in the liquid, that
    has percolated through or drained from hazardous waste.
     
    “Liner” means a continuous layer of natural or manmade materials beneath or on the
    sides of a surface impoundment, landfill, or landfill cell that restricts the downward
    or lateral escape of hazardous waste, hazardous waste constituents, or leachate.
     
    “Leak-detection system” means a system capable of detecting the failure of either the
    primary or secondary containment structure or the presence of a release of hazardous
    waste or accumulated liquid in the secondary containment structure. Such a system
    must employ operational controls (e.g., daily visual inspections for releases into the
    secondary containment system of aboveground tanks) or consist of an interstitial
    monitoring device designed to detect continuously and automatically the failure of
    the primary or secondary containment structure or the presence of a release of
    hazardous waste into the secondary containment structure.
     
    “Management” or “hazardous waste management” means the systematic control of
    the collection, source separation, storage, transportation, processing, treatment,
    recovery, and disposal of hazardous waste.
     
    “Manifest” means the shipping document USEPA Form 8700-22 (including, if
    necessary, USEPA Form 8700-22A) originated and signed by the generator or
    offeror that contains the information required by Subpart B of 35 Ill. Adm. Code 722
    and the applicable requirements of 35 Ill. Adm. Code 722 through 725.
     
    “Manifest document number” means, until September 5, 2006, the USEPA twelve
    digit identification number assigned to the generator plus a unique five-digit
    document number assigned to the manifest by the generator for recording and
    reporting purposes.
     
    “Manifest tracking number” means, effective September 5, 2006, the
    alphanumeric identification number (i.e., a unique three letter suffix preceded by
    nine numerical digits) that is pre-printed in Item 4 of the manifest by a registered

     
    82
    source.
     
    “Mercury-containing equipment” means mercury switches and mercury relays,
    and scientific instruments and instructional equipment containing mercury added
    during their manufacture.
    BOARD NOTE: The definition of “mercury-containing equipment” was added
    pursuant to Sections 3.283, 3.284, and 22.23b of the Act [415 ILCS 5/3.283,
    3.284, and 22.23b], (See P.A. 93-964, effective August 20, 2004).
     
    “Mercury relay” means a product or device, containing mercury added during its
    manufacture, that opens or closes electrical contacts to effect the operation of
    other devices in the same or another electrical circuit. Mercury relay includes,
    but is not limited to, mercury displacement relays, mercury wetted reed relays,
    and mercury contact relays.
    [415 ILCS 5/3.283]
    BOARD NOTE: The definition of “mercury relay” was added pursuant to
    Section 3.283 of the Act [415 ILCS 5/.283], (See P.A. 93-964, effective August
    20, 2004).
     
    “Mercury switch” means a product or device, containing mercury added during
    its manufacture, that opens or closes an electrical circuit or gas valve, including,
    but not limited to, mercury float switches actuated by rising or falling liquid
    levels, mercury tilt switches actuated by a change in the switch position, mercury
    pressure switches actuated by a change in pressure, mercury temperature
    switches actuated by a change in temperature, and mercury flame sensors.
    [415
    ILCS 5/3.284]
    BOARD NOTE: The definition of “mercury switch” was added pursuant to
    Section 3.284 of the Act [415 ILCS 5/.284], (See P.A. 93-964, effective August
    20, 2004).
     
    “Military munitions” means all ammunition products and components produced
    or used by or for the United States Department of Defense or the United States
    Armed Services for national defense and security, including military munitions
    under the control of the United States Department of Defense (USDOD), the
    United States Coast Guard, the United States Department of Energy (USDOE),
    and National Guard personnel. The term military munitions includes: confined
    gaseous, liquid, and solid propellants, explosives, pyrotechnics, chemical and riot
    control agents, smokes, and incendiaries used by USDOD components, including
    bulk explosives and chemical warfare agents, chemical munitions, rockets, guided
    and ballistic missiles, bombs, warheads, mortar rounds, artillery ammunition,
    small arms ammunition, grenades, mines, torpedoes, depth charges, cluster
    munitions and dispensers, demolition charges, and devices and components of
    these items and devices. Military munitions do not include wholly inert items,
    improvised explosive devices, and nuclear weapons, nuclear devices, and nuclear
    components of these items and devices. However, the term does include non-
    nuclear components of nuclear devices, managed under USDOE’s nuclear
    weapons program after all sanitization operations required under the Atomic

     
    83
    Energy Act of 1954 (42 USC 2014 et seq.), as amended, have been completed.
     
    “Mining overburden returned to the mine site” means any material overlying an
    economic mineral deposit that is removed to gain access to that deposit and is then
    used for reclamation of a surface mine.
     
    “Miscellaneous unit” means a hazardous waste management unit where hazardous
    waste is treated, stored, or disposed of and that is not a container; tank; surface
    impoundment; pile; land treatment unit; landfill; incinerator; boiler; industrial
    furnace; underground injection well with appropriate technical standards under 35
    Ill. Adm. Code 730; containment building; corrective action management unit
    (CAMU); unit eligible for a research, development, and demonstration permit under
    35 Ill. Adm. Code 703.231; or staging pile.
     
    “Movement” means hazardous waste that is transported to a facility in an individual
    vehicle.
     
    “New hazardous waste management facility” or “new facility” means a facility that
    began operation, or for which construction commenced after November 19, 1980.
    (See also “Existing hazardous waste management facility.”)
     
    “New tank system” or “new tank component” means a tank system or component
    that will be used for the storage or treatment of hazardous waste and for which
    installation commenced after July 14, 1986; except, however, for purposes of 35 Ill.
    Adm. Code 724.293(g)(2) and 725.293(g)(2), a new tank system is one for which
    construction commenced after July 14, 1986. (See also “existing tank system.”)
     
    “Onground tank” means a device meeting the definition of tank that is situated in
    such a way that the bottom of the tank is on the same level as the adjacent
    surrounding surfaces so that the external tank bottom cannot be visually inspected.
     
    “On-site” means the same or geographically contiguous property that may be divided
    by public or private right-of-way, provided the entrance and exit between the
    properties is at a crossroads intersection and access is by crossing as opposed to
    going along the right-of-way. Noncontiguous properties owned by the same person
    but connected by a right-of-way that the owner controls and to which the public does
    not have access is also considered on-site property.
     
    “Open burning” means the combustion of any material without the following
    characteristics:
     
    Control of combustion air to maintain adequate temperature for efficient
    combustion;
     
    Containment of the combustion reaction in an enclosed device to provide
    sufficient residence time and mixing for complete combustion; and

     
    84
     
    Control of emission of the gaseous combustion products.
     
    (See also “incineration” and “thermal treatment.”)
     
    “Operator” means the person responsible for the overall operation of a facility.
     
    “Owner” means the person that owns a facility or part of a facility.
     
    “Partial closure” means the closure of a hazardous waste management unit in
    accordance with the applicable closure requirements of 35 Ill. Adm. Code 724 or 725
    at a facility that contains other active hazardous waste management units. For
    example, partial closure may include the closure of a tank (including its associated
    piping and underlying containment systems), landfill cell, surface impoundment,
    waste pile, or other hazardous waste management unit, while other units of the same
    facility continue to operate.
     
    “Person” means an individual, trust, firm, joint stock company, federal agency,
    corporation (including a government corporation), partnership, association, state,
    municipality, commission, political subdivision of a state, or any interstate body.
     
    “Personnel” or “facility personnel” means all persons who work at or oversee the
    operations of a hazardous waste facility and whose actions or failure to act may
    result in noncompliance with the requirements of 35 Ill. Adm. Code 724 or 725.
     
    “Pesticide” means any substance or mixture of substances intended for preventing,
    destroying, repelling, or mitigating any pest or intended for use as a plant regulator,
    defoliant, or desiccant, other than any article that fulfills one of the following
    descriptions:
     
    It is a new animal drug under section 201(v) of the Federal Food, Drug and
    Cosmetic Act (FFDCA; 21 USC 321(v)), incorporated by reference in
    Section 720.111 720.111(c);
     
    It is an animal drug that has been determined by regulation of the federal
    Secretary of Health and Human Services pursuant to FFDCA section 512 (21
    USC 360b), incorporated by reference in Section 720.111 720.111(c), to be
    an exempted new animal drug; or
     
    It is an animal feed under FFDCA section 201(w) (21 USC 321(w)),
    incorporated by reference in Section 720.111 720.111(c), that bears or
    contains any substances described in either of the two preceding paragraphs
    of this definition.
    BOARD NOTE: The second exception of corresponding 40 CFR 260.10
    reads as follows: “Is an animal drug that has been determined by regulation
    of the Secretary of Health and Human Services not to be a new animal

     
    85
    drug.” This is very similar to the language of section 2(u) of the Federal
    Insecticide, Fungicide, and Rodenticide Act (FIFRA; 7 USC 136(u)). The
    three exceptions, taken together, appear intended not to include as pesticide
    any material within the scope of federal Food and Drug Administration
    regulation. The Board codified this provision with the intent of retaining the
    same meaning as its federal counterpart while adding the definiteness
    required under Illinois law.
     
    “Pile” means any noncontainerized accumulation of solid, non-flowing hazardous
    waste that is used for treatment or storage, and that is not a containment building.
     
    “Plasma arc incinerator” means any enclosed device that uses a high intensity
    electrical discharge or arc as a source of heat followed by an afterburner using
    controlled flame combustion and which is not listed as an industrial furnace.
     
    “Point source” means any discernible, confined, and discrete conveyance, including,
    but not limited to, any pipe, ditch, channel, tunnel, conduit, well, discrete fissure,
    container, rolling stock, concentrated animal feeding operation, or vessel or other
    floating craft from which pollutants are or may be discharged. This term does not
    include return flows from irrigated agriculture.
     
    “Publicly owned treatment works” or “POTW” is as defined in 35 Ill. Adm. Code
    310.110.
     
    “Qualified groundwater scientist” means a scientist or engineer who has received a
    baccalaureate or postgraduate degree in the natural sciences or engineering, and has
    sufficient training and experience in groundwater hydrology and related fields, as
    demonstrated by state registration, professional certifications, or completion of
    accredited university courses that enable the individual to make sound professional
    judgments regarding groundwater monitoring and contaminant rate and transport.
    BOARD NOTE: State registration includes, but is not limited to, registration as a
    professional engineer with the Department of Professional Regulation, pursuant to
    225 ILCS 325 and 68 Ill. Adm. Code 1380. Professional certification includes, but is
    not limited to, certification under the certified groundwater professional program of
    the National Ground Water Association.
     
    “RCRA” means the Solid Waste Disposal Act, as amended by the Resource
    Conservation and Recovery Act of 1976, as amended (42 USC 6901 et seq.).
     
    “Regional Administrator” means the Regional Administrator for the USEPA Region
    in which the facility is located or the Regional Administrator’s designee.
     
    “Remediation waste” means all solid and hazardous wastes, and all media (including
    groundwater, surface water, soils, and sediments) and debris that are managed for
    implementing cleanup.
     

     
    86
    “Remediation waste management site” means a facility where an owner or operator
    is or will be treating, storing, or disposing of hazardous remediation wastes. A
    remediation waste management site is not a facility that is subject to corrective
    action under 35 Ill. Adm. Code 724.201, but a remediation waste management site
    is subject to corrective action requirements if the site is located in such a facility.
     
    “Replacement unit” means a landfill, surface impoundment, or waste pile unit from
    which all or substantially all of the waste is removed, and which is subsequently
    reused to treat, store, or dispose of hazardous waste. Replacement unit does not
    include a unit from which waste is removed during closure, if the subsequent reuse
    solely involves the disposal of waste from that unit and other closing units or
    corrective action areas at the facility, in accordance with a closure or corrective
    action plan approved by USEPA or the Agency.
     
    “Representative sample” means a sample of a universe or whole (e.g., waste pile,
    lagoon, groundwater) that can be expected to exhibit the average properties of the
    universe or whole.
     
    “Runoff” means any rainwater, leachate, or other liquid that drains over land from
    any part of a facility.
     
    “Runon” means any rainwater, leachate, or other liquid that drains over land onto
    any part of a facility.
     
    “Saturated zone” or “zone of saturation” means that part of the earth’s crust in which
    all voids are filled with water.
     
    “SIC Code code” means “Standard Industrial Classification Code code,” as defined
    assigned to a site by the United States Department of Transportation, Federal
    Highway Administration, based on the particular activities that occur on the site,
    as set forth in its publication, “Standard Industrial Classification Manual,”
    incorporated by reference in Section 720.111 720.111(a).
     
    “Sludge” means any solid, semi-solid, or liquid waste generated from a municipal,
    commercial, or industrial wastewater treatment plant, water supply treatment plant,
    or air pollution control facility, exclusive of the treated effluent from a wastewater
    treatment plant.
     
    “Sludge dryer” means any enclosed thermal treatment device that is used to
    dehydrate sludge and which has a total thermal input, excluding the heating value of
    the sludge itself, of 2500 2,500 Btu/lb or less of sludge treated on a wet-weight basis.
     
    “Small quantity generator” means a generator that generates less than 1000 1,000 kg
    of hazardous waste in a calendar month.
     
    “Solid waste” means a solid waste as defined in 35 Ill. Adm. Code 721.102.

     
    87
     
    “Sorbent” means a material that is used to soak up free liquids by either adsorption or
    absorption, or both. “Sorb” means to either adsorb or absorb, or both.
     
    “Staging pile” means an accumulation of solid, non-flowing “remediation waste”
    (as defined in this Section) that is not a containment building and that is used only
    during remedial operations for temporary storage at a facility. Staging piles must be
    designated by the Agency according to the requirements of 35 Ill. Adm. Code
    724.654.
     
    “State” means any of the several states, the District of Columbia, the Commonwealth
    of Puerto Rico, the Virgin Islands, Guam, American Samoa, and the Commonwealth
    of the Northern Mariana Islands.
     
    “Storage” means the holding of hazardous waste for a temporary period, at the end of
    which the hazardous waste is treated, disposed of, or stored elsewhere.
     
    “Sump” means any pit or reservoir that meets the definition of tank and those troughs
    or trenches connected to it that serve to collect hazardous waste for transport to
    hazardous waste storage, treatment, or disposal facilities; except that, as used in the
    landfill, surface impoundment, and waste pile rules, sump means any lined pit or
    reservoir that serves to collect liquids drained from a leachate collection and removal
    system or leak detection system for subsequent removal from the system.
     
    “Surface impoundment” or “impoundment” means a facility or part of a facility that
    is a natural topographic depression, manmade excavation, or diked area formed
    primarily of earthen materials (although it may be lined with manmade materials)
    that is designed to hold an accumulation of liquid wastes or wastes containing free
    liquids and which is not an injection well. Examples of surface impoundments are
    holding, storage, settling and aeration pits, ponds, and lagoons.
     
    “Tank” means a stationary device, designed to contain an accumulation of hazardous
    waste that is constructed primarily of nonearthen materials (e.g., wood, concrete,
    steel, plastic) that provide structural support.
     
    “Tank system” means a hazardous waste storage or treatment tank and its associated
    ancillary equipment and containment system.
     
    “TEQ” means toxicity equivalence, the international method of relating the
    toxicity of various dioxin and furan congeners to the toxicity of 2,3,7,8-tetra-
    chlorodibenzo-p-dioxin.
     
    “Thermal treatment” means the treatment of hazardous waste in a device that uses
    elevated temperatures as the primary means to change the chemical, physical, or
    biological character or composition of the hazardous waste. Examples of thermal
    treatment processes are incineration, molten salt, pyrolysis, calcination, wet air

     
    88
    oxidation, and microwave discharge. (See also “incinerator” and “open burning.”)
     
    “Thermostat” means a temperature control device that contains metallic mercury in
    an ampule attached to a bimetal sensing element and mercury-containing ampules
    that have been removed from such a temperature control device in compliance with
    the requirements of 35 Ill. Adm. Code 733.113(c)(2) or 733.133(c)(2).
     
    “Totally enclosed treatment facility” means a facility for the treatment of hazardous
    waste that is directly connected to an industrial production process and which is
    constructed and operated in a manner that prevents the release of any hazardous
    waste or any constituent thereof into the environment during treatment. An example
    is a pipe in which waste acid is neutralized.
     
    “Transfer facility” means any transportation related facility, including loading docks,
    parking areas, storage areas, and other similar areas where shipments of hazardous
    waste are held during the normal course of transportation.
     
    “Transport vehicle” means a motor vehicle or rail car used for the transportation of
    cargo by any mode. Each cargo-carrying body (trailer, railroad freight car, etc.) is a
    separate transport vehicle.
     
    “Transportation” means the movement of hazardous waste by air, rail, highway, or
    water.
     
    “Transporter” means a person engaged in the off-site transportation of hazardous
    waste by air, rail, highway, or water.
     
    “Treatability study” means the following:
     
    A study in which a hazardous waste is subjected to a treatment process to
    determine the following:
     
    Whether the waste is amenable to the treatment process;
     
    What pretreatment (if any) is required;
     
    The optimal process conditions needed to achieve the desired
    treatment;
     
    The efficiency of a treatment process for a specific waste or wastes;
    and
     
    The characteristics and volumes of residuals from a particular
    treatment process;
     
    Also included in this definition for the purpose of 35 Ill. Adm. Code

     
    89
    721.104(e) and (f) exemptions are liner compatibility, corrosion and other
    material compatibility studies, and toxicological and health effects studies. A
    treatability study is not a means to commercially treat or dispose of
    hazardous waste.
     
    “Treatment” means any method, technique, or process, including neutralization,
    designed to change the physical, chemical, or biological character or composition of
    any hazardous waste so as to neutralize the waste, recover energy or material
    resources from the waste, or render the waste non-hazardous or less hazardous; safer
    to transport, store, or dispose of; or amenable for recovery, amenable for storage, or
    reduced in volume.
     
    “Treatment zone” means a soil area of the unsaturated zone of a land treatment unit
    within which hazardous constituents are degraded, transformed, or immobilized.
     
    “Underground injection” means the subsurface emplacement of fluids through a
    bored, drilled, or driven well or through a dug well, where the depth of the dug well
    is greater than the largest surface dimension. (See also “injection well.”)
     
    “Underground tank” means a device meeting the definition of tank whose entire
    surface area is totally below the surface of and covered by the ground.
     
    “Unfit-for-use tank system” means a tank system that has been determined, through
    an integrity assessment or other inspection, to be no longer capable of storing or
    treating hazardous waste without posing a threat of release of hazardous waste to the
    environment.
     
    “United States” means the 50 states, the District of Columbia, the Commonwealth of
    Puerto Rico, the U.S. Virgin Islands, Guam, American Samoa, and the
    Commonwealth of the Northern Mariana Islands.
     
    “Universal waste” means any of the following hazardous wastes that are managed
    under the universal waste requirements of 35 Ill. Adm. Code 733:
     
    Batteries, as described in 35 Ill. Adm. Code 733.102;
     
    Pesticides, as described in 35 Ill. Adm. Code 733.103;
     
    Thermostats, as described in 35 Ill. Adm. Code 733.104;
     
    Lamps, as described in 35 Ill. Adm. Code 733.105; and
     
    Mercury-containing equipment, as described in 35 Ill. Adm. Code
    733.106.
    BOARD NOTE: Mercury-containing equipment was added pursuant to
    Sections 3.283, 3.284, and 22.23b of the Act [415 ILCS 5/.283, 3.284, and

     
    90
    22.23b] (See P.A. 93-964, effective August 20, 2004).
     
    “Universal waste handler” means either of the following:
     
    A generator (as defined in this Section) of universal waste; or
     
    The owner or operator of a facility, including all contiguous property, that
    receives universal waste from other universal waste handlers, accumulates
    the universal waste, and sends that universal waste to another universal waste
    handler, to a destination facility, or to a foreign destination.
     
    “Universal waste handler” does not mean either of the following:
     
    A person that treats (except under the provisions of Section
    733.113(a) or (c) or 733.133(a) or (c)), disposes of, or recycles
    universal waste; or
     
    A person engaged in the off-site transportation of universal waste by
    air, rail, highway, or water, including a universal waste transfer
    facility.
     
    “Universal waste transporter” means a person engaged in the off-site transportation
    of universal waste by air, rail, highway, or water.
     
    “Unsaturated zone” or “zone of aeration” means the zone between the land surface
    and the water table.
     
    “Uppermost aquifer” means the geologic formation nearest the natural ground
    surface that is an aquifer, as well as lower aquifers that are hydraulically
    interconnected with this aquifer within the facility’s property boundary.
     
    “USDOT” or “Department of Transportation” means the United States Department
    of Transportation.
     
    “Used oil” means any oil that has been refined from crude oil, or any synthetic oil,
    that has been used and as a result of such use is contaminated by physical or
    chemical impurities.
     
    “USEPA” or “EPA” or “U.S. EPA” means the United States Environmental
    Protection Agency.
     
    “Vessel” includes every description of watercraft used or capable of being used as a
    means of transportation on the water.
     
    “Wastewater treatment unit” means a device of which the following is true:
     

     
    91
    It is part of a wastewater treatment facility that has an NPDES permit
    pursuant to 35 Ill. Adm. Code 309 or a pretreatment permit or authorization
    to discharge pursuant to 35 Ill. Adm. Code 310; and
     
    It receives and treats or stores an influent wastewater that is a hazardous
    waste as defined in 35 Ill. Adm. Code 721.103, or generates and accumulates
    a wastewater treatment sludge that is a hazardous waste as defined in 35 Ill.
    Adm. Code 721.103, or treats or stores a wastewater treatment sludge that is
    a hazardous waste as defined in 35 Ill. Adm. Code 721.103; and
     
    It meets the definition of tank or tank system in this Section.
     
    “Water (bulk shipment)” means the bulk transportation of hazardous waste that is
    loaded or carried on board a vessel without containers or labels.
     
    “Well” means any shaft or pit dug or bored into the earth, generally of a cylindrical
    form, and often walled with bricks or tubing to prevent the earth from caving in.
     
    “Well injection” (See “underground injection.”)
     
    “Zone of engineering control” means an area under the control of the owner or
    operator that, upon detection of a hazardous waste release, can be readily cleaned up
    prior to the release of hazardous waste or hazardous constituents to groundwater or
    surface water.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 720.111 References
     
    The following documents are incorporated by reference for the purposes of this Part and 35 Ill.
    Adm. Code 703 through 705, 721 through 726, 728, 730, 733, 738, and 739:
     
    a) Non-Regulatory Government Publications and Publications of Recognized
    Organizations and Associations:
     
    ACI. Available from the American Concrete Institute, Box 19150,
    Redford Station, Detroit, Michigan 48219:
     
    ACI 318-83: “Building Code Requirements for Reinforced
    Concrete,” adopted September 1983, referenced in 35 Ill. Adm.
    Code 724.673 and 725.543.
     
    ANSI. Available from the American National Standards Institute, 1430
    Broadway, New York, New York 10018, 212-354-3300:
     
    ANSI B31.3 and B31.4. See ASME/ANSI B31.3 and B31.4 and

     
    92
    supplements below in this subsection (a) under ASME.
     
    API. Available from the American Petroleum Institute, 1220 L Street,
    N.W., Washington, D.C. 20005, 202-682-8000:
     
    “Cathodic Protection of Underground Petroleum Storage Tanks
    and Piping Systems,” API Recommended Practice 1632, Second
    Edition, December 1987, referenced in 35 Ill. Adm. Code 724.292,
    724.295, 725.292, and 725.295.
     
    “Evaporative Loss from External Floating-Roof Tanks,” API
    Publication publication 2517, Third Edition, February 1989,
    USEPA-approved for 35 Ill. Adm. Code 725.984.
     
    “Guide for Inspection of Refinery Equipment,” Chapter XIII,
    “Atmospheric and Low Pressure Storage Tanks,” 4th Edition,
    1981, reaffirmed December 1987, referenced in 35 Ill. Adm. Code
    724.291, 724.293, 725.291, and 725.292.
     
    “Installation of Underground Petroleum Storage Systems,” API
    Recommended Practice 1615, Fourth Edition, November 1987,
    referenced in 35 Ill. Adm. Code 724.292.
     
    ASME. Available from the American Society of Mechanical Engineers,
    345 East 47th Street, New York, NY 10017, 212-705-7722:
     
    “Chemical Plant and Petroleum Refinery Piping,” ASME/ANSI
    B31.3-1987, as supplemented by B31.3a-1988 and B31.3b-1988,
    referenced in 35 Ill. Adm. Code 724.292 and 725.292. Also
    available from ANSI.
     
    “Liquid Transportation Systems for Hydrocarbons, Liquid
    Petroleum Gas, Anhydrous Ammonia, and Alcohols,”
    ASME/ANSI B31.4-1986, as supplemented by B31.4a-1987,
    referenced in 35 Ill. Adm. Code 724.292 and 725.292. Also
    available from ANSI.
     
    ASTM. Available from American Society for Testing and Materials, 100
    Barr Harbor Drive, West Conshohocken, PA 19428-2959, 610-832-9585:
     
    ASTM C 94-90, “Standard Specification for Ready-Mixed
    Concrete,” approved March 30, 1990, referenced in 35 Ill. Adm.
    Code 724.673 and 725.543.
     
    ASTM D 88-87, “Standard Test Method for Saybolt Viscosity,”
    approved April 24, 1981, reapproved January 1987, referenced in

     
    93
    35 Ill. Adm. Code 726.200.
     
    ASTM D 93-85, “Standard Test Methods for Flash Point by
    Pensky-Martens Closed Tester,” approved October 25, 1985,
    USEPA-approved for 35 Ill. Adm. Code 721.121.
     
    ASTM D 140-70, “Standard Practice for Sampling Bituminous
    Materials,” approved 1970, referenced in Appendix A to 35 Ill.
    Adm. Code 721.
     
    ASTM D 346-75, “Standard Practice for Collection and
    Preparation of Coke Samples for Laboratory Analysis,” approved
    1975, referenced in Appendix A to 35 Ill. Adm. Code 721.
     
    ASTM D 420–69, “Guide to Site Characterization for Engineering,
    Design, and Construction Purposes,” approved 1969, referenced in
    Appendix A to 35 Ill. Adm. Code 721.
     
    ASTM D 1452–65, “Standard Practice for Soil Investigation and
    Sampling by Auger Borings,” approved 1965, referenced in
    Appendix A to 35 Ill. Adm. Code 721.
     
    ASTM D 1946-90, “Standard Practice for Analysis of Reformed
    Gas by Gas Chromatography,” approved March 30, 1990, USEPA-
    approved for 35 Ill. Adm. Code 724.933 and 725.933.
     
    ASTM D 2161-87, “Standard Practice for Conversion of
    Kinematic Viscosity to Saybolt Universal or to Saybolt Furol
    Viscosity,” March 27, 1987, referenced in 35 Ill. Adm. Code
    726.200.
     
    ASTM D 2234-76, “Standard Practice for Collection of a Gross
    Sample of Coal,” approved 1976, referenced in Appendix A to 35
    Ill. Adm. Code 721.
     
    ASTM D 2267-88, “Standard Test Method for Aromatics in Light
    Naphthas and Aviation Gasolines by Gas Chromatography,”
    approved November 17, 1988, USEPA-approved for 35 Ill. Adm.
    Code 724.963.
     
    ASTM D 2382-88, “Standard Test Method for Heat of Combustion
    of Hydrocarbon Fuels by Bomb Calorimeter (High Precision
    Method),” approved October 31, 1988, USEPA-approved for 35
    Ill. Adm. Code 724.933 and 725.933.
     
    ASTM D 2879-92, “Standard Test Method for Vapor Pressure-

     
    94
    Temperature Relationship and Initial Decomposition Temperature
    of Liquids by Isoteniscope,” approved 1992, USEPA-approved for
    35 Ill. Adm. Code 725.984, referenced in 35 Ill. Adm. Code
    724.963 and 725.963.
     
    ASTM D 3828-87, “Standard Test Methods for Flash Point of
    Liquids by Setaflash Closed Tester,” approved December 14,
    1988, USEPA-approved for 35 Ill. Adm. Code 721.121(a).
     
    ASTM E 168-88, “Standard Practices for General Techniques of
    Infrared Quantitative Analysis,” approved May 27, 1988, USEPA-
    approved for 35 Ill. Adm. Code 724.963.
     
    ASTM E 169-87, “Standard Practices for General Techniques of
    Ultraviolet-Visible Quantitative Analysis,” approved February 1,
    1987, USEPA-approved for 35 Ill. Adm. Code 724.963.
     
    ASTM E 260-85, “Standard Practice for Packed Column Gas
    Chromatography,” approved June 28, 1985, USEPA-approved for
    35 Ill. Adm. Code 724.963.
     
    ASTM Method G 21-70 (1984a), “Standard Practice for
    Determining Resistance of Synthetic Polymer Materials to Fungi.”,
    referenced in 35 Ill. Adm. Code 724.414 and 725.414.
     
    ASTM Method G 22-76 (1984b), “Standard Practice for
    Determining Resistance of Plastics to Bacteria.”, referenced in 35
    Ill. Adm. Code 724.414 and 725.414.
     
    MICE. Methods Information Communication Exchange Service, 703-
    821-4690:
     
    “Test Methods for Evaluating Solid Waste, Physical/Chemical
    Methods,” USEPA publication number SW-846, Update IIIA
    (April 1998).
     
    GPO. Available from the Superintendent of Documents, U.S.
    Government Printing Office, Washington, D.C. 20402,202-512-1800:
     
    Standard Industrial Classification Manual (1972), and 1977
    Supplement, republished in 1983, referenced in 35 Ill. Adm. Code
    702.110 and Section 720.110.
     
    “Test Methods for Evaluating Solid Waste, Physical/Chemical
    Methods,” USEPA Publication publication number EPA-530/SW-
    846 (Third Edition, November 1986), as amended by Updates I

     
    95
    (July 1992), II (September 1994), IIA (August, 1993), IIB (January
    1995), and III (December 1996), and IIIA (April 1998), and IIIB
    (November 2004) (document number 955-001-00000-1). See
    below in this subsection (a) under NTIS.
     
    NACE. Available from the National Association of Corrosion Engineers,
    1400 South Creek Dr., Houston, TX 77084, 713-492-0535:
     
    “Control of External Corrosion on Metallic Buried, Partially
    Buried, or Submerged Liquid Storage Systems,” NACE
    Recommended Practice RP-02-85 RP0285-85, approved March
    1985, referenced in 35 Ill. Adm. Code 724.292, 724.295, 725.292,
    and 725.295.
     
    NFPA. Available from the National Fire Protection Association, 1
    Batterymarch Park, Boston, MA 02269, 617-770-3000 or 800-344-3555:
     
    “Flammable and Combustible Liquids Code,” NFPA 30, issued
    July 17, 1987, USEPA-approved for 35 Ill. Adm. Code 724.298
    and 725.298, referenced in 35 Ill. Adm. Code 724.298 and
    726.211. Also available from ANSI.
     
    NTIS. Available from the U.S. Department of Commerce, National
    Technical Information Service, 5285 Port Royal Road, Springfield, VA
    22161, 703-605-6000 or 800-553-6847 (Internet address: www.ntis.gov):
     
    “APTI Course 415: Control of Gaseous Emissions,” December
    1981, USEPA publication number 450/2-81-005, NTIS document
    number PB80-208895, December 1981 USEPA-approved for 35
    Ill. Adm. Code 703.210, 703.211, 724.935, and 725.935.
    BOARD NOTE: “APTI” denotes USEPA’s “Air Pollution
    Training Institute” (Internet address:
    www.epa.gov/air/oaqps/eog/).
     
    “Generic Quality Assurance Project Plan for Land Disposal
    Restrictions Program,” EPA/530-SW-87-011 USEPA publication
    number EPA-530/SW-87-011, March 15, 1987, (NTIS document
    number PB88-170766), referenced in 35 Ill. Adm. Code 728.106.
     
    “Guideline on Air Quality Models,” Revised 1986 (document
    number PB86-245-248 (Guideline) and PB88-150-958
    (Supplement), also set forth at 40 CFR 51, Appendix W).
     
    “Method 164, 1664, Revision A, n-Hexane Extractable Material
    (HEM; Oil and Grease) and Silica Gel Treated n-Hexane
    Extractable Material (SGT-HEM; Non-polar Material) by

     
    96
    Extraction and Gravimetry,” (USEPA publication number EPA-
    821/R-98-002, NTIS document number PB99-121949), USEPA-
    approved for Appendix I to 35 Ill. Adm. Code 721.
    BOARD NOTE: EPA-821/R-98-002 is also available on the
    Internet for free download as a PDF document from the USEPA
    website at: www.epa.gov/waterscience/methods/16640514.pdf.
     
    “Methods for Chemical Analysis of Water and Wastes,” Third
    Edition, March 1983, USEPA document number EPA-600/4-79-
    020 (NTIS document number PB84-128677), referenced in 35 Ill.
    Adm. Code 725.192.
    BOARD NOTE: EPA-600/4-79-002 is also available on the
    Internet as a viewable/printable HTML document from the USEPA
    website at: www.epa.gov/clariton/clhtml/pubtitleORD.html as
    document 600479002.
     
    “Methods Manual for Compliance with BIF Regulations,”
    December 1990 (document number PB91-120-006).
     
    “Procedures Manual for Ground Water Monitoring at Solid Waste
    Disposal Facilities,” August, 1977, EPA-530/SW-611, NTIS
    document number PB84-174820, referenced in 35 Ill. Adm. Code
    725.192.
     
    “Screening Procedures for Estimating the Air Quality Impact of
    Stationary Sources,” October 1992, USEPA publication number
    EPA-450/R-92-019 EPA-454/R-92-019, NTIS document number
    93-219095, referenced in 35 Ill. Adm. Code 726.204 and 726.206.
    BOARD NOTE: EPA-454/R-92-019 is also available on the
    Internet for free download as a WordPerfect document from the
    USEPA website at following Internet address:
    www.epa.gov/scram001/guidance/guide/scrng.wpd.
     
    “Test Methods for Evaluating Solid Waste, Physical/Chemical
    Methods,” USEPA Publication publication number EPA-530/SW-
    846 (Third Edition, November 1986; Revision 6, January 2005), as
    amended by Updates I (July 1992), II (September 1994), IIA
    (August 1993), IIB (January 1995), III (December 1996), and IIIA
    (April 1998), and IIIB (November 2004) (document number 955-
    001-00000-1)., generally referenced in Appendices A and I to 35
    Ill. Adm. Code 721 and 35 Ill. Adm. Code 726.200, 726.206,
    726.212, and 728.106 (in addition to the references cited below for
    specific methods):
     
    Method 0010 (September 1986) (Modified Method 5
    Sampling Train), USEPA-approved for Appendix I to 35

     
    97
    Ill. Adm. Code 721.
     
    Method 0011 (December 1996) (Sampling for Selected
    Aldehyde and Ketone Emissions from Stationary Sources),
    USEPA-approved for Appendix I to 35 Ill. Adm. Code 721
    and for Appendix I to 35 Ill. Adm. Code 726.
     
    Method 0020 (September 1986) (Source Assessment
    Sampling System), USEPA-approved for Appendix I to 35
    Ill. Adm. Code 721.
     
    Method 0023A (December 1996) (Sampling Method for
    Polychlorinated Dibenzo-p-Dioxins and Polychlorinated
    Dibenzofuran Emissions from Stationary Sources),
    USEPA-approved for Appendix I to 35 Ill. Adm. Code 721,
    Appendix I to 35 Ill. Adm. Code 726, and 35 Ill. Adm.
    Code 726.204.
     
    Method 0030 (September 1986) (Volatile Organic
    Sampling Train), USEPA-approved for Appendix I to 35
    Ill. Adm. Code 721.
     
    Method 0031 (December 1996) (Sampling Method for
    Volatile Organic Compounds (SMVOC)), USEPA-
    approved for Appendix I to 35 Ill. Adm. Code 721.
     
    Method 0040 (December 1996) (Sampling of Principal
    Organic Hazardous Constituents from Combustion Sources
    Using Tedlar
    ®
    Bags), USEPA-approved for Appendix I to
    35 Ill. Adm. Code 721.
     
    Method 0050 (December 1996) (Isokinetic HCl/Cl2
    Emission Sampling Train), USEPA-approved for Appendix
    I to 35 Ill. Adm. Code 721, Appendix I to 35 Ill. Adm.
    Code 726, and 35 Ill. Adm. Code 726.207.
     
    Method 0051 (December 1996) (Midget Impinger HCl/Cl2
    Emission Sampling Train), USEPA-approved for Appendix
    I to 35 Ill. Adm. Code 721, Appendix I to 35 Ill. Adm.
    Code 726, and 35 Ill. Adm. Code 726.207.
     
    Method 0060 (December 1996) (Determination of Metals
    in Stack Emissions), USEPA-approved for Appendix I to
    35 Ill. Adm. Code 721, Appendix I to 35 Ill. Adm. Code
    726, and 35 Ill. Adm. Code 726.206.
     

     
    98
    Method 0061 (December 1996) (Determination of
    Hexavalent Chromium Emissions from Stationary
    Sources), USEPA-approved for Appendix I to 35 Ill. Adm.
    Code 721, 35 Ill. Adm. Code 726.206, and Appendix I to
    35 Ill. Adm. Code 726.
     
    Method 1010A (November 2004) (Test Methods for Flash
    Point by Pensky-Martens Closed Cup Tester), USEPA-
    approved for Appendix I to 35 Ill. Adm. Code 721.
     
    Method 1020B (November 2004) (Standard Test Methods
    for Flash Point by Setaflash (Small Scale) Closed-cup
    Apparatus), USEPA-approved for Appendix I to 35 Ill.
    Adm. Code 721.
     
    Method 1110A (November 2004) (Corrosivity Toward
    Steel), USEPA-approved for 35 Ill. Adm. Code 721.122
    and Appendix I to 35 Ill. Adm. Code 721.
     
    Method 1310B (November 2004) (Extraction Procedure
    (EP) Toxicity Test Method and Structural Integrity Test),
    USEPA-approved for Appendix I to 35 Ill. Adm. Code 721
    and referenced in Appendix I to 35 Ill. Adm. Code 728.
     
    Method 1311 (September 1992) (Toxicity Characteristic
    Leaching Procedure), USEPA-approved for Appendix I to
    35 Ill. Adm. Code 721; for 35 Ill. Adm. Code 721.124,
    728.107, and 728.140; and for Table T to 35 Ill. Adm. Code
    728.
     
    Method 1312 (September 1994) (Synthetic Precipitation
    Leaching Procedure), USEPA-approved for Appendix I to
    35 Ill. Adm. Code 721.
     
    Method 1320 (September 1986) (Multiple Extraction
    Procedure), USEPA-approved for Appendix I to 35 Ill.
    Adm. Code 721.
     
    Method 1330A (September 1992) (Extraction Procedure
    for Oily Wastes), USEPA-approved for Appendix I to 35
    Ill. Adm. Code 721.
     
    Method 9010C (November 2004) (Total and Amenable
    Cyanide: Distillation), USEPA-approved for Appendix I to
    35 Ill. Adm. Code 721 and 35 Ill. Adm. Code 728.140,
    728.144, and 728.148, referenced in Table H to 35 Ill.

     
    99
    Adm. Code 728.
     
    Method 9012B (November 2004) (Total and Amenable
    Cyanide (Automated Colorimetric, with Off-Line
    Distillation)), USEPA-approved for Appendix I to 35 Ill.
    Adm. Code 721 and 35 Ill. Adm. Code 728.140, 728.144,
    and 728.148, referenced in Table H to 35 Ill. Adm. Code
    728.
     
    Method 9040C (November 2004) (pH Electrometric
    Measurement), USEPA-approved for 35 Ill. Adm. Code
    721.122 and Appendix I to 35 Ill. Adm. Code 721.
     
    Method 9045D (November 2004) (Soil and Waste pH),
    USEPA-approved for Appendix I to 35 Ill. Adm. Code 721.
     
    Method 9060A (November 2004) (Total Organic Carbon),
    USEPA-approved for Appendix I to 35 Ill. Adm. Code 721
    and 35 Ill. Adm. Code 724.934, 724.963, 725.934, and
    725.963.
     
    Method 9070A (November 2004) (n-Hexane Extractable
    Material (HEM) for Aqueous Samples), USEPA-approved
    for Appendix I to 35 Ill. Adm. Code 721.
     
    Method 9071B (April 1998) (n-Hexane Extractable
    Material (HEM) for Sludge, Sediment, and Solid Samples),
    USEPA-approved for Appendix I to 35 Ill. Adm. Code 721.
     
    Method 9095B (November 2004) (Paint Filter Liquids
    Test), USEPA-approved for Appendix I to 35 Ill. Adm.
    Code 721 and 35 Ill. Adm. Code 724.290, 724.414,
    725.290, 725.414, 725.981, and 728.132.
     
    BOARD NOTE: EPA-530/SW-846 is also available on the
    Internet for free download in segments in PDF format from the
    USEPA website at: www.epa.gov/SW-846.
     
    OECD. Organisation for Economic Co-operation and Development,
    Environment Directorate, 2 rue Andre Pascal, 75775 Paris Cedex 16,
    France, also OECD Washington Center, 2001 L Street, NW, Suite 650,
    Washington, DC 20036-4922, 202-785-6323 or 800-456-6323
    (www.oecdwash.org):
     
    OECD “Amber List of Wastes,” Appendix 4 to the OECD Council
    Decision C(92)39/FINAL C(92)39(Final) (March 30, 1992,

     
    100
    revised May 1993) (Concerning the Control of Transfrontier
    Movements of Wastes Destined for Recovery Operations),
    “Decision of the Council Concerning the Control of Transfrontier
    Movements of Wastes Destined for Recovery
    Operations.”USEPA-approved for 35 Ill. Adm. Code 722.189,
    referenced in 35 Ill. Adm. Code 722.181.
     
    OECD “Amber Tier,” Section IV of the annex to the OECD
    Council Decision C(92)39(Final) (Concerning the Control of
    Transfrontier Movements of Wastes Destined for Recovery
    Operations) (revised May 1993), referenced in 35 Ill. Adm. Code
    722.181.
     
    Annex to OECD Council Decision C(88)90(Final), as amended by
    C(94)152/FINAL (revised July 1994), referenced in 35 Ill. Adm.
    Code 722.187.
     
    OECD “Green List of Wastes,” Appendix 3 to the OECD Council
    Decision C(92)39/FINAL C(92)39(Final) (March 30, 1992,
    revised May 1994) (Concerning the Control of Transfrontier
    Movements of Wastes Destined for Recovery Operations)),
    “Decision of the Council Concerning the Control of Transfrontier
    Movements of Wastes Destined for Recovery
    Operations.”USEPA-approved for 35 Ill. Adm. Code 722.189,
    referenced in 35 Ill. Adm. Code 722.181.
     
    OECD “Green Tier,” Section III of the annex to the OECD
    Council Decision C(92)39(Final) (Concerning the Control of
    Transfrontier Movements of Wastes Destined for Recovery
    Operations) (revised May 1993), referenced in 35 Ill. Adm. Code
    722.181.
     
    OECD Guideline for Testing of Chemicals, “Ready
    Biodegradability,” Method 301B (17 July 1992), “CO2 Evolution
    (Modified Sturm Test),”, referenced in 35 Ill. Adm. Code 724.414.
     
    OECD “Red List of Wastes,” Appendix 5 to the OECD Council
    Decision C(92)39/FINAL C(92)39(Final) (March 30, 1992,
    revised revised May 1993), “Decision of the Council Concerning
    the Control of Transfrontier Movements of Wastes Destined for
    Recovery Operations.”USEPA-approved for 35 Ill. Adm. Code
    722.189, referenced in 35 Ill. Adm. Code 722.181.
     
    OECD “Red Tier,” Section V of the annex to the OECD Council
    Decision C(92)39(Final) (Concerning the Control of Transfrontier
    Movements of Wastes Destined for Recovery Operations) (revised

     
    101
    May 1993), referenced in 35 Ill. Adm. Code 722.181.
     
    Table 2.B of the Annex of OECD Council Decision
    C(88)90(Final) (27 May 1988), amended by C(94)152(Final) (July
    28, 1994), “Decision of the Council on Transfrontier Movements
    of Hazardous Wastes”, referenced in 35 Ill. Adm. Code 722.181
    and 722.187.
     
    STI. Available from the Steel Tank Institute, 728 Anthony Trail,
    Northbrook, IL 60062, 708-498-1980:
     
    “Standard for Dual Wall Underground Steel Storage Tanks”
    (1986), referenced in 35 Ill. Adm. Code 724.293.
     
    USDOD. Available from the United States Department of Defense:
     
    “DOD Ammunition and Explosives Safety Standards” (DOD
    6055.9-STD), as in effect in July 1999, referenced in 35 Ill. Adm.
    Code 726.305.
     
    “The Motor Vehicle Inspection Report” (DD Form 626), as in
    effect on November 8, 1995, referenced in 35 Ill. Adm. Code
    726.303.
     
    “Requisition Tracking Form” (DD Form 1348), as in effect on
    November 8, 1995, referenced in 35 Ill. Adm. Code 726.303.
     
    “The Signature and Tally Record” (DD Form 1907), as in effect on
    November 8, 1995, referenced in 35 Ill. Adm. Code 726.303.
     
    “Special Instructions for Motor Vehicle Drivers” (DD Form 836),
    as in effect on November 8, 1995, referenced in 35 Ill. Adm. Code
    726.303.
     
    USEPA, Office of Drinking Water. Available from United States
    Environmental Protection Agency, Office of Drinking Water, State
    Programs Division, WH 550 E, Washington, D.C. 20460:
     
    “Technical Assistance Document: Corrosion, Its Detection and
    Control in Injection Wells,” EPA 570/9-87-002 USEPA
    publication number EPA-570/9-87-002, August 1987, referenced
    in 35 Ill. Adm. Code 730.165.
     
    USEPA, Receptor Analysis Branch. Available from Receptor Analysis
    Branch, USEPA (MD-14), Research Triangle Park, NC 27711:
     

     
    102
    “Samplers and Sampling Procedures for Hazardous Waste
    Streams,” EPA 600/2–80–018, January 1980.
     
    “Screening Procedures for Estimating the Air Quality Impact of
    Stationary Sources, Revised,” October 1992, USEPA publication
    number EPA-450/R-92-019 EPA-450/R-92-019, USEPA-approved
    for Appendix I to 35 Ill. Adm. Code 726.
     
    USEPA Region 6. Available from United States Environmental
    Protection Agency, Region 6, Multimedia Permitting and Planning
    Division, 1445 Ross Avenue, Dallas, TX 75202 (phone: 214-665-7430):
     
    “EPA RCRA Delisting Program--Guidance Manual for the
    Petitioner,” March 23, 2000, referenced in Section 720.122.
     
    USGSA. Available from the United States Government Services
    Administration:
     
    Government Bill of Lading (GBL) (GSA Standard Form 1109), as
    in effect on November 8, 1995, referenced in Section 726.303.
     
    b) Code of Federal Regulations. Available from the Superintendent of Documents,
    U.S. Government Printing Office, Washington, D.C. 20401, 202-783-3238:
     
    10 CFR 20.2006 (2004) (2005) (Transfer for Disposal and Manifests),
    referenced in 35 Ill. Adm. Code 702.110, 726.425, and 726.450.
     
    Table II, column 2 in Appendix B to 10 CFR 20, Appendix B (2004)
    (2005) (Water Effluent Concentrations), referenced in 35 Ill. Adm. Code
    702.110, 730.103, and 730.151.
     
    Appendix G to 10 CFR 20 (2005) (Requirements for Transfers of Low-
    Level Radioactive Waste Intended for Disposal at Licensed Land Disposal
    Facilities and Manifests), referenced in 35 Ill. Adm. Code 726.440.
     
    10 CFR 71 (2004) (2005) (Packaging and Transportation of Radioactive
    Material), referenced generally in 35 Ill. Adm. Code 726.430.
     
    10 CFR 71.5 (2005) (Transportation of Licensed Material), referenced in
    35 Ill. Adm. Code 726.425.
     
    33 CFR 153.203 (2005) (Procedure for the Notice of Discharge),
    referenced in 35 Ill. Adm. Code 723.130 and 739.143.
     
    40 CFR 51.100(ii) (2004) (2005) (Definitions), referenced in 35 Ill. Adm.
    Code 726.200.

     
    103
     
    Appendix W to 40 CFR 51, Appendix W (2004) (2005) (Guideline on Air
    Quality Models), referenced in 35 Ill. Adm. Code 726.204.
    BOARD NOTE: Also available from the NTIS (see above for contact
    information) as “Guideline on Air Quality Models,” Revised 1986,
    USEPA publication number EPA-450/12-78-027R, NTIS document
    numbers PB86-245248 (Guideline) and PB88-150958 (Supplement).
     
    Appendix B to 40 CFR 52.741, Appendix B (2004) (2005) (VOM
    Measurement Techniques for Capture Efficiency), referenced in 35 Ill.
    Adm. Code 703.213, 724.982, 724.984, 724.986, 724.989, 725.983,
    725.985, 725.987, and 725.990.
     
    40 CFR 60 (2004) (2005) (Standards of Performance for New Stationary
    Sources), referenced generally in 35 Ill. Adm. Code 724.964, 724.980,
    725.964, and 725.980.
     
    Subpart VV of 40 CFR 60 (2005) (Standards of Performance for
    Equipment Leaks of VOC in the Synthetic Organic Chemicals
    Manufacturing Industry), referenced in 35 Ill. Adm. Code 724.989 and
    725.990.
     
    Appendix A to 40 CFR 60 (2005) (Test Methods), referenced generally in
    35 Ill. Adm. Code 726.205 (in addition to the references cited below for
    specific methods):
     
    Method 1 (Sample and Velocity Traverses for Stationary Sources),
    referenced in 35 Ill. Adm. Code 726.205.
     
    Method 2 (Determination of Stack Gas Velocity and Volumetric
    Flow Rate (Type S Pitot Tube)), referenced in 35 Ill. Adm. Code
    724.933, 724.934, 725.933, 725.934, and 726.205.
     
    Method 2A (Direct Measurement of Gas Volume through Pipes
    and Small Ducts), referenced in 35 Ill. Adm. Code 724.933,
    725.933, and 726.205.
     
    Method 2B (Determination of Exhaust Gas Volume Flow Rate
    from Gasoline Vapor Incinerators), referenced in 35 Ill. Adm.
    Code 726.205.
     
    Method 2C (Determination of Gas Velocity and Volumetric Flow
    Rate in Small Stacks or Ducts (Standard Pitot Tube)), referenced in
    35 Ill. Adm. Code 724.933, 725.933, and 726.205.
     
    Method 2D (Measurement of Gas Volume Flow Rates in Small

     
    104
    Pipes and Ducts), referenced in 35 Ill. Adm. Code 724.933,
    725.933, and 726.205.
     
    Method 2E (Determination of Landfill Gas Production Flow Rate),
    referenced in 35 Ill. Adm. Code 726.205.
     
    Method 2F (Determination of Stack Gas Velocity and Volumetric
    Flow Rate with Three-Dimensional Probes), referenced in 35 Ill.
    Adm. Code 726.205.
     
    Method 2G (Determination of Stack Gas Velocity and Volumetric
    Flow Rate with Two-Dimensional Probes), referenced in 35 Ill.
    Adm. Code 726.205.
     
    Method 2H (Determination of Stack Gas Velocity Taking into
    Account Velocity Decay Near the Stack Wall), referenced in 35 Ill.
    Adm. Code 726.205.
     
    Method 3 (Gas Analysis for the Determination of Dry Molecular
    Weight), referenced in 35 Ill. Adm. Code 724.443 and 726.205.
     
    Method 3A (Determination of Oxygen and Carbon Dioxide
    Concentrations in Emissions from Stationary Sources
    (Instrumental Analyzer Procedure)), referenced in 35 Ill. Adm.
    Code 726.205.
     
    Method 3B (Gas Analysis for the Determination of Emission Rate
    Correction Factor or Excess Air), referenced in 35 Ill. Adm. Code
    726.205.
     
    Method 3C (Determination of Carbon Dioxide, Methane, Nitrogen,
    and Oxygen from Stationary Sources), referenced in 35 Ill. Adm.
    Code 726.205.
     
    Method 4 (Determination of Moisture Content in Stack Gases),
    referenced in 35 Ill. Adm. Code 726.205.
     
    Method 5 (Determination of Particulate Matter Emissions from
    Stationary Sources), referenced in 35 Ill. Adm. Code 726.205.
     
    Method 5A (Determination of Particulate Matter Emissions from
    the Asphalt Processing and Asphalt Roofing Industry), referenced
    in 35 Ill. Adm. Code 726.205.
     
    Method 5B (Determination of Nonsulfuric Acid Particulate Matter
    Emissions from Stationary Sources), referenced in 35 Ill. Adm.

     
    105
    Code 726.205.
     
    Method 5D (Determination of Particulate Matter Emissions from
    Positive Pressure Fabric Filters), referenced in 35 Ill. Adm. Code
    726.205.
     
    Method 5E (Determination of Particulate Matter Emissions from
    the Wool Fiberglass Insulation Manufacturing Industry),
    referenced in 35 Ill. Adm. Code 726.205.
     
    Method 5F (Determination of Nonsulfate Particulate Matter
    Emissions from Stationary Sources), referenced in 35 Ill. Adm.
    Code 726.205.
     
    Method 5G (Determination of Particulate Matter Emissions from
    Wood Heaters (Dilution Tunnel Sampling Location)), referenced
    in 35 Ill. Adm. Code 726.205.
     
    Method 5H (Determination of Particulate Emissions from Wood
    Heaters from a Stack Location), referenced in 35 Ill. Adm. Code
    726.205.
     
    Method 5I (Determination of Low Level Particulate Matter
    Emissions from Stationary Sources), referenced in 35 Ill. Adm.
    Code 726.205.
     
    Method 18 (Measurement of Gaseous Organic Compound
    Emissions by Gas Chromatography), referenced in 35 Ill. Adm.
    Code 724.933, 724.934, 725.933, and 725.934.
     
    Method 21 (Determination of Volatile Organic Compound Leaks),
    referenced in 35 Ill. Adm. Code 703.213, 724.934, 724.935,
    724.963, 725.934, 725.935, 725.963, and 725.984.
     
    Method 22 (Visual Determination of Fugitive Emissions from
    Material Sources and Smoke Emissions from Flares), referenced in
    35 Ill. Adm. Code 724.933, 724.1101, 725.933, and 725.1101.
     
    Method 25A (Determination of Total Gaseous Organic
    Concentration Using a Flame Ionization Analyzer), referenced in
    35 Ill. Adm. Code 724.934 and 725.985.
     
    Method 25D (Determination of the Volatile Organic Concentration
    of Waste Samples), referenced in 35 Ill. Adm. Code 724.982,
    725.983, and 725.984.
     

     
    106
    Method 25E (Determination of Vapor Phase Organic
    Concentration in Waste Samples), referenced in 35 Ill. Adm. Code
    725.984.
     
    Method 27 (Determination of Vapor Tightness of Gasoline
    Delivery Tank Using Pressure-Vacuum Test), referenced in 35 Ill.
    Adm. Code 724.987 and 725.987.
     
    40 CFR 61 (2005) (National Emission Standards for Hazardous Air
    Pollutants), referenced generally in 35 Ill. Adm. Code 725.933, 725.964,
    and 725.980.
     
    Subpart V of 40 CFR 61, Subpart V (2004) (2005) (National Emission
    Standard for Equipment Leaks (Fugitive Emission Sources)), referenced in
    35 Ill. Adm. Code 724.989 and 725.990.
     
    Subpart FF of 40 CFR 61 (2005) (National Emission Standard for
    Benzene Waste Operations), referenced in 35 Ill. Adm. Code 724.982 and
    725.983.
     
    40 CFR 63 (2005) (National Emission Standards for Hazardous Air
    Pollutants for Source Categories), referenced generally in 35 Ill. Adm.
    Code 725.933, 725.964, and 725.980.
     
    Subpart RR of 40 CFR 63 (2005) (National Emission Standards for
    Individual Drain Systems), referenced in 35 Ill. Adm. Code 724.982,
    724.984, 724.985, 725.983, 725.985, and 725.986.
     
    Subpart EEE of 40 CFR 63 (2004) (2005) (National Emission Standards
    for Hazardous Air Pollutants from Hazardous Waste Combustors)
    (includes 40 CFR 63.1206 (When and How Must You Comply with the
    Standards and Operating Requirements?)), referenced in Appendix A to
    35 Ill. Adm. Code 703 and 35 Ill. Adm. Code 703.155, 703.205, 703.208,
    703.221, 703.232, 703.320, 724.440, 724.701, 724.950 725.440, and
    726.200.
     
    Method 301 (Field Validation of Pollutant Measurement Methods from
    Various Waste Media) in appendix A to 40 CFR 63 (2005) (Test
    Methods), referenced in 35 Ill. Adm. Code 725.984.
     
    Appendix C to 40 CFR 63 (2005) (Determination of the Fraction
    Biodegraded (Fbio) in a Biological Treatment Unit), referenced in 35 Ill.
    Adm. Code 725.984.
     
    Appendix D to 40 CFR 63 (2005) (Test Methods), referenced in 35 Ill.
    Adm. Code 725.984.

     
    107
     
    40 CFR 136 (2004) 136.3 (Identification of Test Procedures) (2005),
    referenced in 35 Ill. Adm. Code 702.110, 704.150, 704.187, and 730.103.
     
    40 CFR 142 (2004)
     
    40 CFR 144.70 (2005) (Wording of the Instruments), referenced in 35 Ill.
    Adm. Code 704.240.
     
    40 CFR 220 (2004)
     
    40 CFR 232.2 (2004) (2005) (Definitions), referenced in 35 Ill. Adm.
    Code 721.104.
     
    40 CFR 257 (2005) (Criteria for Classification of Solid Waste Disposal
    Facilities and Practices), referenced in Section 739.181.
     
    40 CFR 258 (2005) (Criteria for Municipal Solid Waste Landfills),
    referenced in Section 739.181.
     
    40 CFR 260.20 (2004)
     
    40 CFR 260.21 (2005) (Alternative Equivalent Testing Methods),
    referenced in Section 720.121.
     
    Appendix I to 40 CFR 260 (2005) (Overview of Subtitle C Regulations),
    referenced in Appendix A to 35 Ill. Adm. Code 720.
     
    Appendix III to 40 CFR 261 (2005) (Chemical Analysis Test Methods),
    referenced in 35 Ill. Adm. Code 704.150 and 704.187.
     
    40 CFR 262.53 through 262.57 and Appendix (2004) (2005) (Notification
    of Intent to Export), referenced in 35 Ill. Adm. Code 722.153.
     
    40 CFR 262.54 (2005) (Special Manifest Requirements), and as amended
    at 70 Fed. Reg. 10776 (March 4, 2005), referenced in 35 Ill. Adm. Code
    722.154.
     
    40 CFR 262.55 (2005) (Exception Reports), referenced in 35 Ill. Adm.
    Code 722.155.
     
    40 CFR 262.56 (2005) (Annual Reports), referenced in 35 Ill. Adm. Code
    722.156.
     
    40 CFR 262.57 (2005) (Recordkeeping), referenced in 35 Ill. Adm. Code
    722.157.

     
    108
     
    Appendix to 40 CFR 262 (2005) (Uniform Hazardous Waste Manifest and
    Instructions (EPA Forms 8700–22 and 8700–22a and Their Instructions)),
    and as amended at 70 Fed. Reg. 10776 (March 4, 2005), referenced in
    Appendix A to 35 Ill. Adm. Code 722 and 35 Ill. Adm. Code 724.986 and
    725.987.
     
    40 CFR 264 (2004) 264.151 (2005) (Wording of the Instruments),
    referenced in 35 Ill. Adm. Code 724.251.
     
    Appendix I to 40 CFR 264 (2005) (Recordkeeping Instructions),
    referenced in Appendix A to 35 Ill. Adm. Code 724.
     
    Appendix IV to 40 CFR 264 (2005) (Cochran’s Approximation to the
    Behrens-Fisher Students’ T-Test), referenced in Appendix D to 35 Ill.
    Adm. Code 724.
     
    Appendix V to 40 CFR 264 (2005) (Examples of Potentially Incompatible
    Waste), referenced in Appendix E to 35 Ill. Adm. Code 724.
     
    Appendix VI to 40 CFR 264 (2005) (Political Jurisdictions in Which
    Compliance with§ 264.18(a) Must Be Demonstrated), referenced in 35 Ill.
    Adm. Code 703.306 and 724.118.
     
    Appendix I to 40 CFR 265, Appendices I and III through V (2004) (2005)
    (Recordkeeping Instructions), referenced in Appendix A to 35 Ill. Adm.
    Code 725.
     
    Appendix III to 40 CFR 265 (2005) (EPA Interim Primary Drinking Water
    Standards), referenced in Appendix C to 35 Ill. Adm. Code 725.
     
    Appendix IV to 40 CFR 265 (2005) (Tests for Significance), referenced in
    Appendix D to 35 Ill. Adm. Code 725.
     
    Appendix V to 40 CFR 265 (2005) (Examples of Potentially Incompatible
    Waste), referenced in 35 Ill. Adm. Code 725.277, 725.330, 725.357,
    725.382, and 725.413 and Appendix E to 35 Ill. Adm. Code 725.
     
    Appendix IX to 40 CFR 266 (2005) (Methods Manual for Compliance
    with the BIF Regulations), referenced generally in Appendix I to 35 Ill.
    Adm. Code 726.
     
    Section 4.0 (Procedures for Estimating the Toxicity Equivalence of
    Chlorinated Dibenzo-p-Dioxin and Dibenzofuran Congeners),
    referenced in 35 Ill. Adm. Code 726.200 and 726.204.
     

     
    109
    Section 5.0 (Hazardous Waste Combustion Air Qualtiy Screening
    Procedure), referenced in 35 Ill. Adm. Code 726.204.
     
    Section 7.0 (Statistical Methodology for Bevill Residue
    Determinations), referenced in 35 Ill. Adm. Code 726.212.
     
    BOARD NOTE: Also available from the NTIS (see above for contact
    information) as “Methods Manual for Compliance with BIF Regulations:
    Burning Hazardous Waste in Boilers and Industrial Furnaces,” December
    1990, USEPA publication number EPA-530/SW-91-010, NTIS document
    number PB91-120006.
     
    40 CFR 268, Appendix IX (2004)
     
    40 CFR 270.5 (2004) (2005) (Noncompliance and Program Reporting by
    the Director), referenced in 35 Ill. Adm. Code 703.305.
     
    40 CFR 302 (2004)
     
    40 CFR 423, appendix A (2004)
     
    40 CFR 761 (2004) (2005) (Polychlorinated Biphenyls (PCBs)
    Manufacturing, Processing, Distribution in Commerce, and Use
    Prohibitions), referenced generally in 35 Ill. Adm. Code 728.145.
     
    40 CFR 761.3 (2005) (Definitions), referenced in 35 Ill. Adm. Code
    728.102 and 739.110.
     
    40 CFR 761.60 (2005) (Disposal Requirements), referenced in 35 Ill.
    Adm. Code 728.142.
     
    40 CFR 761.65 (2005) (Storage for Disposal), referenced in 35 Ill. Adm.
    Code 728.150.
     
    40 CFR 761.70 (2005) (Incineration), referenced in 35 Ill. Adm. Code
    728.142.
     
    Subpart B of 49 CFR 107 (2003) (2004) (Exemptions), referenced
    generally in 35 Ill. Adm. Code 724.986 and 725.987.
     
    49 CFR 171 (2003) (2004) (General Information, Regulations, and
    Definitions), referenced generally in 35 Ill. Adm. Code 733.118, 733.138,
    733.152, and 739.143.
     
    49 CFR 171.3 (2004) (Hazardous Waste), referenced in 35 Ill. Adm. Code
    722.133.

     
    110
     
    49 CFR 171.8 (2004) (Definitions and Abbreviations), referenced in 35 Ill.
    Adm. Code 733.118, 733.138, 733.152, 733.155, and 733.155.
     
    49 CFR 171.15 (2004) (Immediate Notice of Certain Hazardous Materials
    Incidents), referenced in 35 Ill. Adm. Code 723.130 and 739.143.
     
    49 CFR 171.16 (2004) (Detailed Hazardous Materials Incident Reports),
    referenced in 35 Ill. Adm. Code 723.130 and 739.143.
     
    49 CFR 172 (2003) (2004) (Hazardous Materials Table, Special
    Provisions, Hazardous Materials Communications, Emergency Response
    Information, and Training Requirements), referenced generally in 35 Ill.
    Adm. Code 722.131, 722.132, 724.986, 725.987, 733.114, 733.118,
    733.134, 733.138, 733.152, 733.155, and 739.143.
     
    49 CFR 172.304 (2004) (Hazardous Materials Table, Special Provisions,
    Hazardous Materials Communications, Emergency Response Information,
    and Training Requirements), referenced in 35 Ill. Adm. Code 722.132.
     
    Subpart F of 49 CFR 172 (2004) (Placarding), referenced in 35 Ill. Adm.
    Code 722.133.
     
    49 CFR 173 (2003) (2004) (Shippers--General Requirements for
    Shipments and Packages), referenced generally in 35 Ill. Adm. Code
    722.130, 724.986, 724.416, 725.987, 733.118, 733.138, 733.152, and
    739.143.
     
    49 CFR 173.2 (2004) (Hazardous Materials Classes and Index to Hazard
    Class Definitions), referenced in 35 Ill. Adm. Code 733.152.
     
    49 CFR 173.12 (2004) (Exceptions for Shipments of Waste Materials),
    referenced in 35 Ill. Adm. Code 724.416, 724.986, and 725.987.
     
    49 CFR 173.28 (2004) (Reuse, Reconditioning, and Remanufacture of
    Packagings), referenced in 35 Ill. Adm. Code 725.273.
     
    49 CFR 173.50 (2004) (Class 1--Definitions), referenced in 35 Ill. Adm.
    Code 721.124.
     
    49 CFR 173.54 (2004) (Forbidden Explosives), referenced in 35 Ill. Adm.
    Code 721.124.
     
    49 CFR 173.115 (2004) (Class 2, Divisions 2.1, 2.2, and 2.3--Definitions),
    referenced in 35 Ill. Adm. Code 721.121.
     

     
    111
    49 CFR 173.127 (2004) (Class 5, Divisions 5.1--Definition and
    Assignment of Packaging Groups), referenced in 35 Ill. Adm. Code
    721.121.
     
    49 CFR 174 (2004) (Carriage by Rail), referenced generally in 35 Ill.
    Adm. Code 733.118, 733.138, 733.152, and 739.143.
     
    49 CFR 175 (2004) (Carriage by Aircraft), referenced generally in 35 Ill.
    Adm. Code 733.118, 733.138, 733.152, and 739.143.
     
    49 CFR 176 (2004) (Carriage by Vessel), referenced generally in 35 Ill.
    Adm. Code 733.118, 733.138, 733.152, and 739.143.
     
    49 CFR 177 (2004) (Carriage by Public Highway), referenced generally in
    35 Ill. Adm. Code 733.118, 733.138, 733.152, and 739.143.
     
    49 CFR 178 (2003) (2004) (Specifications for Packagings), referenced
    generally in 35 Ill. Adm. Code 722.130, 724.416, 724.986, 725.416,
    725.987, 733.118, 733.138, 733.152, and 739.143.
     
    49 CFR 179 (2003) (2004) (Specifications for Tank Cars), referenced in
    35 Ill. Adm. Code 722.130, 724.416, 724.986, 725.416, 725.987, 733.118,
    733.138, 733.152, and 739.143.
     
    49 CFR 180 (2004) (Continuing Qualification and Maintenance of
    Packagings), referenced generally in 35 Ill. Adm. Code 724.986, 725.987,
    733.118, 733.138, 733.152, and 739.143.
     
    c) Federal Statutes
     
    Section 11 of the Atomic Energy Act of 1954 (42 USC 2014), as amended
    through January 23, 2000, referenced in 35 Ill. Adm. Code 721.104 and
    726.310.
     
    Sections 201(v), 201(w), and 360b(j) 512(j) of the Federal Food, Drug,
    and Cosmetic Act (FFDCA; 21 USC 321(v), 321(w), and 512(j) 360b(j)),
    as amended through January 2, 2001, referenced in Section 720.110 and
    35 Ill. Adm. Code 733.109.
     
    Section 1412 of the Department of Defense Authorization Act of 1986,
    Pub. L. 99-145, (50 USC 1521(j)(1)), as amended through January 23,
    2000, referenced in 35 Ill. Adm. Code 726.301.
     
    d) This Section incorporates no later editions or amendments.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)

     
    112
     
    SUBPART C: RULEMAKING PETITIONS AND OTHER PROCEDURES
     
    Section 720.121 Alternative Equivalent Testing Methods
     
    a) The Agency has no authority to alter the universe of regulated wastes.
    Modification of testing methods that are stated in 35 Ill. Adm. Code 721 requires
    rulemaking pursuant to Section 720.120. However, deviation from these methods
    is allowed under 35 Ill. Adm. Code 721, as observed, for example, in the Board
    Note appended to 35 Ill. Adm. Code 721.120(c).
     
    b) The Agency may approve alternative equivalent testing methods for a particular
    person’s use to determine whether specified waste streams are subject to these
    regulations. This must be done by permit condition or letter. Any petition to the
    Board or request to the Agency concerning alternative equivalent testing methods
    must include the information required by 40 CFR 260.21(b), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    c) The testing methods specified in 35 Ill. Adm. Code 721 or alternative equivalent
    testing methods approved by the Agency need not be applied to identify or
    distinguish waste streams that are known, admitted, or assumed to be subject to
    these regulations. In this case, any method may be used, subject to the Agency’s
    authority to approve the testing procedures used.
     
    d) Any petition to the Board or request to the Agency concerning alternative
    equivalent testing methods must include the information required by 40 CFR
    260.21(b). If USEPA amends the federal regulations to allow the use of a new
    testing method, USEPA has stated that it will incorporate the new method by
    reference in 40 CFR 260.11 and add it to “Test Methods for Evaluating Solid
    Waste, Physical/Chemical Methods,” USEPA publication number EPA-530/SW-
    846, incorporated by reference in Section 720.111(b).
     
    e) Alternative equivalent testing methods will not be approved if the result of the
    approval would make the Illinois RCRA Subtitle C program less than
    substantially equivalent to the federal.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 720.122 Waste Delisting
     
    a) Any person seeking to exclude a waste from a particular generating facility from
    the lists in Subpart D of 35 Ill. Adm. Code 721 may file a petition, as specified in
    subsection (n) of this Section. The Board will grant the petition if the following
    occur:
     
    1) The petitioner demonstrates that the waste produced by a particular

     
    113
    generating facility does not meet any of the criteria under which the waste
    was listed as a hazardous or acute hazardous waste; and
     
    2) If the Board determines that there is a reasonable basis to believe that
    factors (including additional constituents) other than those for which the
    waste was listed could cause the waste to be a hazardous waste, that such
    factors do not warrant retaining the waste as a hazardous waste. A Board
    determination under the preceding sentence must be made by reliance on,
    and in a manner consistent with, “EPA RCRA Delisting Program--
    Guidance Manual for the Petitioner,” incorporated by reference in Section
    720.111(a). A waste that is so excluded, however, still may be a
    hazardous waste by operation of Subpart C of 35 Ill. Adm. Code 721.
     
    b) Listed wastes and mixtures. A person may also petition the Board to exclude
    from 35 Ill. Adm. Code 721.103(a)(2)(B) or (a)(2)(C), a waste that is described in
    these Sections and is either a waste listed in Subpart D of 35 Ill. Adm. Code 721,
    or is derived from a waste listed in that Subpart. This exclusion may only be
    granted for a particular generating, storage, treatment, or disposal facility. The
    petitioner must make the same demonstration as required by subsection (a) of this
    Section. Where the waste is a mixture of a solid waste and one or more listed
    hazardous wastes or is derived from one or more listed hazardous wastes, the
    demonstration must be made with respect to the waste mixture as a whole;
    analyses must be conducted for not only those constituents for which the listed
    waste contained in the mixture was listed as hazardous, but also for factors
    (including additional constituents) that could cause the waste mixture to be a
    hazardous waste. A waste that is so excluded may still be a hazardous waste by
    operation of Subpart C of 35 Ill. Adm. Code 721.
     
    c) Ignitable, corrosive, reactive and toxicity characteristic wastes. If the waste is
    listed in codes “I,” “C,” “R,” or “E” in Subpart D of 35 Ill. Adm. Code 721, the
    following requirements apply:
     
    1) The petitioner must demonstrate that the waste does not exhibit the
    relevant characteristic for which the waste was listed, as defined in 35 Ill.
    Adm. Code 721.121, 721.122, 721.123, or 721.124, using any applicable
    methods prescribed in those Sections. The petitioner must also show that
    the waste does not exhibit any of the other characteristics, defined in those
    Sections, using any applicable methods prescribed in those Sections; and
     
    2) Based on a complete petition, the Board will determine, if it has a
    reasonable basis to believe that factors (including additional constituents)
    other than those for which the waste was listed could cause the waste to be
    hazardous waste, that such factors do not warrant retaining the waste as a
    hazardous waste. A Board determination under the preceding sentence
    must be made by reliance on, and in a manner consistent with, “EPA
    RCRA Delisting Program--Guidance Manual for the Petitioner,”

     
    114
    incorporated by reference in Section 720.111(a). A waste that is so
    excluded, however, may still be a hazardous waste by operation of Subpart
    C of 35 Ill. Adm. Code 721.
     
    d) Toxic waste. If the waste is listed in code “T” in Subpart D of 35 Ill. Adm. Code
    721, the following requirements apply:
     
    1) The petitioner must demonstrate that the waste fulfills the following
    criteria:
     
    A) It does not contain the constituent or constituents (as defined in
    Appendix G of 35 Ill. Adm. Code 721) that caused USEPA to list
    the waste, using the appropriate test methods prescribed in “Test
    Methods for Evaluating Solid Waste, Physical/Chemical
    Methods,” USEPA Publication SW-846, as incorporated by
    reference in Section 720.111(a); or
     
    B) Although containing one or more of the hazardous constituents (as
    defined in Appendix G of 35 Ill. Adm. Code 721) that caused
    USEPA to list the waste, the waste does not meet the criterion of
    35 Ill. Adm. Code 721.111(a)(3) when considering the factors used
    in 35 Ill. Adm. Code 721.111(a)(3)(A) through (a)(3)(K) under
    which the waste was listed as hazardous.
     
    2) Based on a complete petition, the Board will determine, if it has a
    reasonable basis to believe that factors (including additional constituents)
    other than those for which the waste was listed could cause the waste to be
    hazardous waste, that such factors do not warrant retaining the waste as a
    hazardous waste.
     
    3) The petitioner must demonstrate that the waste does not exhibit any of the
    characteristics, defined in 35 Ill. Adm. Code 721.121, 721.122, 721.123,
    or 721.124, using any applicable methods prescribed in those Sections.
     
    4) A waste that is so excluded, however, may still be a hazardous waste by
    operation of Subpart C of 35 Ill. Adm. Code 721.
     
    e) Acute hazardous waste. If the waste is listed with the code “H” in Subpart D of
    35 Ill. Adm. Code 721, the following requirements apply:
     
    1) The petitioner must demonstrate that the waste does not meet the criterion
    of 35 Ill. Adm. Code 721.111(a)(2); and
     
    2) Based on a complete petition, the Board will determine, if it has a
    reasonable basis to believe that factors (including additional constituents)
    other than those for which the waste was listed could cause the waste to be

     
    115
    hazardous waste, that such factors do not warrant retaining the waste as a
    hazardous waste. A Board determination under the preceding sentence
    must be made by reliance on, and in a manner consistent with, “EPA
    RCRA Delisting Program--Guidance Manual for the Petitioner,”
    incorporated by reference in Section 720.111(a).
     
    3) The petitioner must demonstrate that the waste does not exhibit any of the
    characteristics, defined in 35 Ill. Adm. Code 721.121, 721.122, 721.123,
    or 721.124, using any applicable methods prescribed in those Sections.
     
    4) A waste that is so excluded, however, may still be a hazardous waste by
    operation of Subpart C of 35 Ill. Adm. Code 721.
     
    f) This subsection corresponds with 40 CFR 260.22(f), which USEPA has marked
    “reserved.” This statement maintains structural consistency with the federal
    regulations.
     
    g) This subsection corresponds with 40 CFR 260.22(g), which USEPA has marked
    “reserved.” This statement maintains structural consistency with the federal
    regulations.
     
    h) Demonstration samples must consist of enough representative samples, but in no
    case less than four samples, taken over a period of time sufficient to represent the
    variability or the uniformity of the waste.
     
    i) Each petition must include, in addition to the information required by subsection
    (n) of this Section:
     
    1) The name and address of the laboratory facility performing the sampling
    or tests of the waste;
     
    2) The names and qualifications of the persons sampling and testing the
    waste;
     
    3) The dates of sampling and testing;
     
    4) The location of the generating facility;
     
    5) A description of the manufacturing processes or other operations and feed
    materials producing the waste and an assessment of whether such
    processes, operations, or feed materials can or might produce a waste that
    is not covered by the demonstration;
     
    6) A description of the waste and an estimate of the average and maximum
    monthly and annual quantities of waste covered by the demonstration;
     

     
    116
    7) Pertinent data on and discussion of the factors delineated in the respective
    criterion for listing a hazardous waste, where the demonstration is based
    on the factors in 35 Ill. Adm. Code 721.111(a)(3);
     
    8) A description of the methodologies and equipment used to obtain the
    representative samples;
     
    9) A description of the sample handling and preparation techniques,
    including techniques used for extraction, containerization, and
    preservation of the samples;
     
    10) A description of the tests performed (including results);
     
    11) The names and model numbers of the instruments used in performing the
    tests; and
     
    12) The following statement signed by the generator or the generator’s
    authorized representative:
     
    I certify under penalty of law that I have personally examined and
    am familiar with the information submitted in this demonstration
    and all attached documents, and that, based on my inquiry of those
    individuals immediately responsible for obtaining the information,
    I believe that the submitted information is true, accurate and
    complete. I am aware that there are significant penalties for
    submitting false information, including the possibility of fine and
    imprisonment.
     
    j) After receiving a petition, the Board may request any additional information that
    the Board needs to evaluate the petition.
     
    k) An exclusion will only apply to the waste generated at the individual facility
    covered by the demonstration and will not apply to waste from any other facility.
     
    l) The Board will exclude only part of the waste for which the demonstration is
    submitted if the Board determines that variability of the waste justifies a partial
    exclusion.
     
    BOARD NOTE: See “EPA RCRA Delisting Program--Guidance Manual for the
    Petitioner,” incorporated by reference in Section 720.111(a).
     
    m) Delisting of specific wastes from specific sources that have been adopted by
    USEPA may be proposed as State regulations that are identical in substance
    pursuant to Section 720.120(a).
     
    n) Delistings that have not been adopted by USEPA may be proposed to the Board

     
    117
    pursuant to a petition for adjusted standard pursuant to Section 28.1 of the Act
    [415 ILCS 5/28.1] and Subpart D of 35 Ill. Adm. Code 104. The justification for
    the adjusted standard is as specified in subsections (a) through (g) of this Section,
    as applicable to the waste in question. The petition must be clearly labeled as a
    RCRA delisting adjusted standard petition.
     
    1) In accordance with 35 Ill. Adm. Code 101.304, the petitioner must serve
    copies of the petition, and any other documents filed with the Board, on
    USEPA at the following addresses:
     
    USEPA
    Office of Solid Waste and Emergency Response
    1200 Pennsylvania Avenue, NW
    Washington, D.C. 20460
     
    USEPA, Region 5
    77 West Jackson Boulevard
    Chicago, IL 60604
     
    2) The Board will mail copies of all opinions and orders to USEPA at the
    above addresses.
     
    3) In conjunction with the normal updating of the RCRA regulations, the
    Board will maintain, in Appendix I of 35 Ill. Adm. Code 721, a listing of
    all adjusted standards granted by the Board.
     
    o) The Agency may determine in a permit or a letter directed to a generator that,
    based on 35 Ill. Adm. Code 721, a waste from a particular source is not subject to
    these regulations. Such a finding is evidence against the Agency in any
    subsequent proceedings but will not be conclusive with reference to other persons
    or the Board.
     
    p) Any petition to delist directed to the Board or request for determination directed
    to the Agency must include a showing that the waste will be generated or
    managed in Illinois.
     
    q) The Board will not grant any petition that would render the Illinois RCRA
    program less stringent than if the decision were made by USEPA.
     
    r) Delistings apply only within Illinois. Generators must comply with 35 Ill. Adm.
    Code 722 for waste that is hazardous in any state to which it is to be transported.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    118
    Section 720.Appendix A Overview of 40 CFR, Federal RCRA Subtitle C (Hazardous
    Waste) Regulations
     
    See Appendix I to 40 CFR 260 (Overview of Subtitle C Regulations), incorporated by reference
    in Section 720.111(c).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
     
    PART 721
    IDENTIFICATION AND LISTING OF HAZARDOUS WASTE
     
    SUBPART A: GENERAL PROVISIONS
    Section
    721.101 Purpose and Scope
    721.102 Definition of Solid Waste
    721.103 Definition of Hazardous Waste
    721.104 Exclusions
    721.105 Special Requirements for Hazardous Waste Generated by Small Quantity
    Generators
    721.106 Requirements for Recyclable Materials
    721.107 Residues of Hazardous Waste in Empty Containers
    721.108 PCB Wastes Regulated under TSCA
    721.109 Requirements for Universal Waste
     
    SUBPART B: CRITERIA FOR IDENTIFYING THE CHARACTERISTICS OF
    HAZARDOUS WASTE AND FOR LISTING HAZARDOUS WASTES
    Section
    721.110 Criteria for Identifying the Characteristics of Hazardous Waste
    721.111 Criteria for Listing Hazardous Waste
     
    SUBPART C: CHARACTERISTICS OF HAZARDOUS WASTE
    Section
    721.120 General
    721.121 Characteristic of Ignitability
    721.122 Characteristic of Corrosivity
    721.123 Characteristic of Reactivity
    721.124 Toxicity Characteristic
     
    SUBPART D: LISTS OF HAZARDOUS WASTE
    Section
    721.130 General

     
    119
    721.131 Hazardous Wastes from Nonspecific Sources
    721.132 Hazardous Waste from Specific Sources
    721.133 Discarded Commercial Chemical Products, Off-Specification Species, Container
    Residues, and Spill Residues Thereof
    721.135 Wood Preserving Wastes
    721.138 Comparable or Syngas Fuel Exclusion
     
    721.Appendix A Representative Sampling Methods
    721.Appendix B Method 1311 Toxicity Characteristic Leaching Procedure (TCLP)
    721.Appendix C Chemical Analysis Test Methods
    Table A Analytical Characteristics of Organic Chemicals (Repealed)
    Table B Analytical Characteristics of Inorganic Species (Repealed)
    Table C Sample Preparation/Sample Introduction Techniques (Repealed)
    721.Appendix G Basis for Listing Hazardous Wastes
    721.Appendix H Hazardous Constituents
    721.Appendix I Wastes Excluded by Administrative Action
    Table A Wastes Excluded by USEPA under pursuant to 40 CFR 260.20 and 260.22
    from Non-Specific Sources
    Table B Wastes Excluded by USEPA under pursuant to 40 CFR 260.20 and 260.22
    from Specific Sources
    Table C Wastes Excluded by USEPA under pursuant to 40 CFR 260.20 and 260.22
    from Commercial Chemical Products, Off-Specification Species,
    Container Residues, and Soil Residues Thereof
    Table D Wastes Excluded by the Board by Adjusted Standard
    721.Appendix J Method of Analysis for Chlorinated Dibenzo-p-Dioxins and
    Dibenzofurans (Repealed)
    721.Appendix Y Table to Section 721.138
    721.Appendix Z Table to Section 721.102
     
    AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the
    Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].
     
    SOURCE: Adopted in R81-22 at 5 Ill. Reg. 9781, effective May 17, 1982; amended and
    codified in R81-22 at 6 Ill. Reg. 4828, effective May 17, 1982; amended in R82-18 at 7 Ill. Reg.
    2518, effective February 22, 1983; amended in R82-19 at 7 Ill. Reg. 13999, effective October 12,
    1983; amended in R84-34, 61 at 8 Ill. Reg. 24562, effective December 11, 1984; amended in
    R84-9 at 9 Ill. Reg. 11834, effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 998,
    effective January 2, 1986; amended in R85-2 at 10 Ill. Reg. 8112, effective May 2, 1986;
    amended in R86-1 at 10 Ill. Reg. 14002, effective August 12, 1986; amended in R86-19 at 10 Ill.
    Reg. 20647, effective December 2, 1986; amended in R86-28 at 11 Ill. Reg. 6035, effective
    March 24, 1987; amended in R86-46 at 11 Ill. Reg. 13466, effective August 4, 1987; amended in
    R87-32 at 11 Ill. Reg. 16698, effective September 30, 1987; amended in R87-5 at 11 Ill. Reg.
    19303, effective November 12, 1987; amended in R87-26 at 12 Ill. Reg. 2456, effective January
    15, 1988; amended in R87-30 at 12 Ill. Reg. 12070, effective July 12, 1988; amended in R87-39
    at 12 Ill. Reg. 13006, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 382, effective
    December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18300, effective November 13, 1989;

     
    120
    amended in R90-2 at 14 Ill. Reg. 14401, effective August 22, 1990; amended in R90-10 at 14 Ill.
    Reg. 16472, effective September 25, 1990; amended in R90-17 at 15 Ill. Reg. 7950, effective
    May 9, 1991; amended in R90-11 at 15 Ill. Reg. 9332, effective June 17, 1991; amended in R91-
    1 at 15 Ill. Reg. 14473, effective September 30, 1991; amended in R91-12 at 16 Ill. Reg. 2155,
    effective January 27, 1992; amended in R91-26 at 16 Ill. Reg. 2600, effective February 3, 1992;
    amended in R91-13 at 16 Ill. Reg. 9519, effective June 9, 1992; amended in R92-1 at 16 Ill. Reg.
    17666, effective November 6, 1992; amended in R92-10 at 17 Ill. Reg. 5650, effective March 26,
    1993; amended in R93-4 at 17 Ill. Reg. 20568, effective November 22, 1993; amended in R93-
    16 at 18 Ill. Reg. 6741, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12175,
    effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17490, effective November 23, 1994;
    amended in R95-6 at 19 Ill. Reg. 9522, effective June 27, 1995; amended in R95-20 at 20 Ill.
    Reg. 10963, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 275,
    effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7615, effective April 15, 1998;
    amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17531, effective September 28, 1998; amended
    in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1718, effective January 19, 1999; amended in R99-15 at
    23 Ill. Reg. 9135, effective July 26, 1999; amended in R00-13 at 24 Ill. Reg. 9481, effective June
    20, 2000; amended in R01-3 at 25 Ill. Reg. 1281, effective January 11, 2001; amended in R01-
    21/R01-23 at 25 Ill. Reg. 9108, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26
    Ill. Reg. 6584, effective April 22, 2002; amended in R03-18 at 27 Ill. Reg. 12760, effective July
    17, 2003; amended in R04-16 at 28 Ill. Reg. 10693, effective July 19, 2004; amended in R05-8 at
    29 Ill. Reg. 6003, effective April 13, 2005; amended in R06-5/R06-6/R06-7 at 30 Ill. Reg.
    ________, effective ______________________.
     
    SUBPART A: GENERAL PROVISIONS
     
    Section 721.103 Definition of Hazardous Waste
     
    a) A solid waste, as defined in Section 721.102, is a hazardous waste if the following
    is true of the waste:
     
    1) It is not excluded from regulation as a hazardous waste under Section
    721.104(b); and
     
    2) It meets any of the following criteria:
     
    A) It exhibits any of the characteristics of hazardous waste identified
    in Subpart C of this Part. However, any mixture of a waste from
    the extraction, beneficiation, and processing of ores and minerals
    excluded under Section 721.104(b)(7) and any other solid waste
    exhibiting a characteristic of hazardous waste under Subpart C of
    this Part is a hazardous waste only if it exhibits a characteristic that
    would not have been exhibited by the excluded waste alone if such
    mixture had not occurred, or if the mixture continues to exhibit any
    of the characteristics exhibited by the non-excluded wastes prior to
    mixture. Further, for the purposes of applying the toxicity
    characteristic to such mixtures, the mixture is also a hazardous

     
    121
    waste if it exceeds the maximum concentration for any
    contaminant listed in Section 721.124 that would not have been
    exceeded by the excluded waste alone if the mixture had not
    occurred or if it continues to exceed the maximum concentration
    for any contaminant exceeded by the nonexempt waste prior to
    mixture.
     
    B) It is listed in Subpart D of this Part and has not been excluded from
    the lists in Subpart D of this Part under 35 Ill. Adm. Code 720.120
    and 720.122.
     
    C) This subsection (a)(2)(B) corresponds with 40 CFR
    261.3(a)(2)(iii), which USEPA removed and marked as “reserved”
    at 66 Fed. Reg. 27266 (May 16, 2001). This statement maintains
    structural consistency with the federal regulations.
     
    D) It is a mixture of solid waste and one or more hazardous wastes
    listed in Subpart D of this Part and has not been excluded from this
    subsection (a)(2) under 35 Ill. Adm. Code 720.120 and 720.122,
    subsection (g) of this Section, or subsection (h) of this Section;
    however, the following mixtures of solid wastes and hazardous
    wastes listed in Subpart D of this Part are not hazardous wastes
    (except by application of subsection (a)(2)(A) or (a)(2)(B) of this
    Section) if the generator demonstrates that the mixture consists of
    wastewater the discharge of which is subject to regulation under
    either 35 Ill. Adm. Code 309 or 310 (including wastewater at
    facilities that have eliminated the discharge of wastewater) and the
    following is true of the waste:
     
    i) It is one or more of the following solvents listed in Section
    721.131: carbon tetrachloride, tetrachloroethylene,
    trichloroethylene, provided that the maximum total weekly
    usage of these solvents (other than the amounts that can be
    demonstrated not to be discharged to wastewater) divided
    by the average weekly flow of wastewater into the
    headworks of the facility’s wastewater treatment or
    pretreatment system does not exceed 1 part per million;
     
    ii) It is one or more of the following spent solvents listed in
    Section 721.131: methylene chloride, 1,1,1-trichloro-
    ethane, chlorobenzene, o-dichlorobenzene, cresols, cresylic
    acid, nitrobenzene, toluene, methyl ethyl ketone, carbon
    disulfide, isobutanol, pyridine, spent chlorofluorocarbon
    solvents, provided that the maximum total weekly usage of
    these solvents (other than the amounts that can be
    demonstrated not to be discharged to wastewater) divided

     
    122
    by the average weekly flow of wastewater into the
    headworks of the facility’s wastewater treatment or
    pretreatment system does not exceed 25 parts per million;
     
    iii) It is one of the following wastes listed in Section 721.132,
    provided that the wastes are discharged to the refinery oil
    recovery sewer before primary oil/water/solids separation:
    heat exchanger bundle cleaning sludge from the petroleum
    refining industry (USEPA hazardous waste no. K050),
    crude oil storage tank sediment from petroleum refining
    operations (USEPA hazardous waste number K169),
    clarified slurry oil tank sediment or in-line filter/separation
    solids from petroleum refining operations (USEPA
    hazardous waste number K170), spent hydrotreating
    catalyst (USEPA hazardous waste number K171), and
    spent hydrorefining catalyst (USEPA hazardous waste
    number K172);
     
    iv) It is a discarded commercial chemical product or chemical
    intermediate listed in Section 721.133 arising from de
    minimis losses of these materials from manufacturing
    operations in which these materials are used as raw
    materials or are produced in the manufacturing process.
    For purposes of this subsection, “de minimis” losses
    include those from normal material handling operations
    (e.g., spills from the unloading or transfer of materials from
    bins or other containers, leaks from pipes, valves, or other
    devices used to transfer materials); minor leaks of process
    equipment, storage tanks, or containers; leaks from well-
    maintained pump packings and seals; sample purgings;
    relief device discharges; discharges from safety showers
    and rinsing and cleaning of personal safety equipment; and
    rinsate from empty containers or from containers that are
    rendered empty by that rinsing;
     
    v) It is wastewater resulting from laboratory operations
    containing toxic (T) wastes listed in Subpart D of this Part,
    provided that the annualized average flow of laboratory
    wastewater does not exceed one percent of total wastewater
    flow into the headworks of the facility’s wastewater
    treatment or pretreatment system or provided that the
    wastes’ combined annualized average concentration does
    not exceed one part per million in the headworks of the
    facility’s wastewater treatment or pretreatment facility.
    Toxic (T) wastes used in laboratories that are demonstrated
    not to be discharged to wastewater are not to be included in

     
    123
    this calculation;
     
    vi) It is one or more of the following wastes listed in Section
    721.132: wastewaters from the production of carbamates
    and carbamoyl oximes (USEPA Hazardous Waste No.
    K157), provided that the maximum weekly usage of
    formaldehyde, methyl chloride, methylene chloride, and
    triethylamine (including all amounts that cannot be
    demonstrated to be reacted in the process, destroyed
    through treatment, or recovered, i.e., what is discharged or
    volatilized) divided by the average weekly flow of process
    wastewater prior to any dilutions into the headworks of the
    facility’s wastewater treatment system does not exceed a
    total of 5 parts per million by weight; or
     
    vii) It is wastewater derived from the treatment of one or more
    of the following wastes listed in Section 721.132: organic
    waste (including heavy ends, still bottoms, light ends, spent
    solvents, filtrates, and decantates) from the production of
    carbamates and carbamoyl oximes (USEPA Hazardous
    Waste No. K156), provided that the maximum
    concentration of formaldehyde, methyl chloride, methylene
    chloride, and triethylamine prior to any dilutions into the
    headworks of the facility’s wastewater treatment system
    does not exceed a total of 5 milligrams per liter.
     
    E) Rebuttable presumption for used oil. Used oil containing more
    than 1,000 ppm total halogens is presumed to be a hazardous waste
    because it has been mixed with halogenated hazardous waste listed
    in Subpart D of this Part. Persons may rebut this presumption by
    demonstrating that the used oil does not contain hazardous waste
    (for example, by using an analytical method from number SW-846,
    incorporated by reference at 35 Ill. Adm. Code 720.111, to show
    that the used oil does not contain significant concentrations of
    halogenated hazardous constituents listed in Appendix H of this
    Part).
     
    i) The rebuttable presumption does not apply to a
    metalworking oil or fluid containing chlorinated paraffins if
    it is processed through a tolling arrangement, as described
    in 35 Ill. Adm. Code 739.124(c), to reclaim metalworking
    oils or fluids. The presumption does apply to a
    metalworking oil or fluid if such an oil or fluid is recycled
    in any other manner, or disposed.
     
    ii) The rebuttable presumption does not apply to a used oil

     
    124
    contaminated with chlorofluorocarbons (CFCs) removed
    from refrigeration units where the CFCs are destined for
    reclamation. The rebuttable presumption does apply to a
    used oil contaminated with CFCs that have been mixed
    with used oil from a source other than a refrigeration unit.
     
    b) A solid waste that is not excluded from regulation under subsection (a)(1) of this
    Section becomes a hazardous waste when any of the following events occur:
     
    1) In the case of a waste listed in Subpart D of this Part, when the waste first
    meets the listing description set forth in Subpart D of this Part.
     
    2) In the case of a mixture of solid waste and one or more listed hazardous
    wastes, when a hazardous waste listed in Subpart D of this Part is first
    added to the solid waste.
     
    3) In the case of any other waste (including a waste mixture), when the waste
    exhibits any of the characteristics identified in Subpart C of this Part.
     
    c) Unless and until it meets the criteria of subsection (d) of this Section, a hazardous
    waste will remain a hazardous waste.
     
    BOARD NOTE: This subsection (c) corresponds with 40 CFR 261.3(c)(1). The
    Board has codified 40 CFR 261.3(c)(2) at subsection (e) of this Section.
     
    d) Any solid waste described in subsection (e) of this Section is not a hazardous
    waste if it meets the following criteria:
     
    1) In the case of any solid waste, it does not exhibit any of the characteristics
    of hazardous waste identified in Subpart C of this Part. (However, wastes
    that exhibit a characteristic at the point of generation may still be subject
    to the requirements of 35 Ill. Adm. Code 728, even if they no longer
    exhibit a characteristic at the point of land disposal.)
     
    2) In the case of a waste that is a listed waste under Subpart D of this Part, a
    waste that contains a waste listed under Subpart D of this Part, or a waste
    that is derived from a waste listed in Subpart D of this Part, it also has
    been excluded from subsection (e) of this Section under 35 Ill. Adm. Code
    720.120 and 720.122.
     
    e) Specific inclusions and exclusions.
     
    1) Except as otherwise provided in subsection (e)(2), (g), or (h) of this
    Section, any solid waste generated from the treatment, storage, or disposal
    of a hazardous waste, including any sludge, spill residue, ash, emission
    control dust, or leachate (but not including precipitation run-off), is a

     
    125
    hazardous waste. (However, materials that are reclaimed from solid
    wastes and that are used beneficially are not solid wastes and hence are
    not hazardous wastes under this provision unless the reclaimed material is
    burned for energy recovery or used in a manner constituting disposal.)
     
    2) The following solid wastes are not hazardous even though they are
    generated from the treatment, storage, or disposal of a hazardous waste,
    unless they exhibit one or more of the characteristics of hazardous waste:
     
    A) Waste pickle liquor sludge generated by lime stabilization of spent
    pickle liquor from the iron and steel industry (SIC Codes 331 and
    332).
     
    B) Wastes from burning any of the materials exempted from
    regulation by Section 721.106(a)(3)(C) and (a)(3)(D).
     
    C) Nonwastewater residues, such as slag, resulting from high
    temperature metal recovery (HTMR) processing of K061, K062, or
    F006 waste in the units identified in this subsection (e)(2) that are
    disposed of in non-hazardous waste units, provided that these
    residues meet the generic exclusion levels identified in the tables
    in this subsection (e)(2)(C) for all constituents and the residues
    exhibit no characteristics of hazardous waste. The types of units
    identified are rotary kilns, flame reactors, electric furnaces, plasma
    arc furnaces, slag reactors, rotary hearth furnace/electric furnace
    combinations, or the following types of industrial furnaces (as
    defined in 35 Ill. Adm. Code 720.110): blast furnaces; smelting,
    melting, and refining furnaces (including pyrometallurgical
    devices such as cupolas, reverberator furnaces, sintering machines,
    roasters, and foundry furnaces); and other furnaces designated by
    the Agency pursuant to that definition.
     
    i) Testing requirements must be incorporated in a facility’s
    waste analysis plan or a generator’s self-implementing
    waste analysis plan; at a minimum, composite samples of
    residues must be collected and analyzed quarterly and
    when the process or operation generating the waste
    changes.
     
    ii) Persons claiming this exclusion in an enforcement action
    will have the burden of proving by clear and convincing
    evidence that the material meets all of the exclusion
    requirements. The generic exclusion levels are the
    following:
     
    Generic exclusion levels for K061 and K062

     
    126
    nonwastewater HTMR residues:
     
    Constituent Maximum for any single
    composite sample
    (mg/Lmg/
    )
    Antimony 0.10
    Arsenic 0.50
    Barium 7.6
    Beryllium 0.010
    Cadmium 0.050
    Chromium (total) 0.33
    Lead 0.15
    Mercury 0.009
    Nickel 1.0
    Selenium 0.16
    Silver 0.30
    Thallium 0.020
    Vanadium 1.26
    Zinc 70
     
    Generic exclusion levels for F006 nonwastewater HTMR
    residues:
     
    Constituent Maximum for any single
    composite sample
    (mg/Lmg/
    )
    Antimony 0.10
    Arsenic 0.50
    Barium 7.6
    Beryllium 0.010
    Cadmium 0.050
    Chromium (total) 0.33
    Cyanide (total) (mg/kg) 1.8
    Lead 0.15
    Mercury 0.009
    Nickel 1.0
    Selenium 0.16
    Silver 0.30
    Thallium 0.020
    Zinc 70
     
    iii) A one-time notification and certification must be placed in
    the facility’s files and sent to the Agency (or, for out-of-
    State shipments, to the appropriate Regional Administrator
    of USEPA or the state agency authorized to implement
    federal 40 CFR 268 requirements) for K061, K062, or F006

     
    127
    HTMR residues that meet the generic exclusion levels for
    all constituents, which do not exhibit any characteristics,
    and which are sent to RCRA Subtitle D (municipal solid
    waste landfill) units. The notification and certification that
    is placed in the generator’s or treater’s files must be
    updated if the process or operation generating the waste
    changes or if the RCRA Subtitle D unit receiving the waste
    changes. However, the generator or treater need only
    notify the Agency on an annual basis if such changes
    occur. Such notification and certification should be sent to
    the Agency by the end of the calendar year, but no later
    than December 31. The notification must include the
    following information: the name and address of the
    nonhazardous waste management unit receiving the waste
    shipment; the USEPA hazardous waste number and
    treatability group at the initial point of generation; and the
    treatment standards applicable to the waste at the initial
    point of generation. The certification must be signed by an
    authorized representative and must state as follows:
     
    “I certify under penalty of law that the generic
    exclusion levels for all constituents have been met
    without impermissible dilution and that no
    characteristic of hazardous waste is exhibited. I am
    aware that there are significant penalties for
    submitting a false certification, including the
    possibility of fine and imprisonment.”
     
    D) Biological treatment sludge from the treatment of one of the
    following wastes listed in Section 721.132: organic waste
    (including heavy ends, still bottoms, light ends, spent solvents,
    filtrates, and decantates) from the production of carbamates and
    carbamoyl oximes (USEPA Hazardous Waste No. K156) and
    wastewaters from the production of carbamates and carbamoyl
    oximes (USEPA Hazardous Waste No. K157).
     
    E) Catalyst inert support media separated from one of the following
    wastes listed in Section 721.132: spent hydrotreating catalyst
    (USEPA hazardous waste number K171) and spent hydrorefining
    catalyst (USEPA hazardous waste number K172).
     
    BOARD NOTE: This subsection (e) would normally correspond with 40 CFR
    261.3(e), a subsection that has been deleted and marked “reserved” by USEPA.
    Rather, this subsection (e) corresponds with 40 CFR 261.3(c)(2), which the Board
    codified here to comport with codification requirements and to enhance clarity.
     

     
    128
    f) Notwithstanding subsections (a) through (e) of this Section and provided the
    debris, as defined in 35 Ill. Adm. Code 728.102, does not exhibit a characteristic
    identified at Subpart C of this Part, the following materials are not subject to
    regulation under 35 Ill. Adm. Code 702, 703, 720, 721 to 726, or 728:
     
    1) Hazardous debris as defined in 35 Ill. Adm. Code 728.102 that has been
    treated using one of the required extraction or destruction technologies
    specified in Table F to 35 Ill. Adm. Code 728; persons claiming this
    exclusion in an enforcement action will have the burden of proving by
    clear and convincing evidence that the material meets all of the exclusion
    requirements; or
     
    2) Debris, as defined in 35 Ill. Adm. Code 728.102, that the Agency,
    considering the extent of contamination, has determined is no longer
    contaminated with hazardous waste.
     
    g) Exclusion of certain wastes listed in Subpart D of this Part solely because they
    exhibit a characteristic of ignitability, corrosivity, or reactivity.
     
    1) A hazardous waste that is listed in Subpart D of this Part solely because it
    exhibits one or more characteristics of ignitability, as defined under
    Section 721.121; corrosivity, as defined under Section 721.122; or
    reactivity, as defined under Section 721.123 is not a hazardous waste if the
    waste no longer exhibits any characteristic of hazardous waste identified
    in Subpart C of this Part.
     
    2) The exclusion described in subsection (g)(1) of this Section also pertains
    to the following:
     
    A) Any mixture of a solid waste and a hazardous waste listed in
    Subpart D of this Part solely because it exhibits the characteristics
    of ignitability, corrosivity, or reactivity, as regulated under
    subsection (a)(2)(D) of this Section; and
     
    B) Any solid waste generated from treating, storing, or disposing of a
    hazardous waste listed in Subpart D of this Part solely because it
    exhibits the characteristics of ignitability, corrosivity, or reactivity,
    as regulated under subsection (e)(1) of this Section.
     
    3) Wastes excluded under this subection (g) are subject to 35 Ill. Adm. Code
    728 (as applicable), even if they no longer exhibit a characteristic at the
    point of land disposal.
     
    h) Eligible radioactive mixed waste.
     
    1) Hazardous waste containing radioactive waste is no longer a hazardous

     
    129
    waste when it meets the eligibility criteria and conditions of Subpart N of
    35 Ill. Adm. Code 726 (i.e., it is “eligible radioactive mixed waste”).
     
    2) The exemption described in subsection (h)(1) of this Section also pertains
    to the following:
     
    A) Any mixture of a solid waste and an eligible radioactive mixed
    waste; and
     
    B) Any solid waste generated from treating, storing, or disposing of
    an eligible radioactive mixed waste.
     
    3) Waste exempted under this subsection (h) must meet the eligibility criteria
    and specified conditions in 35 Ill. Adm. Code 726.325 and 726.330 (for
    storage and treatment) and in 35 Ill. Adm. Code 726.410 and 726.415 (for
    transportation and disposal). Waste that fails to satisfy these eligibility
    criteria and conditions is regulated as hazardous waste.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.104 Exclusions
     
    a) Materials that are not solid wastes. The following materials are not solid wastes
    for the purpose of this Part:
     
    1) Sewage.
     
    A) Domestic sewage (untreated sanitary wastes that pass through a
    sewer system); and
     
    B) Any mixture of domestic sewage and other waste that passes
    through a sewer system to publicly-owned treatment works for
    treatment.
     
    2) Industrial wastewater discharges that are point source discharges with
    National Pollutant Discharge Elimination System (NPDES) permits issued
    by the Agency pursuant to Section 12(f) of the Environmental Protection
    Act and 35 Ill. Adm. Code 309.
     
    BOARD NOTE: This exclusion applies only to the actual point source
    discharge. It does not exclude industrial wastewaters while they are being
    collected, stored, or treated before discharge, nor does it exclude sludges
    that are generated by industrial wastewater treatment.
     
    3) Irrigation return flows.
     

     
    130
    4) Source, by-product, or special nuclear material, as defined by section 11
    of the Atomic Energy Act of 1954, as amended (42 USC 2011 et seq.
    2014), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    5) Materials subjected to in-situ mining techniques that are not removed from
    the ground as part of the extraction process.
     
    6) Pulping liquors (i.e., black liquors) that are reclaimed in a pulping liquor
    recovery furnace and then reused in the pulping process, unless it is
    accumulated speculatively, as defined in Section 721.101(c).
     
    7) Spent sulfuric acid used to produce virgin sulfuric acid, unless it is
    accumulated speculatively, as defined in Section 721.101(c).
     
    8) Secondary materials that are reclaimed and returned to the original process
    or processes in which they were generated, where they are reused in the
    production process, provided that the following is true:
     
    A) Only tank storage is involved, and the entire process through
    completion of reclamation is closed by being entirely connected
    with pipes or other comparable enclosed means of conveyance;
     
    B) Reclamation does not involve controlled flame combustion (such
    as occurs in boilers, industrial furnaces, or incinerators);
     
    C) The secondary materials are never accumulated in such tanks for
    over 12 months without being reclaimed; and
     
    D) The reclaimed material is not used to produce a fuel or used to
    produce products that are used in a manner constituting disposal.
     
    9) Wood preserving wastes.
     
    A) Spent wood preserving solutions that have been used and which
    are reclaimed and reused for their original intended purpose;
     
    B) Wastewaters from the wood preserving process that have been
    reclaimed and which are reused to treat wood; and
     
    C) Prior to reuse, the wood preserving wastewaters and spent wood
    preserving solutions described in subsections (a)(9)(A) and
    (a)(9)(B) of this Section, so long as they meet all of the following
    conditions:
     
    i) The wood preserving wastewaters and spent wood
    preserving solutions are reused on-site at water-borne

     
    131
    plants in the production process for their original intended
    purpose;
     
    ii) Prior to reuse, the wastewaters and spent wood preserving
    solutions are managed to prevent release to either land or
    groundwater or both;
     
    iii) Any unit used to manage wastewaters or spent wood
    preserving solutions prior to reuse can be visually or
    otherwise determined to prevent such releases;
     
    iv) Any drip pad used to manage the wastewaters or spent
    wood preserving solutions prior to reuse complies with the
    standards in Subpart W of 35 Ill. Adm. Code 725,
    regardless of whether the plant generates a total of less than
    100 kg/month of hazardous waste; and
     
    v) Prior to operating pursuant to this exclusion, the plant
    owner or operator submits a one-time notification to the
    Agency stating that the plant intends to claim the exclusion,
    giving the date on which the plant intends to begin
    operating under the exclusion, and containing the following
    language: “I have read the applicable regulation
    establishing an exclusion for wood preserving wastewaters
    and spent wood preserving solutions and understand it
    requires me to comply at all times with the conditions set
    out in the regulation.” The plant must maintain a copy of
    that document in its on-site records for a period of no less
    than three years from the date specified in the notice. The
    exclusion applies only so long as the plant meets all of the
    conditions. If the plant goes out of compliance with any
    condition, it may apply to the Agency for reinstatement.
    The Agency must reinstate the exclusion in writing if it
    finds that the plant has returned to compliance with all
    conditions and that violations are not likely to recur. If the
    Agency denies an application, it must transmit to the
    applicant specific, detailed statements in writing as to the
    reasons it denied the application. The applicant under this
    subsection (a)(9)(C)(v) may appeal the Agency’s
    determination to deny the reinstatement, to grant the
    reinstatement with conditions, or to terminate a
    reinstatement before the Board pursuant to Section 40 of
    the Act [415 ILCS 5/40].
     
    10) Hazardous waste numbers K060, K087, K141, K142, K143, K144, K145,
    K147, and K148, and any wastes from the coke by-products processes that

     
    132
    are hazardous only because they exhibit the toxicity characteristic
    specified in Section 721.124, when subsequent to generation these
    materials are recycled to coke ovens, to the tar recovery process as a
    feedstock to produce coal tar, or are mixed with coal tar prior to the tar’s
    sale or refining. This exclusion is conditioned on there being no land
    disposal of the waste from the point it is generated to the point it is
    recycled to coke ovens, to tar recovery, to the tar refining processes, or
    prior to when it is mixed with coal.
     
    11) Nonwastewater splash condenser dross residue from the treatment of
    hazardous waste number K061 in high temperature metals recovery units,
    provided it is shipped in drums (if shipped) and not land disposed before
    recovery.
     
    12) Certain oil-bearing hazardous secondary materials and recovered oil, as
    follows:
     
    A) Oil-bearing hazardous secondary materials (i.e., sludges, by-
    products, or spent materials) that are generated at a petroleum
    refinery (standard industrial classification (SIC code 2911) and are
    inserted into the petroleum refining process (SIC code 2911:
    including, but not limited to, distillation, catalytic cracking,
    fractionation, or thermal cracking units (i.e., cokers)), unless the
    material is placed on the land, or speculatively accumulated before
    being so recycled. Materials inserted into thermal cracking units
    are excluded under this subsection (a)(12), provided that the coke
    product also does not exhibit a characteristic of hazardous waste.
    Oil-bearing hazardous secondary materials may be inserted into
    the same petroleum refinery where they are generated or sent
    directly to another petroleum refinery and still be excluded under
    this provision. Except as provided in subsection (a)(12)(B) of this
    Section, oil-bearing hazardous secondary materials generated
    elsewhere in the petroleum industry (i.e., from sources other than
    petroleum refineries) are not excluded under this Section.
    Residuals generated from processing or recycling materials
    excluded under this subsection (a)(12)(A), where such materials as
    generated would have otherwise met a listing under Subpart D of
    this Part, are designated as USEPA hazardous waste number F037
    listed wastes when disposed of or intended for disposal.
     
    B) Recovered oil that is recycled in the same manner and with the
    same conditions as described in subsection (a)(12)(A) of this
    Section. Recovered oil is oil that has been reclaimed from
    secondary materials (including wastewater) generated from normal
    petroleum industry practices, including refining, exploration and
    production, bulk storage, and transportation incident thereto (SIC

     
    133
    codes 1311, 1321, 1381, 1382, 1389, 2911, 4612, 4613, 4922,
    4923, 4789, 5171, and 5172). Recovered oil does not include oil-
    bearing hazardous wastes listed in Subpart D of this Part; however,
    oil recovered from such wastes may be considered recovered oil.
    Recovered oil does not include used oil, as defined in 35 Ill. Adm.
    Code 739.100.
     
    13) Excluded scrap metal (processed scrap metal, unprocessed home scrap
    metal, and unprocessed prompt scrap metal) being recycled.
     
    14) Shredded circuit boards being recycled, provided that they meet the
    following conditions:
     
    A) The circuit boards are stored in containers sufficient to prevent a
    release to the environment prior to recovery; and
     
    B) The circuit boards are free of mercury switches, mercury relays,
    nickel-cadmium batteries, and lithium batteries.
     
    15) Condensates derived from the overhead gases from kraft mill steam
    strippers that are used to comply with federal Clean Air Act regulation 40
    CFR 63.446(e). The exemption applies only to combustion at the mill
    generating the condensates.
     
    16) Comparable fuels or comparable syngas fuels (i.e., comparable or syngas
    fuels) that meet the requirements of Section 721.138.
     
    17) Spent materials (as defined in Section 721.101) (other than hazardous
    wastes listed in Subpart D of this Part) generated within the primary
    mineral processing industry from which minerals, acids, cyanide, water, or
    other values are recovered by mineral processing or by benefication,
    provided that the following is true:
     
    A) The spent material is legitimately recycled to recover minerals,
    acids, cyanide, water, or other values;
     
    B) The spent material is not accumulated speculatively;
     
    C) Except as provided in subsection (a)(17)(D) of this Section, the
    spent material is stored in tanks, containers, or buildings that meet
    the following minimum integrity standards: a building must be an
    engineered structure with a floor, walls, and a roof all of which are
    made of non-earthen materials providing structural support (except
    that smelter buildings may have partially earthen floors, provided
    that the spent material is stored on the non-earthen portion), and
    have a roof suitable for diverting rainwater away from the

     
    134
    foundation; a tank must be free standing, not be a surface
    impoundment (as defined in 35 Ill. Adm. Code 720.110), and be
    manufactured of a material suitable for containment of its contents;
    a container must be free standing and be manufactured of a
    material suitable for containment of its contents. If a tank or
    container contains any particulate that may be subject to wind
    dispersal, the owner or operator must operate the unit in a manner
    that controls fugitive dust. A tank, container, or building must be
    designed, constructed, and operated to prevent significant releases
    to the environment of these materials.
     
    D) The Agency must allow by permit that solid mineral processing
    spent materials only may be placed on pads, rather than in tanks,
    containers, or buildings if the facility owner or operator can
    demonstrate the following: the solid mineral processing secondary
    materials do not contain any free liquid; the pads are designed,
    constructed, and operated to prevent significant releases of the
    spent material into the environment; and the pads provide the same
    degree of containment afforded by the non-RCRA tanks,
    containers, and buildings eligible for exclusion.
     
    i) The Agency must also consider whether storage on pads
    poses the potential for significant releases via groundwater,
    surface water, and air exposure pathways. Factors to be
    considered for assessing the groundwater, surface water,
    and air exposure pathways must include the following: the
    volume and physical and chemical properties of the spent
    material, including its potential for migration off the pad;
    the potential for human or environmental exposure to
    hazardous constituents migrating from the pad via each
    exposure pathway; and the possibility and extent of harm to
    human and environmental receptors via each exposure
    pathway.
     
    ii) Pads must meet the following minimum standards: they
    must be designed of non-earthen material that is compatible
    with the chemical nature of the mineral processing spent
    material; they must be capable of withstanding physical
    stresses associated with placement and removal; they must
    have runon and runoff controls; they must be operated in a
    manner that controls fugitive dust; and they must have
    integrity assurance through inspections and maintenance
    programs.
     
    iii) Before making a determination under this subsection
    (a)(17)(D), the Agency must provide notice and the

     
    135
    opportunity for comment to all persons potentially
    interested in the determination. This can be accomplished
    by placing notice of this action in major local newspapers,
    or broadcasting notice over local radio stations.
     
    BOARD NOTE: See Subpart D of 35 Ill. Adm. Code 703
    for the RCRA Subtitle C permit public notice requirements.
     
    E) The owner or operator provides a notice to the Agency, providing
    the following information: the types of materials to be recycled,
    the type and location of the storage units and recycling processes,
    and the annual quantities expected to be placed in non-land-based
    units. This notification must be updated when there is a change in
    the type of materials recycled or the location of the recycling
    process.
     
    F) For purposes of subsection (b)(7) of this Section, mineral
    processing spent materials must be the result of mineral processing
    and may not include any listed hazardous wastes. Listed
    hazardous wastes and characteristic hazardous wastes generated by
    non-mineral processing industries are not eligible for the
    conditional exclusion from the definition of solid waste.
     
    18) Petrochemical recovered oil from an associated organic chemical
    manufacturing facility, where the oil is to be inserted into the petroleum
    refining process (SIC code 2911) along with normal petroleum refinery
    process streams, provided that both of the following conditions are true of
    the oil:
     
    A) The oil is hazardous only because it exhibits the characteristic of
    ignitability (as defined in Section 721.121) or toxicity for benzene
    (Section 721.124, USEPA hazardous waste code D018);
     
    B) The oil generated by the organic chemical manufacturing facility is
    not placed on the land, or speculatively accumulated before being
    recycled into the petroleum refining process. An “associated
    organic chemical manufacturing facility” is a facility for which all
    of the following is true: its primary SIC code is 2869, but its
    operations may also include SIC codes 2821, 2822, and 2865; it is
    physically co-located with a petroleum refinery; and the petroleum
    refinery to which the oil being recycled is returned also provides
    hydrocarbon feedstocks to the organic chemical manufacturing
    facility. “Petrochemical recovered oil” is oil that has been
    reclaimed from secondary materials (i.e., sludges, by-products, or
    spent materials, including wastewater) from normal organic
    chemical manufacturing operations, as well as oil recovered from

     
    136
    organic chemical manufacturing processes.
     
    19) Spent caustic solutions from petroleum refining liquid treating processes
    used as a feedstock to produce cresylic or naphthenic acid, unless the
    material is placed on the land or accumulated speculatively, as defined in
    Section 721.101(c).
     
    20) Hazardous secondary materials used to make zinc fertilizers, provided that
    the following conditions are satisfied:
     
    A) Hazardous secondary materials used to make zinc micronutrient
    fertilizers must not be accumulated speculatively, as defined in
    Section 721.101(c)(8).
     
    B) A generator or intermediate handler of zinc-bearing hazardous
    secondary materials that are to be incorporated into zinc fertilizers
    must fulfill the following conditions:
     
    i) It must submit a one-time notice to the Agency that
    contains the name, address, and USEPA identification
    number of the generator or intermediate handler facility,
    that provides a brief description of the secondary material
    that will be subject to the exclusion, and which identifies
    when the manufacturer intends to begin managing excluded
    zinc-bearing hazardous secondary materials under the
    conditions specified in this subsection (a)(20).
     
    ii) It must store the excluded secondary material in tanks,
    containers, or buildings that are constructed and maintained
    in a way which prevents releases of the secondary materials
    into the environment. At a minimum, any building used for
    this purpose must be an engineered structure made of non-
    earthen materials that provide structural support, and it
    must have a floor, walls, and a roof that prevent wind
    dispersal and contact with rainwater. A tank used for this
    purpose must be structurally sound and, if outdoors, it must
    have a roof or cover that prevents contact with wind and
    rain. A container used for this purpose must be kept
    closed, except when it is necessary to add or remove
    material, and it must be in sound condition. Containers that
    are stored outdoors must be managed within storage areas
    that fulfill the conditions of subsection (a)(20)(F) of this
    Section:
     
    iii) With each off-site shipment of excluded hazardous
    secondary materials, it must provide written notice to the

     
    137
    receiving facility that the material is subject to the
    conditions of this subsection (a)(20).
     
    iv) It must maintain records at the generator’s or intermediate
    handler’s facility for no less than three years of all
    shipments of excluded hazardous secondary materials. For
    each shipment these records must, at a minimum, contain
    the information specified in subsection (a)(20)(G) of this
    Section.
     
    C) A manufacturer of zinc fertilizers or zinc fertilizer ingredients
    made from excluded hazardous secondary materials must fulfill the
    following conditions:
     
    i) It must store excluded hazardous secondary materials in
    accordance with the storage requirements for generators
    and intermediate handlers, as specified in subsection
    (a)(20)(B)(ii) of this Section.
     
    ii) It must submit a one-time notification to the Agency that, at
    a minimum, specifies the name, address, and USEPA
    identification number of the manufacturing facility and
    which identifies when the manufacturer intends to begin
    managing excluded zinc-bearing hazardous secondary
    materials under the conditions specified in this subsection
    (a)(20).
     
    iii) It must maintain for a minimum of three years records of
    all shipments of excluded hazardous secondary materials
    received by the manufacturer, which must at a minimum
    identify for each shipment the name and address of the
    generating facility, the name of transporter, and the date on
    which the materials were received, the quantity received,
    and a brief description of the industrial process that
    generated the material.
     
    iv) It must submit an annual report to the Agency that
    identifies the total quantities of all excluded hazardous
    secondary materials that were used to manufacture zinc
    fertilizers or zinc fertilizer ingredients in the previous year,
    the name and address of each generating facility, and the
    industrial processes from which the hazardous secondary
    materials were generated.
     
    D) Nothing in this Section preempts, overrides, or otherwise negates
    the provision in 35 Ill. Adm. Code 722.111 that requires any

     
    138
    person who generates a solid waste to determine if that waste is a
    hazardous waste.
     
    E) Interim status and permitted storage units that have been used to
    store only zinc-bearing hazardous wastes prior to the submission
    of the one-time notice described in subsection (a)(20)(B)(i) of this
    Section, and that afterward will be used only to store hazardous
    secondary materials excluded under this subsection (a)(20), are not
    subject to the closure requirements of 35 Ill. Adm. Code 724 and
    725.
     
    F) A container used to store excluded secondary material must fulfill
    the following conditions:
     
    i) It must have containment structures or systems sufficiently
    impervious to contain leaks, spills, and accumulated
    precipitation;
     
    ii) It must provide for effective drainage and removal of leaks,
    spills, and accumulated precipitation; and
     
    iii) It must prevent run-on into the containment system.
     
    BOARD NOTE: Subsections (a)(20)(F)(i) through (a)(20)(F)(iii)
    are derived from 40 CFR 261.4(a)(20)(ii)(B)(
    1
    ) through
    (a)(20)(ii)(B)(
    3
    ). The Board added the preamble to these federal
    paragraphs as subsection (a)(20)(F) to comport with Illinois
    Administrative Code codification requirements.
     
    G) Required records of shipments of excluded hazardous secondary
    materials must, at a minimum, contain the following information:
     
    i) The name of the transporter and date of the shipment;
     
    ii) The name and address of the facility that received the
    excluded material, along with documentation confirming
    receipt of the shipment; and
     
    iii) The type and quantity of excluded secondary material in
    each shipment.
     
    BOARD NOTE: Subsections (a)(20)(G)(i) through (a)(20)(G)(iii)
    are derived from 40 CFR 261.4(a)(20)(ii)(D)(
    1
    ) through
    (a)(20)(ii)(D)(
    3
    ). The Board added the preamble to these federal
    paragraphs as subsection (a)(20)(G) to comport with Illinois
    Administrative Code codification requirements.

     
    139
     
    21) Zinc fertilizers made from hazardous wastes or hazardous secondary
    materials that are excluded under subsection (a)(20) of this Section,
    provided that the following conditions are fulfilled:
     
    A) The fertilizers meet the following contaminant limits:
     
    i) For metal contaminants:
     
    Constituent Maximum Allowable Total Concentration
    in Fertilizer, per Unit (1%) of Zinc (ppm)
    Arsenic 0.3
    Cadmium 1.4
    Chromium 0.6
    Lead 2.8
    Mercury 0.3
     
    ii) For dioxin contaminants, the fertilizer must contain no
    more than eight parts per trillion of dioxin, measured as
    toxic equivalent (TEQ).
     
    B) The manufacturer performs sampling and analysis of the fertilizer
    product to determine compliance with the contaminant limits for
    metals no less frequently than once every six months, and for
    dioxins no less frequently than once every 12 months. Testing
    must also be performed whenever changes occur to manufacturing
    processes or ingredients that could significantly affect the amounts
    of contaminants in the fertilizer product. The manufacturer may
    use any reliable analytical method to demonstrate that no
    constituent of concern is present in the product at concentrations
    above the applicable limits. It is the responsibility of the
    manufacturer to ensure that the sampling and analysis are
    unbiased, precise, and representative of the products introduced
    into commerce.
     
    C) The manufacturer maintains for no less than three years records of
    all sampling and analyses performed for purposes of determining
    compliance with the requirements of subsection (a)(21)(B) of this
    Section. Such records must at a minimum include the following:
     
    i) The dates and times product samples were taken, and the
    dates the samples were analyzed;
     
    ii) The names and qualifications of the persons taking the
    samples;
     

     
    140
    iii) A description of the methods and equipment used to take
    the samples;
     
    iv) The name and address of the laboratory facility at which
    analyses of the samples were performed;
     
    v) A description of the analytical methods used, including any
    cleanup and sample preparation methods; and
     
    vi) All laboratory analytical results used to determine
    compliance with the contaminant limits specified in this
    subsection (a)(21).
     
    b) Solid wastes that are not hazardous wastes. The following solid wastes are not
    hazardous wastes:
     
    1) Household waste, including household waste that has been collected,
    transported, stored, treated, disposed, recovered (e.g., refuse-derived fuel),
    or reused. “Household waste” means any waste material (including
    garbage, trash, and sanitary wastes in septic tanks) derived from
    households (including single and multiple residences, hotels, and motels,
    bunkhouses, ranger stations, crew quarters, campgrounds, picnic grounds,
    and day-use recreation areas). A resource recovery facility managing
    municipal solid waste must not be deemed to be treating, storing,
    disposing of, or otherwise managing hazardous wastes for the purposes of
    regulation under this Part, if the following describe the facility:
     
    A) The facility receives and burns only the following waste:
     
    i) Household waste (from single and multiple dwellings,
    hotels, motels, and other residential sources); or
     
    ii) Solid waste from commercial or industrial sources that
    does not contain hazardous waste; and
     
    B) The facility does not accept hazardous waste and the owner or
    operator of such facility has established contractual requirements
    or other appropriate notification or inspection procedures to assure
    that hazardous wastes are not received at or burned in such facility.
     
    BOARD NOTE: The U.S. Supreme Court determined, in City of Chicago
    v. Environmental Defense Fund, Inc., 511 U.S. 328, 114 S. Ct. 1588, 128
    L. Ed. 2d 302 (1994), that this exclusion and RCRA section 3001(i) (42
    USC 6921(i)) do not exclude the ash from facilities covered by this
    subsection (b)(1) from regulation as a hazardous waste. At 59 Fed. Reg.
    29372 (June 7, 1994), USEPA granted facilities managing ash from such

     
    141
    facilities that is determined a hazardous waste under Subpart C of this Part
    until December 7, 1994 to file a Part A permit application pursuant to 35
    Ill. Adm. Code 703.181. At 60 Fed. Reg. 6666 (Feb. 3, 1995), USEPA
    stated that it interpreted that the point at which ash becomes subject to
    RCRA Subtitle C regulation is when that material leaves the combustion
    building (including connected air pollution control equipment).
     
    2) Solid wastes generated by any of the following that are returned to the soil
    as fertilizers:
     
    A) The growing and harvesting of agricultural crops, or
     
    B) The raising of animals, including animal manures.
     
    3) Mining overburden returned to the mine site.
     
    4) Fly ash waste, bottom ash waste, slag waste, and flue gas emission control
    waste generated primarily from the combustion of coal or other fossil
    fuels, except as provided in 35 Ill. Adm. Code 726.212 for facilities that
    burn or process hazardous waste.
     
    5) Drilling fluids, produced waters, and other wastes associated with the
    exploration, development, or production of crude oil, natural gas, or
    geothermal energy.
     
    6) Chromium wastes.
     
    A) Wastes that fail the test for the toxicity characteristic (Section
    721.124 and Appendix B to this Part) because chromium is present
    or which are listed in Subpart D of this Part due to the presence of
    chromium, that do not fail the test for the toxicity characteristic for
    any other constituent or which are not listed due to the presence of
    any other constituent, and that do not fail the test for any other
    characteristic, if the waste generator shows the following:
     
    i) The chromium in the waste is exclusively (or nearly
    exclusively) trivalent chromium;
     
    ii) The waste is generated from an industrial process that uses
    trivalent chromium exclusively (or nearly exclusively) and
    the process does not generate hexavalent chromium; and
     
    iii) The waste is typically and frequently managed in non-
    oxidizing environments.
     
    B) The following are specific wastes that meet the standard in

     
    142
    subsection (b)(6)(A) of this Section (so long as they do not fail the
    test for the toxicity characteristic for any other constituent and do
    not exhibit any other characteristic):
     
    i) Chrome (blue) trimmings generated by the following
    subcategories of the leather tanning and finishing industry:
    hair pulp/chrome tan/retan/wet finish, hair save/chrome
    tan/retan/wet finish, retan/wet finish, no beamhouse,
    through-the-blue, and shearling;
     
    ii) Chrome (blue) shavings generated by the following
    subcategories of the leather tanning and finishing industry:
    hair pulp/chrome tan/retan/wet finish, hair save/chrome
    tan/retan/wet finish, retan/wet finish, no beamhouse,
    through-the-blue, and shearling;
     
    iii) Buffing dust generated by the following subcategories of
    the leather tanning and finishing industry: hair
    pulp/chrome tan/retan/wet finish, hair save/chrome
    tan/retan/wet finish, retan/wet finish, no beamhouse,
    through-the-blue;
     
    iv) Sewer screenings generated by the following subcategories
    of the leather tanning and finishing industry: hair
    pulp/chrome tan/retan/wet finish, hair save/chrome
    tan/retan/wet finish, retan/wet finish, no beamhouse,
    through-the-blue, and shearling;
     
    v) Wastewater treatment sludges generated by the following
    subcategories of the leather tanning and finishing industry:
    hair pulp/chrome tan/retan/wet finish, hair save/chrome
    tan/retan/wet finish, retan/wet finish, no beamhouse,
    through-the-blue, and shearling;
     
    vi) Wastewater treatment sludges generated by the following
    subcategories of the leather tanning and finishing industry:
    hair pulp/chrome tan/retan/wet finish, hair save/chrome
    tan/retan/wet finish, and through-the-blue;
     
    vii) Waste scrap leather from the leather tanning industry, the
    shoe manufacturing industry, and other leather product
    manufacturing industries; and
     
    viii) Wastewater treatment sludges from the production of
    titanium dioxide pigment using chromium-bearing ores by
    the chloride process.

     
    143
     
    7) Solid waste from the extraction, beneficiation, and processing of ores and
    minerals (including coal, phosphate rock, and overburden from the mining
    of uranium ore), except as provided by 35 Ill. Adm. Code 726.212 for
    facilities that burn or process hazardous waste.
     
    A) For purposes of this subsection (b)(7), beneficiation of ores and
    minerals is restricted to the following activities: crushing;
    grinding; washing; dissolution; crystallization; filtration; sorting;
    sizing; drying; sintering; pelletizing; briquetting; calcining to
    remove water or carbon dioxide; roasting; autoclaving or
    chlorination in preparation for leaching (except where the roasting
    (or autoclaving or chlorination) and leaching sequence produces a
    final or intermediate product that does not undergo further
    beneficiation or processing); gravity concentration; magnetic
    separation; electrostatic separation; floatation; ion exchange;
    solvent extraction; electrowinning; precipitation; amalgamation;
    and heap, dump, vat tank, and in situ leaching.
     
    B) For the purposes of this subsection (b)(7), solid waste from the
    processing of ores and minerals includes only the following wastes
    as generated:
     
    i) Slag from primary copper processing;
     
    ii) Slag from primary lead processing;
     
    iii) Red and brown muds from bauxite refining;
     
    iv) Phosphogypsum from phosphoric acid production;
     
    v) Slag from elemental phosphorus production;
     
    vi) Gasifier ash from coal gasification;
     
    vii) Process wastewater from coal gasification;
     
    viii) Calcium sulfate wastewater treatment plant sludge from
    primary copper processing;
     
    ix) Slag tailings from primary copper processing;
     
    x) Fluorogypsum from hydrofluoric acid production;
     
    xi) Process wastewater from hydrofluoric acid production;
     

     
    144
    xii) Air pollution control dust or sludge from iron blast
    furnaces;
     
    xiii) Iron blast furnace slag;
     
    xiv) Treated residue from roasting and leaching of chrome ore;
     
    xv) Process wastewater from primary magnesium processing
    by the anhydrous process;
     
    xvi) Process wastewater from phosphoric acid production;
     
    xvii) Basic oxygen furnace and open hearth furnace air pollution
    control dust or sludge from carbon steel production;
     
    xviii) Basic oxygen furnace and open hearth furnace slag from
    carbon steel production;
     
    xix) Chloride processing waste solids from titanium
    tetrachloride production; and
     
    xx) Slag from primary zinc production.
     
    C) A residue derived from co-processing mineral processing
    secondary materials with normal beneficiation raw materials or
    with normal mineral processing raw materials remains excluded
    under this subsection (b) if the following conditions are fulfilled:
     
    i) The owner or operator processes at least 50 percent by
    weight normal beneficiation raw materials or normal
    mineral processing raw materials; and
     
    ii) The owner or operator legitimately reclaims the secondary
    mineral processing materials.
     
    8) Cement kiln dust waste, except as provided by 35 Ill. Adm. Code 726.212
    for facilities that burn or process hazardous waste.
     
    9) Solid waste that consists of discarded arsenical-treated wood or wood
    products that fails the test for the toxicity characteristic for hazardous
    waste codes D004 through D017 and which is not a hazardous waste for
    any other reason if the waste is generated by persons that utilize the
    arsenical-treated wood and wood products for these materials’ intended
    end use.
     
    10) Petroleum-contaminated media and debris that fail the test for the toxicity

     
    145
    characteristic of Section 721.124 (hazardous waste codes D018 through
    D043 only) and which are subject to corrective action regulations under
    35 Ill. Adm. Code 731.
     
    11) This subsection (b)(11) corresponds with 40 CFR 261.4(b)(11), which
    expired by its own terms on January 25, 1993. This statement maintains
    structural parity with USEPA regulations.
     
    12) Used chlorofluorocarbon refrigerants from totally enclosed heat transfer
    equipment, including mobile air conditioning systems, mobile
    refrigeration, and commercial and industrial air conditioning and
    refrigeration systems, that use chlorofluorocarbons as the heat transfer
    fluid in a refrigeration cycle, provided the refrigerant is reclaimed for
    further use.
     
    13) Non-terne plated used oil filters that are not mixed with wastes listed in
    Subpart D of this Part, if these oil filters have been gravity hot-drained
    using one of the following methods:
     
    A) Puncturing the filter anti-drain back valve or the filter dome end
    and hot-draining;
     
    B) Hot-draining and crushing;
     
    C) Dismantling and hot-draining; or
     
    D) Any other equivalent hot-draining method that will remove used
    oil.
     
    14) Used oil re-refining distillation bottoms that are used as feedstock to
    manufacture asphalt products.
     
    15) Leachate or gas condensate collected from landfills where certain solid
    wastes have been disposed of, under the following circumstances:
     
    A) The following conditions must be fulfilled:
     
    i) The solid wastes disposed of would meet one or more of
    the listing descriptions for the following USEPA hazardous
    waste numbers that are generated after the effective date
    listed for the waste:
     
    USEPA Hazardous Waste
    Numbers
     
    Listing Effective
    Date
    K169, K170, K171, and K172 February 8, 1999

     
    146
     
    K174 and K175
     
    May 7, 2001
    K176, K177, and K178 May 20, 2002
     
      
    K181 August 23, 2005
     
    ii) The solid wastes described in subsection (b)(15)(A)(i) of
    this Section were disposed of prior to the effective date of
    the listing (as set forth in that subsection);
     
    iii) The leachate or gas condensate does not exhibit any
    characteristic of hazardous waste nor is derived from any
    other listed hazardous waste; and
     
    iv) Discharge of the leachate or gas condensate, including
    leachate or gas condensate transferred from the landfill to a
    POTW by truck, rail, or dedicated pipe, is subject to
    regulation under section 307(b) or 402 of the federal Clean
    Water Act.
     
    B) Leachate or gas condensate derived from K169, K170, K171, or
    K172, waste will no longer be exempt if it is stored or managed in
    a surface impoundment prior to discharge. After November 21,
    2003, leachate or gas condensate derived from K176, K177, or
    K178 waste will no longer be exempt if it is stored or managed in a
    surface impoundment prior to discharge. After February 26, 2007,
    leachate or gas condensate derived from K181 waste will no longer
    be exempt if it is stored or managed in a surface impoundment
    prior to discharge. There is one exception: if the surface
    impoundment is used to temporarily store leachate or gas
    condensate in response to an emergency situation (e.g., shutdown
    of wastewater treatment system), provided the impoundment has a
    double liner, and provided the leachate or gas condensate is
    removed from the impoundment and continues to be managed in
    compliance with the conditions of this subsection (b)(15) of this
    Section after the emergency ends.
     
    c) Hazardous wastes that are exempted from certain regulations. A hazardous waste
    that is generated in a product or raw material storage tank, a product or raw
    material transport vehicle or vessel, a product or raw material pipeline, or in a
    manufacturing process unit, or an associated non-waste-treatment manufacturing
    unit, is not subject to regulation under 35 Ill. Adm. Code 702, 703, 722 through
    725, and 728 or to the notification requirements of section 3010 of RCRA until it
    exits the unit in which it was generated, unless the unit is a surface impoundment,
    or unless the hazardous waste remains in the unit more than 90 days after the unit

     
    147
    ceases to be operated for manufacturing or for storage or transportation of product
    or raw materials.
     
    d) Samples.
     
    1) Except as provided in subsection (d)(2) of this Section, a sample of solid
    waste or a sample of water, soil, or air that is collected for the sole
    purpose of testing to determine its characteristics or composition is not
    subject to any requirements of this Part or 35 Ill. Adm. Code 702, 703,
    722 through 726, and 728. The sample qualifies when it fulfills one of the
    following conditions:
     
    A) The sample is being transported to a laboratory for the purpose of
    testing;
     
    B) The sample is being transported back to the sample collector after
    testing;
     
    C) The sample is being stored by the sample collector before transport
    to a laboratory for testing;
     
    D) The sample is being stored in a laboratory before testing;
     
    E) The sample is being stored in a laboratory for testing but before it
    is returned to the sample collector; or
     
    F) The sample is being stored temporarily in the laboratory after
    testing for a specific purpose (for example, until conclusion of a
    court case or enforcement action where further testing of the
    sample may be necessary).
     
    2) In order to qualify for the exemption in subsection (d)(1)(A) or (d)(1)(B)
    of this Section, a sample collector shipping samples to a laboratory and a
    laboratory returning samples to a sample collector must do the following:
     
    A) Comply with U.S. Department of Transportation (USDOT), U.S.
    Postal Service (USPS), or any other applicable shipping
    requirements; or
     
    B) Comply with the following requirements if the sample collector
    determines that USDOT, USPS, or other shipping requirements do
    not apply to the shipment of the sample:
     
    i) Assure that the following information accompanies the
    sample: The sample collector’s name, mailing address, and
    telephone number; the laboratory’s name, mailing address,

     
    148
    and telephone number; the quantity of the sample; the date
    of the shipment; and a description of the sample; and
     
    ii) Package the sample so that it does not leak, spill, or
    vaporize from its packaging.
     
    3) This exemption does not apply if the laboratory determines that the waste
    is hazardous but the laboratory is no longer meeting any of the conditions
    stated in subsection (d)(1) of this Section.
     
    e) Treatability study samples.
     
    1) Except as is provided in subsection (e)(2) of this Section, a person that
    generates or collects samples for the purpose of conducting treatability
    studies, as defined in 35 Ill. Adm. Code 720.110, are not subject to any
    requirement of 35 Ill. Adm. Code 721 through 723 or to the notification
    requirements of section 3010 of the Resource Conservation and Recovery
    Act. Nor are such samples included in the quantity determinations of
    Section 721.105 and 35 Ill. Adm. Code 722.134(d) when:
     
    A) The sample is being collected and prepared for transportation by
    the generator or sample collector;
     
    B) The sample is being accumulated or stored by the generator or
    sample collector prior to transportation to a laboratory or testing
    facility; or
     
    C) The sample is being transported to the laboratory or testing facility
    for the purpose of conducting a treatability study.
     
    2) The exemption in subsection (e)(1) of this Section is applicable to samples
    of hazardous waste being collected and shipped for the purpose of
    conducting treatability studies provided that the following conditions are
    fulfilled:
     
    A) The generator or sample collector uses (in “treatability studies”) no
    more than 10,000 kg of media contaminated with non-acute
    hazardous waste, 1000 1,000 kg of non-acute hazardous waste
    other than contaminated media, 1 kg of acute hazardous waste, or
    2500 2,500 kg of media contaminated with acute hazardous waste
    for each process being evaluated for each generated waste stream;
     
    B) The mass of each shipment does not exceed 10,000 kg; the 10,000
    kg quantity may be all media contaminated with non-acute
    hazardous waste, or may include 2500 2,500 kg of media
    contaminated with acute hazardous waste, 1000 1,000 kg of

     
    149
    hazardous waste, and 1 kg of acute hazardous waste;
     
    C) The sample must be packaged so that it does not leak, spill, or
    vaporize from its packaging during shipment and the requirements
    of subsections (e)(2)(C)(i) or (e)(2)(C)(ii) of this Section are met.
     
    i) The transportation of each sample shipment complies with
    U.S. Department of Transportation (USDOT), U.S. Postal
    Service (USPS), or any other applicable shipping
    requirements; or
     
    ii) If the USDOT, USPS, or other shipping requirements do
    not apply to the shipment of the sample, the following
    information must accompany the sample: The name,
    mailing address, and telephone number of the originator of
    the sample; the name, address, and telephone number of the
    facility that will perform the treatability study; the quantity
    of the sample; the date of the shipment; and, a description
    of the sample, including its USEPA hazardous waste
    number;
     
    D) The sample is shipped to a laboratory or testing facility that is
    exempt under subsection (f) of this Section, or has an appropriate
    RCRA permit or interim status;
     
    E) The generator or sample collector maintains the following records
    for a period ending three years after completion of the treatability
    study:
     
    i) Copies of the shipping documents;
     
    ii) A copy of the contract with the facility conducting the
    treatability study; and
     
    iii) Documentation showing the following: The amount of
    waste shipped under this exemption; the name, address, and
    USEPA identification number of the laboratory or testing
    facility that received the waste; the date the shipment was
    made; and whether or not unused samples and residues
    were returned to the generator; and
     
    F) The generator reports the information required in subsection
    (e)(2)(E)(iii) of this Section in its report under 35 Ill. Adm. Code
    722.141.
     
    3) The Agency may grant requests on a case-by-case basis for up to an

     
    150
    additional two years for treatability studies involving bioremediation. The
    Agency may grant requests, on a case-by-case basis, for quantity limits in
    excess of those specified in subsections (e)(2)(A), (e)(2)(B), and (f)(4) of
    this Section, for up to an additional 5000 5,000 kg of media contaminated
    with non-acute hazardous waste, 500 kg of non-acute hazardous waste,
    2500 2,500 kg of media contaminated with acute hazardous waste, and 1
    kg of acute hazardous waste under the circumstances set forth in either
    subsection (e)(3)(A) or (e)(3)(B) of this Section, subject to the limitations
    of subsection (e)(3)(C) of this Section:
     
    A) In response to requests for authorization to ship, store, and conduct
    further treatability studies on additional quantities in advance of
    commencing treatability studies. Factors to be considered in
    reviewing such requests include the nature of the technology, the
    type of process (e.g., batch versus continuous), the size of the unit
    undergoing testing (particularly in relation to scale-up
    considerations), the time or quantity of material required to reach
    steady-state operating conditions, or test design considerations,
    such as mass balance calculations.
     
    B) In response to requests for authorization to ship, store, and conduct
    treatability studies on additional quantities after initiation or
    completion of initial treatability studies when the following
    occurs: There has been an equipment or mechanical failure during
    the conduct of the treatability study, there is need to verify the
    results of a previously-conducted treatability study, there is a need
    to study and analyze alternative techniques within a previously-
    evaluated treatment process, or there is a need to do further
    evaluation of an ongoing treatability study to determine final
    specifications for treatment.
     
    C) The additional quantities allowed and timeframes allowed in
    subsections (e)(3)(A) and (e)(3)(B) of this Section are subject to all
    the provisions in subsections (e)(1) and (e)(2)(B) through (e)(2)(F)
    of this Section. The generator or sample collector must apply to
    the Agency and provide in writing the following information:
     
    i) The reason why the generator or sample collector requires
    additional time or quantity of sample for the treatability
    study evaluation and the additional time or quantity
    needed;
     
    ii) Documentation accounting for all samples of hazardous
    waste from the waste stream that have been sent for or
    undergone treatability studies, including the date each
    previous sample from the waste stream was shipped, the

     
    151
    quantity of each previous shipment, the laboratory or
    testing facility to which it was shipped, what treatability
    study processes were conducted on each sample shipped,
    and the available results of each treatability study;
     
    iii) A description of the technical modifications or change in
    specifications that will be evaluated and the expected
    results;
     
    iv) If such further study is being required due to equipment or
    mechanical failure, the applicant must include information
    regarding the reason for the failure or breakdown and also
    include what procedures or equipment improvements have
    been made to protect against further breakdowns; and
     
    v) Such other information as the Agency determines is
    necessary.
     
    4) Final Agency determinations pursuant to this subsection (e) may be
    appealed to the Board.
     
    f) Samples undergoing treatability studies at laboratories or testing facilities.
    Samples undergoing treatability studies and the laboratory or testing facility
    conducting such treatability studies (to the extent such facilities are not otherwise
    subject to RCRA requirements) are not subject to any requirement of this Part, or
    of 35 Ill. Adm. Code 702, 703, 722 through 726, and 728 or to the notification
    requirements of Section 3010 of the Resource Conservation and Recovery Act,
    provided that the requirements of subsections (f)(1) through (f)(11) of this Section
    are met. A mobile treatment unit may qualify as a testing facility subject to
    subsections (f)(1) through (f)(11) of this Section. Where a group of mobile
    treatment units are located at the same site, the limitations specified in
    subsections (f)(1) through (f)(11) of this Section apply to the entire group of
    mobile treatment units collectively as if the group were one mobile treatment unit.
     
    1) No less than 45 days before conducting treatability studies, the facility
    notifies the Agency in writing that it intends to conduct treatability studies
    under this subsection (f).
     
    2) The laboratory or testing facility conducting the treatability study has a
    USEPA identification number.
     
    3) No more than a total of 10,000 kg of “as received” media contaminated
    with non-acute hazardous waste, 2500 2,500 kg of media contaminated
    with acute hazardous waste, or 250 kg of other “as received” hazardous
    waste is subject to initiation of treatment in all treatability studies in any
    single day. “As received” waste refers to the waste as received in the

     
    152
    shipment from the generator or sample collector.
     
    4) The quantity of “as received” hazardous waste stored at the facility for the
    purpose of evaluation in treatability studies does not exceed 10,000 kg, the
    total of which can include 10,000 kg of media contaminated with non-
    acute hazardous waste, 2500 2,500 kg of media contaminated with acute
    hazardous waste, 1000 1,000 kg of non-acute hazardous wastes other than
    contaminated media, and 1 kg of acute hazardous waste. This quantity
    limitation does not include treatment materials (including non-hazardous
    solid waste) added to “as received” hazardous waste.
     
    5) No more than 90 days have elapsed since the treatability study for the
    sample was completed, or no more than one year (two years for
    treatability studies involving bioremediation) has elapsed since the
    generator or sample collector shipped the sample to the laboratory or
    testing facility, whichever date first occurs. Up to 500 kg of treated
    material from a particular waste stream from treatability studies may be
    archived for future evaluation up to five years from the date of initial
    receipt. Quantities of materials archived are counted against the total
    storage limit for the facility.
     
    6) The treatability study does not involve the placement of hazardous waste
    on the land or open burning of hazardous waste.
     
    7) The facility maintains records for three years following completion of
    each study that show compliance with the treatment rate limits and the
    storage time and quantity limits. The following specific information must
    be included for each treatability study conducted:
     
    A) The name, address, and USEPA identification number of the
    generator or sample collector of each waste sample;
     
    B) The date the shipment was received;
     
    C) The quantity of waste accepted;
     
    D) The quantity of “as received” waste in storage each day;
     
    E) The date the treatment study was initiated and the amount of “as
    received” waste introduced to treatment each day;
     
    F) The date the treatability study was concluded;
     
    G) The date any unused sample or residues generated from the
    treatability study were returned to the generator or sample
    collector or, if sent to a designated facility, the name of the facility

     
    153
    and the USEPA identification number.
     
    8) The facility keeps, on-site, a copy of the treatability study contract and all
    shipping papers associated with the transport of treatability study samples
    to and from the facility for a period ending three years from the
    completion date of each treatability study.
     
    9) The facility prepares and submits a report to the Agency by March 15 of
    each year that estimates the number of studies and the amount of waste
    expected to be used in treatability studies during the current year, and
    includes the following information for the previous calendar year:
     
    A) The name, address, and USEPA identification number of the
    facility conducting the treatability studies;
     
    B) The types (by process) of treatability studies conducted;
     
    C) The names and addresses of persons for whom studies have been
    conducted (including their USEPA identification numbers);
     
    D) The total quantity of waste in storage each day;
     
    E) The quantity and types of waste subjected to treatability studies;
     
    F) When each treatability study was conducted; and
     
    G) The final disposition of residues and unused sample from each
    treatability study.
     
    10) The facility determines whether any unused sample or residues generated
    by the treatability study are hazardous waste under Section 721.103 and, if
    so, are subject to 35 Ill. Adm. Code 702, 703, and 721 through 728, unless
    the residues and unused samples are returned to the sample originator
    under the exemption of subsection (e) of this Section.
     
    11) The facility notifies the Agency by letter when the facility is no longer
    planning to conduct any treatability studies at the site.
     
    g) Dredged material that is not a hazardous waste. Dredged material that is subject to
    the requirements of a permit that has been issued under section 404 of the Federal
    Water Pollution Control Act (33 USC 1344) is not a hazardous waste. For the
    purposes of this subsection (g), the following definitions apply:
     
    “Dredged material” has the same meaning as ascribed it in 40 CFR 232.2
    (Definitions), incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(b).

     
    154
     
    “Permit” means any of the following:
     
    A permit issued by the U.S. Army Corps of Engineers (Army Corps)
    under section 404 of the Federal Water Pollution Control Act (33
    USC 1344);
     
    A permit issued by the Army Corps under section 103 of the Marine
    Protection, Research, and Sanctuaries Act of 1972 (33 USC 1413);
    or
     
    In the case of Army Corps civil works projects, the administrative
    equivalent of the permits referred to in the preceding two paragraphs
    of this definition, as provided for in Army Corps regulations (for
    example, see 33 CFR 336.1, 336.2, and 337.6).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.105 Special Requirements for Hazardous Waste Generated by Small Quantity
    Generators
     
    a) A generator is a conditionally exempt small quantity generator in a calendar
    month if it generates no more than 100 kilograms of hazardous waste in that
    month.
     
    b) Except for those wastes identified in subsections (e), (f), (g), and (j) of this
    Section, a conditionally exempt small quantity generator’s hazardous wastes are
    not subject to regulation under 35 Ill. Adm. Code 702, 703, 722 through 726, and
    728, and the notification requirements of section 3010 of Resource Conservation
    and Recovery Act, provided the generator complies with the requirements of
    subsections (f), (g), and (j) of this Section.
     
    c) When making the quantity determinations of this Part and 35 Ill. Adm. Code 722,
    the generator must include all hazardous waste that it generates, except the
    following hazardous waste:
     
    1) Hazardous waste that is exempt from regulation under Section 721.104(c)
    through (f), 721.106(a)(3), 721.107(a)(1), or 721.108;
     
    2) Hazardous waste that is managed immediately upon generation only in on-
    site elementary neutralization units, wastewater treatment units, or totally
    enclosed treatment facilities, as defined in 35 Ill. Adm. Code 720.110;
     
    3) Hazardous waste that is recycled, without prior storage or accumulation,
    only in an on-site process subject to regulation under Section
    721.106(c)(2);

     
    155
     
    4) Hazardous waste that is used oil managed under the requirements of
    Section 721.106(a)(4) and 35 Ill. Adm. Code 739;
     
    5) Hazardous waste that is spent lead-acid batteries managed under the
    requirements of Subpart G of 35 Ill. Adm. Code 726; and
     
    6) Hazardous waste that is universal waste managed under Section 721.109
    and 35 Ill. Adm. Code 733.
     
    d) In determining the quantity of hazardous waste it generates, a generator need not
    include the following:
     
    1) Hazardous waste when it is removed from on-site storage;
     
    2) Hazardous waste produced by on-site treatment (including reclamation) of
    its hazardous waste so long as the hazardous waste that is treated was
    counted once;
     
    3) Spent materials that are generated, reclaimed, and subsequently reused on-
    site, so long as such spent materials have been counted once.
     
    e) If a generator generates acute hazardous waste in a calendar month in quantities
    greater than those set forth in subsections (e)(1) and (e)(2) of this Section, all
    quantities of that acute hazardous waste are subject to full regulation under 35 Ill.
    Adm. Code 702, 703, 722 through 726, and 728, and the notification requirements
    of section 3010 of the Resource Conservation and Recovery Act.
     
    1) A total of one kilogram of one or more of the acute hazardous wastes
    listed in Section 721.131, 721.132, or 721.133(e); or
     
    2) A total of 100 kilograms of any residue or contaminated soil, waste, or
    other debris resulting from the clean-up of a spill, into or on any land or
    water, of any one or more of the acute hazardous wastes listed in Section
    721.131, 721.132, or 721.133(e).
     
    BOARD NOTE: “Full regulation” means those regulations applicable to
    generators of greater than 1000 1,000 kg of non-acute hazardous waste in a
    calendar month.
     
    f) In order for acute hazardous wastes generated by a generator of acute hazardous
    wastes in quantities equal to or less than those set forth in subsection (e)(1) or
    (e)(2) of this Section to be excluded from full regulation under this Section, the
    generator must comply with the following requirements:
     
    1) 35 Ill. Adm. Code 722.111.

     
    156
     
    2) The generator may accumulate acute hazardous waste on-site. If the
    generator accumulates at any time acute hazardous wastes in quantities
    greater than set forth in subsection (e)(1) or (e)(2) of this Section, all of
    those accumulated wastes are subject to regulation under 35 Ill. Adm.
    Code 702, 703, 722 through 726, and 728, and the applicable notification
    requirements of section 3010 of the Resource Conservation and Recovery
    Act. The time period of 35 Ill. Adm. Code 722.134(a), for accumulation
    of wastes on-site, begins when the accumulated wastes exceed the
    applicable exclusion limit.
     
    3) A conditionally exempt small quantity generator may either treat or
    dispose of its acute hazardous waste in an on-site facility or ensure
    delivery to an off-site treatment, storage, or disposal facility, any of
    which, if located in the United States, meets any of the following
    conditions:
     
    A) The facility is permitted under 35 Ill. Adm. Code 702 and 703;
     
    B) The facility has interim status under 35 Ill. Adm. Code 702, 703,
    and 725;
     
    C) The facility is authorized to manage hazardous waste by a state
    with a hazardous waste management program approved by USEPA
    pursuant to 40 CFR 271;
     
    D) The facility is permitted, licensed, or registered by a state to
    manage municipal solid waste and, if managed in a municipal solid
    waste landfill facility, the landfill is subject to 35 Ill. Adm. Code
    810 through 814 or federal 40 CFR 258;
     
    E) The facility is permitted, licensed, or registered by a state to
    manage non-municipal non-hazardous waste and, if managed in a
    non-municipal non-hazardous waste disposal unit, the unit is
    subject to the requirements of federal 40 CFR 257.5 through
    257.30;
     
    BOARD NOTE: The Illinois non-hazardous waste landfill
    regulations, 35 Ill. Adm. Code 810 through 814, do not allow the
    disposal of hazardous waste in a landfill regulated under those
    rules. The Board intends that subsections (f)(3)(D) and (f)(3)(E)
    of this Section impose a federal requirement on the hazardous
    waste generator. The Board specifically does not intend that these
    subsections authorize any disposal of conditionally-exempt small
    quantity generator waste in a landfill not specifically permitted to
    accept the particular hazardous waste.

     
    157
     
    F) The facility is one that fulfills one of the following conditions:
     
    i) It beneficially uses or reuses or legitimately recycles or
    reclaims its waste; or
     
    ii) It treats its waste prior to beneficial use or reuse or
    legitimate recycling or reclamation; or
     
    G) For universal waste managed under 35 Ill. Adm. Code 733 or
    federal 40 CFR 273, the facility is a universal waste handler or
    destination facility subject to the requirements of 35 Ill. Adm.
    Code 733 or federal 40 CFR 273.
     
    g) In order for hazardous waste generated by a conditionally exempt small quantity
    generator in quantities of less than 100 kilograms of hazardous waste during a
    calendar month to be excluded from full regulation under this Section, the
    generator must comply with the following requirements:
     
    1) 35 Ill. Adm. Code 722.111;
     
    2) The conditionally exempt small quantity generator may accumulate
    hazardous waste on-site. If it accumulates at any time more than a total of
    1000 1,000 kilograms of the generator’s hazardous waste, all of those
    accumulated wastes are subject to regulation under the special provisions
    of 35 Ill. Adm. Code 722 applicable to generators of between 100 kg and
    1000 1,000 kg of hazardous waste in a calendar month, as well as the
    requirements of 35 Ill. Adm. Code 702, 703, 723 through 726, and 728,
    and the applicable notification requirements of Section 3010 of the
    Resource Conservation and Recovery Act. The time period of 35 Ill.
    Adm. Code 722.134(d) for accumulation of wastes on-site begins for a
    small quantity generator when the accumulated wastes exceed 1000 1,000
    kilograms;
     
    3) A conditionally exempt small quantity generator may either treat or
    dispose of its hazardous waste in an on-site facility or ensure delivery to
    an off-site treatment, storage, or disposal facility, any of which, if located
    in the United States, meets any of the following conditions:
     
    A) The facility is permitted under 35 Ill. Adm. Code 702 and 703;
     
    B) The facility has interim status under 35 Ill. Adm. Code 702, 703,
    and 725;
     
    C) The facility is authorized to manage hazardous waste by a state
    with a hazardous waste management program approved by USEPA

     
    158
    under pursuant to 40 CFR 271 (2002);
     
    D) The facility is permitted, licensed, or registered by a state to
    manage municipal solid waste and, if managed in a municipal solid
    waste landfill facility, the landfill is subject to 35 Ill. Adm. Code
    810 through 814 or federal 40 CFR 258;
     
    E) The facility is permitted, licensed, or registered by a state to
    manage non-municipal non-hazardous waste and, if managed in a
    non-municipal non-hazardous waste disposal unit, the unit is
    subject to the requirements of federal 40 CFR 257.5 through
    257.30;
     
    BOARD NOTE: The Illinois non-hazardous waste landfill
    regulations, 35 Ill. Adm. Code 810 through 814, do not allow the
    disposal of hazardous waste in a landfill regulated under those
    rules. The Board intends that subsections (g)(3)(D) and (g)(3)(E)
    of this Section impose a federal requirement on the hazardous
    waste generator. The Board specifically does not intend that these
    subsections authorize any disposal of conditionally-exempt small
    quantity generator waste in a landfill not specifically permitted to
    accept the particular hazardous waste.
     
    F) The facility is one that fulfills the following conditions:
     
    i) It beneficially uses or re-uses, or legitimately recycles or
    reclaims the small quantity generator’s waste; or
     
    ii) It treats its waste prior to beneficial use or re-use or
    legitimate recycling or reclamation; or
     
    G) For universal waste managed under 35 Ill. Adm. Code 733 or
    federal 40 CFR 273, the facility is a universal waste handler or
    destination facility subject to the requirements of 35 Ill. Adm.
    Code 733 or federal 40 CFR 273.
     
    h) Hazardous waste subject to the reduced requirements of this Section may be
    mixed with non-hazardous waste and remain subject to these reduced
    requirements even though the resultant mixture exceeds the quantity limitations
    identified in this Section, unless the mixture meets any of the characteristics of
    hazardous wastes identified in Subpart C of this Part.
     
    i) If a small quantity generator mixes a solid waste with a hazardous waste that
    exceeds a quantity exclusion level of this Section, the mixture is subject to full
    regulation.
     

     
    159
    j) If a conditionally exempt small quantity generator’s hazardous wastes are mixed
    with used oil, the mixture is subject to 35 Ill. Adm. Code 739. Any material
    produced from such a mixture by processing, blending, or other treatment is also
    so regulated.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.107 Residues of Hazardous Waste in Empty Containers
     
    a) Applicability of rules.
     
    1) Any hazardous waste remaining in either an empty container or an inner
    liner removed from an empty container, as defined in subsection (b), is not
    subject to regulation under 35 Ill. Adm. Code 702, 703, 721 through 725,
    or 728, or to the notification requirements of Section 3010 of the Resource
    Conservation and Recovery Act.
     
    2) Any hazardous waste in either a container that is not empty or an inner
    liner that is removed from a container that is not empty, as defined in
    subsection (b), is subject to regulations under 35 Ill. Adm. Code 702, 703,
    721 through 725, and 728 and to the notification requirements of Section
    3010 of the Resource Conservation and Recovery Act.
     
    b) Definition of “empty”:
     
    1) A container or an inner liner removed from a container that has held any
    hazardous waste, except a waste that is a compressed gas or that is
    identified as an acute hazardous waste listed in Sections 721.131, 721.132,
    or 721.133(e), is empty if the conditions of subsections (b)(1)(A) and
    (b)(1)(B) of this Section exist, subject to the limitations of subsection
    (b)(1)(C) of this Section:
     
    A) All wastes have been removed that can be removed using the
    practices commonly employed to remove materials from that type
    of container, e.g., pouring, pumping, and aspirating, and
     
    B) No more than 2.5 centimeters (one inch) of residue remain on the
    bottom of the container or inner liner, or
     
    C) Weight limits.
     
    i) No more than three percent by weight of the total capacity
    of the container remains in the container or inner liner if
    the container is less than or equal to 110 gallons in size,
    until September 5, 2006, or 119 gallons in size, effective
    September 5, 2006; or

     
    160
     
    ii) No more than 0.3 percent by weight of the total capacity of
    the container remains in the container or inner liner if the
    container is greater than 110 119 gallons in size, until
    September 5, 2006, or 119 gallons in size, effective
    September 5, 2006.
     
    2) A container that has held a hazardous waste that is a compressed gas is
    empty when the pressure in the container approaches ambient atmospheric
    pressure.
     
    3) A container or an inner liner removed from a container that has held an
    acute hazardous waste listed in Sections 721.131, 721.132, or 721.133(e)
    is empty if any of the following occurs:
     
    A) The container or inner liner has been triple rinsed using a solvent
    capable of removing the commercial chemical product or
    manufacturing chemical intermediate;
     
    B) The container or inner liner has been cleaned by another method
    that has been shown in the scientific literature, or by tests
    conducted by the generator, to achieve equivalent removal; or
     
    C) In the case of a container, the inner liner that prevented contact of
    the commercial chemical product or manufacturing chemical
    intermediate with the container has been removed.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.108 PCB Wastes Regulated under TSCA
     
    Polychlorinatedbiphenyl-(PCB-)containing dielectric fluid and electric equipment containing
    such fluid that are authorized for use and regulated under 40 CFR 761 and which are hazardous
    only because they fail the test for toxicity characteristic (hazardous waste codes D018 through
    D043 only), are exempt from regulation under 35 Ill. Adm. Code 702, 703, 721 through 725, and
    728, and from the notification requirements of Section 3010 of the Resource Conservation and
    Recovery Act. if the following conditions are fulfilled with regard to the fluid:
     
    a) The fluid is authorized for use and regulated under pursuant to federal 40 CFR
    761; and
     
    b) The fluid is hazardous only because it fails the test for toxicity characteristic
    (hazardous waste codes D018 through D043 only).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    161
    SUBPART B: CRITERIA FOR IDENTIFYING THE CHARACTERISTICS OF
    HAZARDOUS WASTE AND FOR LISTING HAZARDOUS WASTES
     
    Section 721.110 Criteria for Identifying the Characteristics of Hazardous Waste
     
    a) USEPA stated in corresponding federal 40 CFR 261.10 that it identifies and
    defines a characteristic of hazardous waste in Subpart C of this Part only upon
    determining the following:
     
    1) That a solid waste that exhibits the characteristic may do either of the
    following:
     
    A) It could cause, or significantly contribute to, an increase in
    mortality or an increase in serious irreversible, or incapacitating
    reversible, illness; or
     
    B) It could pose a substantial present or potential hazard to human
    health or the environment when it is improperly treated, stored,
    transported, disposed of or otherwise managed; and
     
    2) That the characteristic can be as follows:
     
    A) It can be measured by an available standardized test method that is
    reasonable within the capability of generators of solid waste or
    private sector laboratories that are available to serve generators of
    solid waste; or
     
    B) It can reasonably be detected by generators of solid waste through
    their knowledge of their waste.
     
    b) Delisting procedures are contained in 35 Ill. Adm. Code 720.122.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.111 Criteria for Listing Hazardous Waste
     
    a) USEPA stated in corresponding federal 40 CFR 261.11 that it lists a solid waste
    as a hazardous waste only upon determining that the solid waste meets one of the
    following criteria:
     
    1) The solid waste exhibits any of the characteristics of hazardous waste
    identified in Subpart C of this Part; or
     
    2) Acute hazardous waste. The solid waste has been found to be fatal to
    humans in low doses or, in the absence of data on human toxicity, it has
    been shown in studies to have an oral LD 50 toxicity (rat) of less than 50

     
    162
    mg/kg, an inhalation LC 50 toxicity (rat) of less than 2 mg/Lmg/
    , or a
    dermal LD 50 toxicity (rabbit) of less than 200 mg/kg or is otherwise
    capable of causing or significantly contributing to an increase in serious
    irreversible or incapacitating reversible, illness.
     
    BOARD NOTE: Waste listed in accordance with these criteria are
    designated Acute Hazardous Waste.
     
    3) Toxic waste. The solid waste contains any of the toxic constituents listed
    in Appendix H of this Part and, after considering the following factors,
    USEPA concludes that the waste is capable of posing a substantial present
    or potential hazard to human health or the environment when improperly
    treated, stored, transported, or disposed of, or otherwise managed:
     
    BOARD NOTE: Substances are listed in Appendix H of this Part only if
    they have been shown in scientific studies to have toxic, carcinogenic,
    mutagenic, or teratogenic effects on humans or other life forms.
     
    A) The nature of the toxicity presented by the constituent;
     
    B) The concentration of the constituent in the waste;
     
    C) The potential of the constituent or any toxic degradation product of
    the constituent to migrate from the waste into the environment
    under the types of improper management considered in subsection
    (a)(3)(G) of this Section;
     
    D) The persistence of the constituent or any toxic degradation product
    of the constituent;
     
    E) The potential for the constituent or any toxic degradation product
    of the constituent to degrade into nonharmful constituents and the
    rate of degradation;
     
    F) The degree to which the constituent or any degradation product of
    the constituent bioaccumulates in ecosystems;
     
    G) The plausible types of improper management to which the waste
    could be subjected;
     
    H) The quantities of the waste generated at individual generation sites
    or on a regional or national basis;
     
    I) The nature and severity of the human health and environmental
    damage that has occurred as a result of the improper management
    of the wastes containing the constituent;

     
    163
     
    J) Action taken by other governmental agencies or regulatory
    programs based on the health or environmental hazard posed by
    the waste or waste constituent; and
     
    K) Such other factors as may be appropriate.
     
    BOARD NOTE: Wastes listed in accordance with these criteria are
    designated toxic wastes.
     
    b) USEPA stated in corresponding federal 40 CFR 261.11(b) that it may list classes
    or types of solid waste as hazardous waste if USEPA has reason to believe that
    individual wastes, within the class or type of waste, typically or frequently are
    hazardous under the definition of hazardous waste found in Section 1004(5) of the
    federal Resource Conservation and Recovery Act (42 USC 6904(5)).
     
    c) USEPA will use the criteria for listing specified in this Section to establish the
    exclusion limits referred to in Section 721.105(c).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART C: CHARACTERISTICS OF HAZARDOUS WASTE
     
    Section 721.121 Characteristic of Ignitability
     
    a) A solid waste exhibits the characteristic of ignitability if a representative sample
    of the waste has any of the following properties:
     
    1) It is a liquid, other than an aqueous solution containing less than 24
    percent alcohol by volume, and has a flash point less than 60°C (140°F),
    as determined by a Pensky-Martens Closed Cup Tester, using the test
    method specified in ASTM D-93D 93-85 (Standard Test Methods for
    Flash Point by Pensky-Martens Closed Tester), incorporated by reference
    in 35 Ill. Adm. Code 720.111, or a Setaflash Closed Cup Tester, using the
    test method specified in ASTM Standard D-3828 D 3828-87, (Standard
    Test Methods for Flash Point of Liquids by Setaflash Closed Tester), each
    incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(a), or as
    determined by an equivalent test method approved by the Board (35 Ill.
    Adm. Code 720.120).
     
    2) It is not a liquid and is capable, under standard temperature and pressure,
    of causing fire through friction, absorption of moisture, or spontaneous
    chemical changes and, when ignited, burns so vigorously and persistently
    that it creates a hazard.
     
    3) It is an ignitable compressed a flammable gas, as defined in federal 49

     
    164
    CFR 173.300 173.115 (Class 2, Divisions 2.1, 2.2, and 2.3--Definitions),
    incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(b), and
    as determined by the test methods described in that regulation or
    equivalent test methods approved by the Board (35 Ill. Adm. Code
    720.120).
     
    BOARD NOTE: Corresponding 40 CFR 261.21(a)(3) cites to 49 CFR
    173.300 for a definition of “ignitable compressed gas.” That provision has
    been removed by USDOT, and it is marked “reserved.” 49 CFR 173.115
    now defines a “flammable gas” as a Division 2.1 material. The Board has
    updated the Illinois provision to correspond with the current USDOT
    regulations.
     
    4) It is an oxidizer, as defined in federal 49 CFR 173.151 173.127 (Class 5,
    Division 5.1--Definition and Assignment of Packaging Groups),
    incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(b).
     
    BOARD NOTE: Corresponding 40 CFR 261.21 cites to 49 CFR 173.151
    for a definition of “oxidizer.” 49 CFR 173.127 classifies an oxidizer as a
    Division 5.1 material. The Board has updated the Illinois provision to
    correspond with the current USDOT regulations.
     
    b) A solid waste that exhibits the characteristic of ignitability has the USEPA
    hazardous waste number of D001.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.122 Characteristic of Corrosivity
     
    a) A solid waste exhibits the characteristic of corrosivity if a representative sample
    of the waste has either of the following properties:
     
    1) It is aqueous and has a pH less than or equal to 2 or greater than or equal
    to 12.5, as determined by a pH meter using Method 9040 9040C (pH
    Electrometric Measurement) in “Test Methods for the Evaluation of Solid
    Waste, Physical/Chemical Methods,” USEPA publication number EPA-
    530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(a).
     
    2) It is a liquid and corrodes steel (SAE 1020) at a rate greater than 6.35 mm
    (0.250 inch) per year at a test temperature of 55° C (130° F), as
    determined by the test method specified in NACE (National Association
    of Corrosion Engineers) Standard TM-01-69 as standardized in Method
    1110A (Corrosivity Toward Steel) in “Test Methods for the Evaluation of
    Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code

     
    165
    720.111 720.111(a).
     
    BOARD NOTE: The corrosivity characteristic determination currently
    does not apply to non-liquid wastes, as discussed by USEPA at 45 Fed.
    Reg. 33109, May 19, 1980 and at 55 Fed. Reg. 22549, June 1, 1990.
     
    b) A solid waste that exhibits the characteristic of corrosivity has the USEPA
    hazardous waste number of D002.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.123 Characteristic of Reactivity
     
    a) A solid waste exhibits the characteristic of reactivity if a representative sample of
    the waste has any of the following properties:
     
    1) It is normally unstable and readily undergoes violent change without
    detonating.
     
    2) It reacts violently with water.
     
    3) It forms potentially explosive mixtures with water.
     
    4) When mixed with water, it generates toxic gases, vapors, or fumes in a
    quantity sufficient to present a danger to human health or the environment.
     
    5) It is a cyanide or sulfide bearing waste which, when exposed to pH
    conditions between 2 and 12.5 can generate toxic gases, vapors, or fumes
    in a quantity sufficient to present a danger to human health or the
    environment.
     
    6) It is capable of detonation or explosive reaction if it is subjected to a
    strong initiating source or if heated under confinement.
     
    7) It is readily capable of detonation or explosive decomposition or reaction
    at standard temperature and pressure.
     
    8) It is a forbidden explosive, as defined in federal 49 CFR 173.51, 173.54
    (Forbidden Explosives) or a Class A Division 1.1, 1.2, or 1.3 explosive, as
    defined in 49 CFR 173.53 173.50 (Class 1--Definitions), or a Class B
    explosive, as defined in 49 CFR 173.88, each incorporated by reference in
    35 Ill. Adm. Code 720.111 720.111(b).
     
    BOARD NOTE: Corresponding 40 CFR 261.23 cites to 49 CFR 173.51
    for a definition of “forbidden explosive,” to 49 CFR 173.53 for a
    definition of “Class A explosive,” and to 49 CFR 173.88 for a definition

     
    166
    of “Class B explosive.” 49 CFR 173.54 now sets forth the definition of
    “forbidden explosive,” and 49 CFR 173.53 explains that what were once
    Class A explosives and Class B explosives are now classified as Division
    1.1, Division 1.2, and Division 1.2 materials. The Board has updated the
    Illinois provision to correspond with the current USDOT regulations.
     
    b) A solid waste that exhibits the characteristic of reactivity has the USEPA
    hazardous waste number of D003.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.124 Toxicity Characteristic
     
    a) A solid waste (except manufactured gas plant waste) exhibits the characteristic of
    toxicity if, using the Toxicity Characteristic Leaching Procedure (TCLP), test
    Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test
    Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    Publication publication number EPA-530/SW-846, as incorporated by reference
    in 35 Ill. Adm. Code 720.111 720.111(a), the extract from a representative sample
    of the waste contains any of the contaminants listed in the table in subsection (b)
    of this Section at a concentration equal to or greater than the respective value
    given in that table. Where the waste contains less than 0.5 percent filterable
    solids, the waste itself, after filtering using the methodology outlined in Method
    1311, is considered to be the extract for the purpose of this Section.
     
    BOARD NOTE: The reference to the “EP toxicity test” in 35 Ill. Adm. Code
    808.410(b)(4) is to be understood as referencing the test required by this Section.
     
    b) A solid waste that exhibits the characteristic of toxicity has the USEPA hazardous
    waste number specified in the following table that corresponds to the toxic
    contaminant causing it to be hazardous.
     
    MAXIMUM CONCENTRATION OF CONTAMINANTS FOR
    THE TOXICITY CHARACTERISTIC
     
    USEPA
    Hazardous
    Waste No. Contaminant CAS Number Note
    Regulatory
    Level
    (mg/Lmg/
    )
     
    D004 Arsenic 7440-38-2 5.0
    D005 Barium 7440-39-3 100.0
    D018 Benzene 71-43-2 0.5
    D006 Cadmium 7440-43-9 1.0
    D019 Carbon tetrachloride 56-23-5 0.5
    D020 Chlordane 57-74-9 0.03
    D021 Chlorobenzene 108-90-7 100.0

     
    167
    D022 Chloroform 67-66-3 6.0
    D007 Chromium 7440-47-3 5.0
    D023 o-Cresol 95-48-7 2 200.0
    D024 m-Cresol 108-39-4 2 200.0
    D025 p-Cresol 106-44-5 2 200.0
    D026 Cresol 2 200.0
    D016 2,4-D 94-75-7 10.0
    D027 1,4-Dichlorobenzene 106-46-7 7.5
    D028 1,2-Dichloroethane 107-06-2 0.5
    D029 1,1-Dichloroethylene 75-35-4 0.7
    D030 2,4-Dinitrotoluene 121-14-2 1 0.13
    D012 Endrin 72-20-8 0.02
    D031 Heptachlor (and its
    epoxide)
    76-44-8 0.008
    D032 Hexachlorobenzene 118-74-1 1 0.13
    D033 Hexachlorobutadiene 87-68-3 0.5
    D034 Hexachloroethane 67-72-1 3.0
    D008 Lead 7439-92-1 5.0
    D013 Lindane 58-89-9 0.4
    D009 Mercury 7439-97-6 0.2
    D014 Methoxychlor 72-43-5 10.0
    D035 Methyl ethyl ketone 78-93-3 200.0
    D036 Nitrobenzene 98-95-3 2.0
    D037 Pentachlorophenol 87-86-5 100.0
    D038 Pyridine 110-86-1 1 5.0
    D010 Selenium 7782-49-2 1.0
    D011 Silver 7440-22-4 5.0
    D039 Tetrachloroethylene 127-18-4 0.7
    D015 Toxaphene 8001-35-2 0.5
    D040 Trichloroethylene 79-01-6 0.5
    D041 2,4,5-Trichlorophenol 95-95-4 400.0
    D042 2,4,6-Trichlorophenol 88-06-2 2.0
    D017 2,4,5-TP (Silvex) 93-72-1 1.0
    D043 Vinyl chloride 75-01-4 0.2
     
    Notes to Table:
     
    1 Quantitation limit is greater than the calculated regulatory level. The
    quantitation limit therefore becomes the regulatory level.
     
    2 If o-, m-, p-cresol concentrations cannot be differentiated, the total cresol
    (D026) concentration is used. The regulatory level of total cresol is 200.0
    mg/Lmg/
    .
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    168
    SUBPART D: LISTS OF HAZARDOUS WASTE
     
    Section 721.130 General
     
    a) A solid waste is a hazardous waste if it is listed in this Subpart D, unless it has
    been excluded from this list under pursuant to 35 Ill. Adm. Code 720.120 and
    720.122.
     
    b) The basis for listing the classes or types of wastes listed in this Subpart D is
    indicated by employing one or more of the following hazard codes:
     
    1) Hazard Codes.
     
    A) Ignitable waste (I)
     
    B) Corrosive waste (C)
     
    C) Reactive waste (R)
     
    D) Toxicity Characteristic waste (E)
     
    E) Acute hazardous waste (H)
     
    F) Toxic waste (T)
     
    2) Appendix G of this Part identifies the constituent that caused the
    Administrator to list the waste as a toxicity characteristic waste (E) or
    toxic waste (T) in Sections 721.131 and 721.132.
     
    c) Each hazardous waste listed in this Subpart D is assigned a USEPA hazardous
    waste number that precedes the name of the waste. This number must be used in
    complying with the federal notification requirements of Section section 3010 of
    RCRA (42 USC 6910) and certain recordkeeping and reporting requirements
    under 35 Ill. Adm. Code 702, 703, 722 through 725, and 728 and federal 40 CFR
    122.
     
    d) The following hazardous wastes listed in Section 721.131 or 721.132 are subject
    to the exclusion limits for acute hazardous wastes established in Section 721.105:
    hazardous wastes numbers F020, F021, F022, F023, F026, and F027.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.132 Hazardous Waste from Specific Sources
     
    a)
    The following solid wastes are listed hazardous wastes from specific sources
    unless they are excluded under 35 Ill. Adm. Code 720.120 and 720.122 and listed

     
    169
    in Appendix I of this Part.
     
    USEPA
    Hazardous
    Waste No. Industry and Hazardous Waste
    Hazard
    Code
     
    Wood Preservation Process Wastes:
     
    K001 Bottom sediment sludge from the treatment of
    wastewaters from wood preserving processes that use
    creosote or pentachlorophenol.
    (T)
     
    Inorganic Pigments Production Wastes:
     
    K002 Wastewater treatment sludge from the production of
    chrome yellow and orange pigments.
    (T)
     
    K003 Wastewater treatment sludge from the production of
    molybdate orange pigments.
    (T)
     
    K004 Wastewater treatment sludge from the production of zinc
    yellow pigments.
    (T)
     
    K005 Wastewater treatment sludge from the production of
    chrome green pigments.
    (T)
     
    K006 Wastewater treatment sludge from the production of
    chrome oxide green pigments (anhydrous and hydrated).
    (T)
     
    K007 Wastewater treatment sludge from the production of iron
    blue pigments.
    (T)
     
    K008 Oven residue from the production of chrome oxide green
    pigments.
    (T)
     
    Organic Chemicals Production Wastes:
     
    K009 Distillation bottoms from the production of acetaldehyde
    from ethylene.
    (T)
     
    K010 Distillation side cuts from the production of acetaldehyde
    from ethylene.
    (T)
     
    K011 Bottom stream from the wastewater stripper in the
    production of acrylonitrile.
    (R, T)
     

     
    170
    K013 Bottom stream from the acetonitrile column in the
    production of acrylonitrile.
    (T)
     
    K014 Bottoms from the acetonitrile purification column in the
    production of acrylonitrile.
    (T)
     
    K015 Still bottoms from the distillation of benzyl chloride. (T)
     
    K016 Heavy ends or distillation residues from the production
    of carbon tetrachloride.
    (T)
     
    K017 Heavy ends (still bottoms) from the purification column
    in the production of epichlorohydrin.
    (T)
     
    K018 Heavy ends from the fractionation column in ethyl
    chloride production.
    (T)
     
    K019 Heavy ends from the distillation of ethylene dichloride in
    ethylene dichloride production.
    (T)
     
    K020 Heavy ends from the distillation of vinyl chloride in
    vinyl chloride monomer production.
    (T)
     
    K021 Aqueous spent antimony catalyst waste from
    fluoromethanes production.
    (T)
     
    K022 Distillation bottom tars from the production of
    phenol/acetone from cumene.
    (T)
     
    K023 Distillation light ends from the production of phthalic
    anhydride from naphthalene.
    (T)
     
    K024 Distillation bottoms from the production of phthalic
    anhydride from naphthalene.
    (T)
     
    K093 Distillation light ends from the production of phthalic
    anhydride from ortho-xylene.
    (T)
     
    K094 Distillation bottoms from the production of phthalic
    anhydride from ortho-xylene.
    (T)
     
    K025 Distillation bottoms from the production of nitrobenzene
    by the nitration of benzene.
    (T)
     
    K026 Stripping still tails from the production of methyl ethyl
    pyridines.
    (T)

     
    171
     
    K027 Centrifuge and distillation residues from toluene di-
    isocyanate production.
    (R, T)
     
    K028 Spent catalyst from the hydrochlorinator reactor in the
    production of 1,1,1-trichloroethane.
    (T)
     
    K029 Waste from the product stream stripper in the production
    of 1,1,1-trichloroethane.
    (T)
     
    K095 Distillation bottoms from the production of 1,1,1-tri-
    chloroethane.
    (T)
     
    K096 Heavy ends from the heavy ends column from the
    production of 1,1,1-trichloroethane.
    (T)
     
    K030 Column bottoms or heavy ends from the combined
    production of trichloroethylene and perchloroethylene.
    (T)
     
    K083 Distillation bottoms from aniline production. (T)
     
    K103 Process residues from aniline extraction from the
    production of aniline.
    (T)
     
    K104 Combined wastewater streams generated from
    nitrobenzene/aniline production.
    (T)
     
    K085 Distillation or fractionation column bottoms from the
    production of chlorobenzenes.
    (T)
     
    K105 Separated aqueous stream from the reactor product
    washing step in the production of chlorobenzenes.
    (T)
     
    K107 Column bottoms from product separation from the
    production of 1,1-dimethylhydrazine (UDMH) from
    carboxylic acid hydrazides.
    (C, T)
     
    K108 Condensed column overheads from product separation
    and condensed reactor vent gases from the production of
    1,1-dimethylhydrazine (UDMH) from carboxylic acid
    hydrazides.
    (I, T)
     
    K109 Spent filter cartridges from the product purification from
    the production of 1,1-dimethylhydrazine (UDMH) from
    carboxylic acid hydrazides.
    (T)
     

     
    172
    K110 Condensed column overheads from intermediate
    separation from the production of 1,1-dimethylhydrazine
    (UDMH) from carboxylic acid hydrazides.
    (T)
     
    K111 Product wastewaters from the production of di-
    nitrotoluene via nitration of toluene.
    (C, T)
     
    K112 Reaction by-product water from the drying column in the
    production of toluenediamine via hydrogenation of di-
    nitrotoluene.
    (T)
     
    K113 Condensed liquid light ends from the purification of
    toluenediamine in the production of toluenediamine via
    hydrogenation of dinitrotoluene.
    (T)
     
    K114 Vicinals from the purification of toluenediamine in the
    production of toluenediamine via hydrogenation of
    dinitrotoluene.
    (T)
     
    K115 Heavy ends from the purification of toluenediamine in
    the production of toluenediamine via hydrogenation of
    dinitrotoluene.
    (T)
     
    K116 Organic condensate from the solvent recovery column in
    the production of toluene diisocyanate via phosgenation
    of toluenediamine.
    (T)
     
    K117 Wastewater from the reactor vent gas scrubber in the
    production of ethylene dibromide via bromination of
    ethene.
    (T)
     
    K118 Spent adsorbent solids from purification of ethylene di-
    bromide in the production of ethylene dibromide via
    bromination of ethene.
    (T)
     
    K136 Still bottoms from the purification of ethylene dibromide
    in the production of ethylene dibromide via bromination
    of ethene.
    (T)
     
    K156 Organic waste (including heavy ends, still bottoms, light
    ends, spent solvents, filtrates, and decantates) from the
    production of carbamates and carbamoyl oximes. (This
    listing does not apply to wastes generated from the
    manufacture of 3-iodo-2-propynyl n-butylcarbamate.)
    (T)
     

     
    173
    K157 Wastewaters (including scrubber waters, condenser
    waters, washwaters, and separation waters) from the
    production of carbamates and carbamoyl oximes. (This
    listing does not apply to wastes generated from the
    manufacture of 3-iodo-2-propynyl n-butylcarbamate.)
    (T)
     
    K158 Baghouse dusts and filter/separation solids from the
    production of carbamates and carbamoyl oximes. (This
    listing does not apply to wastes generated from the
    manufacture of 3-iodo-2-propynyl n-butylcarbamate.)
    (T)
     
    K159 Organics from the treatment of thiocarbamate wastes. (T)
     
    K161 Purification solids (including filtration, evaporation, and
    centrifugation solids), bag house dust and floor
    sweepings from the production of dithiocarbamate acids
    and their salts. (This listing does not include K125 or
    K126.)
    (R, T)
     
    K174 Wastewater treatment sludges from the production of
    ethylene dichloride or vinyl chloride monomer (including
    sludges that result from commingled ethylene dichloride
    or vinyl chloride monomer wastewater and other
    wastewater), unless the sludges meet the following
    conditions: (1) the sludges are disposed of in a RCRA
    Subtitle C (42 USC 6921-6939e) or non-hazardous
    landfill licensed or permitted by a state or the federal
    government; (2) the sludges are not otherwise placed on
    the land prior to final disposal; and (3) the generator
    maintains documentation demonstrating that the waste
    was either disposed of in an on-site landfill or consigned
    to a transporter or disposal facility that provided a
    written commitment to dispose of the waste in an off-site
    landfill. Upon a showing by the government that a
    respondent in any enforcement action brought to enforce
    the requirements of Subtitle C of this Part managed
    wastewater treatment sludges from the production of
    vinyl chloride monomer or ethylene dichloride, the
    respondent must demonstrate that it meets the conditions
    of the exclusion that are set forth above. In doing so, the
    respondent must provide appropriate documentation that
    the terms of the exclusion were met (e.g., contracts
    between the generator and the landfill owner or operator,
    invoices documenting delivery of waste to landfill, etc.).
    (T)
     

     
    174
    K175 Wastewater treatment sludges from the production of
    vinyl chloride monomer using mercuric chloride catalyst
    in an acetylene-based process.
    (T)
     
    Inorganic Chemicals Production Wastes:
     
    K071 Brine purification muds from the mercury cell process in
    chlorine production, where separately prepurified brine is
    not used.
    (T)
     
    K073 Chlorinated hydrocarbon waste from the purification step
    of the diaphragm cell process using graphite anodes in
    chlorine production.
    (T)
     
    K106 Wastewater treatment sludge from the mercury cell
    process in chlorine production.
    (T)
     
    K176 Baghouse filters from the production of antimony oxide,
    including filters from the production of intermediates
    (e.g., antimony metal or crude antimony oxide).
    (E)
     
    K177 Slag from the production of antimony oxide that is
    speculatively accumulated or disposed of, including slag
    from the production of intermediates (e.g., antimony
    metal or crude antimony oxide).
    (T)
     
    K178 Residues from manufacturing and manufacturing-site
    storage of ferric chloride from acids formed during the
    production of titanium dioxide using the chloride-
    ilmenite process.
    (T)
     
    K181 Nonwastewaters from the production of dyes or pigments
    (including nonwastewaters commingled at the point of
    generation with nonwastewaters from other processes)
    that, at the point of generation, contain mass loadings of
    any of the constituents identified in subsection (c) of this
    Section that are equal to or greater than the corresponding
    subsection (c) levels, as determined on a calendar year
    basis. These wastes will not be hazardous if the
    nonwastewaters are managed in one of the following
    ways:
     
    1) They are disposed in a municipal solid waste landfill
    unit that is subject to the design criteria in 35 Ill.
    Adm. Code 811.303 through 811.309 and 811.315
    through 811.317 and Subpart E of 35 Ill. Adm. Code
    (T)

     
    175
    811 or 35 Ill. Adm. Code 814.302 and 814.402;
     
    2) They are disposed in a hazardous waste landfill unit
    that is subject to either 35 Ill. Adm. Code 724.401 or
    725.401;
     
    3) They are disposed in other municipal solid waste
    landfill units that meet the design criteria in 35 Ill.
    Adm. Code 811.303 through 811.309 and 811.315
    through 811.317 and Subpart E of 35 Ill. Adm. Code
    811 or 35 Ill. Adm. Code 814.302 and 814.402, 35
    Ill. Adm. Code 724.401, or 35 Ill. Adm. Code
    725.401; or
     
    4) They are treated in a combustion unit that is
    permitted under 415 ILCS 5/39(d), or an onsite
    combustion unit that is permitted under 415 ILCS
    5/39.5.
     
    For the purposes of this listing, dyes or pigments
    production is defined in subsection (b)(1) of this Section.
    Subsection (d) of this Section describes the process for
    demonstrating that a facility’s nonwastewaters are not
    K181 waste. This listing does not apply to wastes that are
    otherwise identified as hazardous under Sections 721.121
    through 721.124 and 721.131 through 721.133 at the
    point of generation. Also, the listing does not apply to
    wastes generated before any annual mass loading limit is
    met, as set forth in subsection (c) of this Section.
     
    Pesticides Production Wastes:
     
    K031 By-product salts generated in the production of MSMA
    and cacodylic acid.
    (T)
     
    K032 Wastewater treatment sludge from the production of
    chlordane.
    (T)
     
    K033 Wastewater and scrub water from the chlorination of
    cyclopentadiene in the production of chlordane.
    (T)
     
    K034 Filter solids from the filtration of hexachlorocyclopenta-
    diene in the production of chlordane.
    (T)
     
    K097 Vacuum stripper discharge from the chlordane
    chlorinator in the production of chlordane.
    (T)

     
    176
     
    K035 Wastewater treatment sludges generated in the
    production of creosote.
    (T)
     
    K036 Still bottoms from toluene reclamation distillation in the
    production of disulfoton.
    (T)
     
    K037 Wastewater treatment sludges from the production of di-
    sulfoton.
    (T)
     
    K038 Wastewater from the washing and stripping of phorate
    production.
    (T)
     
    K039 Filter cake from the filtration of diethylphosphorodithioic
    acid in the production of phorate.
    (T)
     
    K040 Wastewater treatment sludge from the production of
    phorate.
    (T)
     
    K041 Wastewater treatment sludge from the production of
    toxaphene.
    (T)
     
    K098 Untreated process wastewater from the production of
    toxaphene.
    (T)
     
    K042 Heavy ends or distillation residues from the distillation
    of tetrachlorobenzene in the production of 2,4,5-T.
    (T)
     
    K043 2,6-Dichlorophenol waste from the production of 2,4-D. (T)
     
    K099 Untreated wastewater from the production of 2,4-D. (T)
     
    K123 Process wastewater (including supernates, filtrates, and
    washwaters) from the production of ethylenebisdi-
    thiocarbamic acid and its salts.
    (T)
     
    K124 Reactor vent scrubber water from the production of
    ethylenebisdithiocarbamic acid and its salts.
    (C, T)
     
    K125 Filtration, evaporation, and centrifugation solids from the
    production of ethylenebisdithiocarbamic acid and its
    salts.
    (T)
     
    K126 Baghouse dust and floor sweepings in milling and
    packaging operations from the production or formulation
    of ethylenebisdithiocarbamic acid and its salts.
    (T)

     
    177
     
    K131 Wastewater from the reactor and spent sulfuric acid from
    the acid dryer from the production of methyl bromide.
    (C, T)
     
    K132 Spent absorbent and wastewater separator solids from the
    production of methyl bromide.
    (T)
     
    Explosives Production Wastes:
     
    K044 Wastewater treatment sludges from the manufacturing
    and processing of explosives.
    (R)
     
    K045 Spent carbon from the treatment of wastewater
    containing explosives.
    (R)
     
    K046 Wastewater treatment sludges from the manufacturing,
    formulation and loading of lead-based initiating
    compounds.
    (T)
     
    K047 Pink/red water from TNT operations. (R)
     
    Petroleum Refining Wastes:
     
    K048 Dissolved air flotation (DAF) float from the petroleum
    refining industry.
    (T)
     
    K049 Slop oil emulsion solids from the petroleum refining
    industry.
    (T)
     
    K050 Heat exchanger bundle cleaning sludge from the
    petroleum refining industry.
    (T)
     
    K051 API separator sludge from the petroleum refining
    industry.
    (T)
     
    K052 Tank bottoms (leaded) from the petroleum refining
    industry.
    (T)
     
    K169 Crude oil storage tank sediment from petroleum refining
    operations.
    (T)
     
    K170 Clarified slurry oil tank sediment or in-line
    filter/separation solids from petroleum refining
    operations.
    (T)
     

     
    178
    K171 Spent hydrotreating catalyst from petroleum refining
    operations, including guard beds used to desulfurize
    feeds to other catalytic reactors (this listing does not
    include inert support media).
    (I, T)
     
    K172 Spent hydrorefining catalyst from petroleum refining
    operations, including guard beds used to desulfurize feeds
    to other catalytic reactors (this listing does not include
    inert support media).
    (I, T)
     
    Iron and Steel Production Wastes:
     
    K061 Emission control dust/sludge from the primary
    production of steel in electric furnaces.
    (T)
     
    K062 Spent pickle liquor generated by steel finishing
    operations of facilities within the iron and steel industry
    (SIC Codes 331 and 332) (as defined in 35 Ill. Adm.
    Code 720.110).
    (C, T)
     
    Primary Aluminum Production Wastes:
     
    K088 Spent potliners from primary aluminum reduction. (T)
     
    Secondary Lead Production Wastes:
     
    K069 Emission control dust/sludge from secondary lead
    smelting.
    (T)
     
    BOARD NOTE: This listing is administratively stayed for sludge generated
    from secondary acid scrubber systems. The stay will remain in effect until this
    note is removed.
     
    K100 Waste leaching solution from acid leaching of emission
    control dust/sludge from secondary lead smelting.
    (T)
     
    Veterinary Pharmaceuticals Production Wastes:
     
    K084 Wastewater treatment sludges generated during the
    production of veterinary pharmaceuticals from arsenic or
    organo-arsenic compounds.
    (T)
     
    K101 Distillation tar residues from the distillation of aniline-
    based compounds in the production of veterinary
    pharmaceuticals from arsenic or organo-arsenic
    compounds.
    (T)

     
    179
     
    K102 Residue from use of activated carbon for decolorization
    in the production of veterinary pharmaceuticals from
    arsenic or organo-arsenic compounds.
    (T)
     
    Ink Formulation Wastes:
     
    K086 Solvent washes and sludges, caustic washes and sludges,
    or water washes and sludges from cleaning tubs and
    equipment used in the formulation of ink from pigments,
    dryers, soaps and stabilizers containing chromium and
    lead.
    (T)
     
    Coke Production Wastes:
     
    K060 Ammonia still lime sludge from coking operations. (T)
     
    K087 Decanter tank tar sludge from coking operations. (T)
     
    K141 Process residues from the recovery of coal tar, including,
    but not limited to, collecting sump residues from the
    production of coke from coal or the recovery of coke by-
    products produced from coal. This listing does not
    include K087 (decanter tank tar sludges from coking
    operations).
    (T)
     
    K142 Tar storage tank residues from the production of coke
    from coal or from the recovery of coke by-products
    produced from coal.
    (T)
     
    K143 Process residues from the recovery of light oil, including,
    but not limited to, those generated in stills, decanters, and
    wash oil recovery units from the recovery of coke by-
    products produced from coal.
    (T)
     
    K144 Wastewater sump residues from light oil refining,
    including, but not limited to, intercepting or
    contamination sump sludges from the recovery of coke
    by-products produced from coal.
    (T)
     
    K145 Residues from naphthalene collection and recovery
    operations from the recovery of coke by-products
    produced from coal.
    (T)
     
    K147 Tar storage tank residues from coal tar refining. (T)
     

     
    180
    K148 Residues from coal tar distillation, including, but not
    limited to, still bottoms.
    (T)
     
    K149
    Distillation bottoms from the production of
    α
    - (or
    methyl-) chlorinated toluenes, ring-chlorinated toluenes,
    benzoyl chlorides, and compounds with mixtures of these
    functional groups. (This waste does not include still
    bottoms from the distillation of benzyl chloride.)
    (T)
     
    K150 Organic residuals, excluding spent carbon adsorbent,
    from the spent chlorine gas and hydrochloric acid
    recovery processes associated with the production of
    α
    -
    (or methyl-) chlorinated toluenes, ring-chlorinated
    toluenes, benzoyl chlorides, and compounds with
    mixtures of these functional groups.
    (T)
     
    K151 Wastewater treatment sludges, excluding neutralization
    and biological sludges, generated during the treatment of
    wastewaters from the production of
    α
    - (or methyl-)
    chlorinated toluenes, ring-chlorinated toluenes, benzoyl
    chlorides, and compounds with mixtures of these
    functional groups.
    (T)
     
    b) Listing-specific definition: For the purposes of the K181 hazardous waste listing
    in subsection (a) of this Section, “dyes or pigments production” includes
    manufacture of the following product classes: dyes, pigments, and FDA-certified
    colors that are in the azo, triarylmethane, perylene, and anthraquinone classes.
    Azo products include azo, monoazo, diazo, triazo, polyazo, azoic, benzidine, and
    pyrazolone products. Triarylmethane products include both triarylmethane and
    triphenylmethane products. Wastes that are not generated at a dyes or pigments
    manufacturing site, such as wastes from the offsite use, formulation, and
    packaging of dyes or pigments, are not included in the K181 listing.
     
    c) K181 listing levels. Nonwastewaters containing constituents in amounts equal to
    or exceeding the following levels during any calendar year are subject to the
    K181 hazardous waste listing in subsection (a) of this Section, unless the
    conditions in the K181 hazardous waste listing are met:
     
    Constituent Chemical abstracts No. Mass levels (kg/yr)
    Aniline 62–53–3 9,300
    o-Anisidine 90–04–0 110
    4-Chloroaniline 106–47–8 4,800
    p-Cresidine 120–71–8 660
    2,4-Dimethylaniline 95–68–1 100
    1,2-Phenylenediamine 95–54–5 710

     
    181
    1,3-Phenylenediamine 108–45–2 1,200
     
    d) Procedures for demonstrating that dyes or pigment nonwastewaters are not K181
    waste. The procedures described in subsections (d)(1) through (d)(3) and (d)(5)
    of this Section establish when nonwastewaters from the production of dyes or
    pigments would not be hazardous. (These procedures apply to wastes that are not
    disposed in landfill units or treated in combustion units, as specified in subsection
    (a) of this section). If the nonwastewaters are disposed in landfill units or treated
    in combustion units as described in subsection (a) of this Section, then the
    nonwastewaters are not hazardous. In order to demonstrate that it is meeting the
    landfill disposal or combustion conditions contained in the K181 waste listing
    description, the generator must maintain documentation as described in
    subsection (d)(4) of this Section.
     
    1) Determination based on no K181 waste constituents. A generator that has
    knowledge (e.g., knowledge of constituents in wastes based on prior
    sampling and analysis data or information about raw materials used,
    production processes used, and reaction and degradation products formed)
    that its waste contains none of the K181 waste constituents (see
    subsections (c) of this Section) can use its knowledge to determine that its
    waste is not K181 waste. The generator must document the basis for all
    such determinations on an annual basis and keep each annual
    documentation for three years.
     
    2) Determination for generated quantities of 1,000 tonnes (1,000 metric tons)
    per year or less for wastes that contain K181 waste constituents. If the
    total annual quantity of dyes or pigment nonwastewaters generated is
    1,000 tonnes or less, the generator can use knowledge of the wastes (e.g.,
    knowledge of constituents in wastes based on prior analytical data or
    information about raw materials used, production processes used, and
    reaction and degradation products formed) to conclude that annual mass
    loadings for the K181 constituents are below the listing levels of
    subsection (c) of this Section. To make this determination, the generator
    must fulfill the following conditions:
     
    A) Each year, the generator must document the basis for determining
    that the annual quantity of nonwastewaters expected to be
    generated will be less than 1,000 tonnes;
     
    B) The generator must track the actual quantity of nonwastewaters
    generated from January 1 through December 31 of each calendar
    year. If, at any time within the year, the actual waste quantity
    exceeds 1,000 tonnes, the generator must comply with the
    requirements of subsection (d)(3) of this Section for the remainder
    of that calendar year;
     

     
    182
    C) The generator must keep a running total of the K181 waste
    constituent mass loadings over the course of the calendar year; and
     
    D) The generator must keep the following records on site for the three
    most recent calendar years in which the hazardous waste
    determinations were made:
     
    i) The quantity of dyes or pigment nonwastewaters generated;
     
    ii) The relevant process information used; and
     
    iii) The calculations performed to determine annual total mass
    loadings for each K181 waste constituent in the
    nonwastewaters during the year.
     
    3) Determination for generated quantities greater than 1,000 tonnes per year
    for wastes that contain K181 constituents. If the total annual quantity of
    dyes or pigment nonwastewaters generated is greater than 1,000 tonnes,
    the generator must perform each of the following steps in order to make a
    determination that its waste is not K181 waste:
     
    A) The generator must determine which K181 waste constituents (see
    subsection (c) of this Section) are reasonably expected to be
    present in the wastes based on knowledge of the wastes (e.g.,
    based on prior sampling and analysis data or information about
    raw materials used, production processes used, and reaction and
    degradation products formed);
     
    B) If 1,2-phenylenediamine is present in the wastes, the generator can
    use either knowledge of the wastes or sampling and analysis
    procedures to determine the level of this constituent in the wastes.
    For determinations based on use of knowledge of the wastes, the
    generator must comply with the procedures for using knowledge of
    the wastes described in subsection (d)(2) of this Section and keep
    the records described in subsection (d)(2)(D) of this Section. For
    determinations based on sampling and analysis, the generator must
    comply with the sampling and analysis and recordkeeping
    requirements described in subsection (d)(3)(C) of this Section;
     
    C) The generator must develop a waste sampling and analysis plan (or
    modify an existing plan) to collect and analyze representative
    waste samples for the K181 waste constituents reasonably
    expected to be present in the wastes. At a minimum, the plan must
    include the following elements:
     
    i) A discussion of the number of samples needed to

     
    183
    characterize the wastes fully;
     
    ii) The planned sample collection method to obtain
    representative waste samples;
     
    iii) A discussion of how the sampling plan accounts for
    potential temporal and spatial variability of the wastes; and
     
    iv) A detailed description of the test methods to be used,
    including sample preparation, clean up (if necessary), and
    determinative methods;
     
    D) The generator must collect and analyze samples in accordance with
    the waste sampling and analysis plan, and the plan must fulfill the
    following requirements:
     
    i) The sampling and analysis must be unbiased, precise, and
    representative of the wastes; and
     
    ii) The analytical measurements must be sufficiently sensitive,
    accurate, and precise to support any claim that the
    constituent mass loadings are below the listing levels of
    subsection (c) of this Section;
     
    E) The generator must record the analytical results;
     
    F) The generator must record the waste quantity represented by the
    sampling and analysis results;
     
    G) The genrator must calculate constituent-specific mass loadings
    (product of concentrations and waste quantity);
     
    H) The generator must keep a running total of the K181 waste
    constituent mass loadings over the course of the calendar year;
     
    I) The generator must determine whether the mass of any of the
    K181 waste constituents listed in subsection (c) of this Section
    generated between January 1 and December 31 of any calendar
    year is below the K181 waste listing levels;
     
    J) The generator must keep the following records on site for the three
    most recent calendar years in which the hazardous waste
    determinations are made:
     
    i) The sampling and analysis plan;
     

     
    184
    ii) The sampling and analysis results (including quality
    assurance or quality control data);
     
    iii) The quantity of dyes or pigment nonwastewaters generated;
    and
     
    iv) The calculations performed to determine annual mass
    loadings; and
     
    K) The generator must conduct non-hazardous waste determinations
    annually to verify that the wastes remain non-hazardous.
     
    i) The annual testing requirements are suspended after three
    consecutive successful annual demonstrations that the
    wastes are non-hazardous. The generator can then use
    knowledge of the wastes to support subsequent annual
    determinations.
     
    ii) The annual testing requirements are reinstated if the
    manufacturing or waste treatment processes generating the
    wastes are significantly altered, resulting in an increase of
    the potential for the wastes to exceed the listing levels.
     
    iii) If the annual testing requirements are suspended, the
    generator must keep records of the process knowledge
    information used to support a non-hazardous determination.
    If testing is reinstated, the generator must retain a
    description of the process change.
     
    4) Recordkeeping for the landfill disposal and combustion exemptions. For
    the purposes of meeting the landfill disposal and combustion condition set
    out in the K181 waste listing description in subsection (a) of this Section,
    the generator must maintain on-site for three years documentation
    demonstrating that each shipment of waste was received by a landfill unit
    that is subject to or which meets the landfill design standards set out in the
    listing description or that the waste was treated in combustion units, as
    specified in the listing description in subsection (a) of this Section.
     
    5) Waste holding and handling. During the interim period, from the point of
    generation to completion of the hazardous waste determination, the
    generator must store the wastes appropriately. If the wastes are
    determined to be hazardous and the generator has not complied with the
    hazardous waste storage requirements of 35 Ill. Adm. Code 722.134
    during the interim period, the generator could be subject to an
    enforcement action for improper hazardous waste management.
     

     
    185
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.135 Wood Preserving Wastes
     
    a) Wastes from wood preserving processes at plants that do not resume or initiate
    use of chlorophenolic preservatives will not meet the listing definition of F032
    once the generator has met all of the requirements of subsections (b) and (c) of
    this Section. These wastes may, however, continue to meet another hazardous
    waste listing description or may exhibit one or more of the hazardous waste
    characteristics.
     
    b) Generators must either clean or replace all process equipment that may have come
    into contact with chlorophenolic formulations or constituents thereof, including,
    but not limited to, treatment cylinders, sumps, tanks, piping systems, drip pads,
    fork lifts and trams, in a manner that minimizes or eliminates the escape of
    hazardous waste or constituents, leachate, contaminated drippage or hazardous
    waste decomposition products to the groundwater, surface water, or atmosphere.
     
    1) Generators must do one of the following:
     
    A) Prepare and follow an equipment cleaning plan and clean
    equipment in accordance with this Section; or
     
    B) Prepare and follow an equipment replacement plan and replace
    equipment in accordance with this Section; or
     
    C) Document cleaning and replacement in accordance with this
    Section, carried out after termination of use of chlorophenolic
    preservatives.
     
    2) Cleaning requirements.
     
    A) The generator must prepare and sign a written equipment cleaning
    plan that describes the following:
     
    i) The equipment to be cleaned;
     
    ii) How the equipment will be cleaned;
     
    iii) The solvent to be used in cleaning;
     
    iv) How solvent rinses will be tested; and
     
    v) How cleaning residues will be disposed of.
     
    B) Equipment must be cleaned as follows:

     
    186
     
    i) Remove all visible residues from process equipment; and
     
    ii) Rinse process equipment with an appropriate solvent until
    dioxins and dibenzofurans are not detected in the final
    solvent rinse.
     
    C) Analytical requirements.
     
    i) Rinses must be tested in accordance with SW-846, Method
    8290, incorporated by reference in 35 Ill. Adm. Code
    720.111 by using an appropriate method.
     
    ii) “Not detected” means at or below the following lower
    method calibration limit (MCL) in Method 8290, Table 1
    limit (MCL): the 2,3,7,8-TCDD-based MCL is 0.01 parts
    per trillion (ppt), using a sample weight of 1000 g, an IS
    spiking level of 1 ppt, and a final extraction volume of 10
    to 50 μ
    . For other congeners, multiply the values by 1 for
    TCDF, PeCDD, or PeCDF; by 2.5 for HxCDD, HxCDF,
    HpCDD, or HpCDF; or by 5 for OCDD or OCDF.
     
    D) The generator must manage all residues from the cleaning process
    as F032 waste.
     
    3) Replacement requirements.
     
    A) Prepare and sign a written equipment replacement plan that
    describes the following:
     
    i) The equipment to be replaced;
     
    ii) How the equipment will be replaced; and
     
    iii) How the equipment will be disposed of.
     
    B) The generator must manage the discarded equipment as F032
    waste.
     
    4) Documentation requirements. Document that previous equipment
    cleaning and replacement was performed in accordance with this Section
    and ocurred after cessation of use of chlorophenolic preservatives.
     
    c) The generator must maintain the following records documenting the cleaning and
    replacement as part of the facility’s operating record:
     

     
    187
    1) The name and address of the facility;
     
    2) Formulations previously used and the date on which their use ceased in
    each process at the plant;
     
    3) Formulations currently used in each process at the plant;
     
    4) The equipment cleaning or replacement plan;
     
    5) The name and address of any persons who conducted the cleaning and
    replacement;
     
    6) The dates on which cleaning and replacement were accomplished;
     
    7) The dates of sampling and testing;
     
    8) A description of the sample handling and preparation techniques used for
    extraction, containerization, preservation and chain-of-custody of the
    samples;
     
    9) A description of the tests performed, the date the tests were performed and
    the results of the tests;
     
    10) The name and model numbers of the instruments used in performing the
    tests;
     
    11) QA/QC documentation; and
     
    12) The following statement signed by the generator or the generator’s
    authorized representative:
     
    I certify under penalty of law that all process equipment required
    to be cleaned or replaced under 35 Ill. Adm. Code 721.135 was
    cleaned or replaced as represented in the equipment cleaning and
    replacement plan and accompanying documentation. I am aware
    that there are significant penalties for providing false information,
    including the possibility of fine or imprisonment.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.138 Comparable or Syngas Fuel Exclusion
     
    Wastes that meet the following comparable or syngas fuel requirements are not solid wastes:
     
    a) Comparable fuel specifications.
     

     
    188
    1) Physical specifications.
     
    A) Heating value. The heating value must exceed 5,000 Btu/lb
    (11,500 J/g).
     
    B) Viscosity. The viscosity must not exceed 50 cs, as fired.
     
    2) Constituent specifications. For the compounds listed, the constituent
    specification levels and minimum required detection limits (where non-
    detect is the constituent specification) are set forth in the table at
    subsection (d) of this Section.
     
    b) Synthesis gas fuel specification. Synthesis gas fuel (i.e., syngas fuel) that is
    generated from hazardous waste must fulfill the following requirements:
     
    1) It must have a minimum Btu value of 100 Btu/Scf;
     
    2) It must contain less than 1 ppmv of total halogen;
     
    3) It must contain less than 300 ppmv of total nitrogen other than diatomic
    nitrogen (N2);
     
    4) It must contain less than 200 ppmv of hydrogen sulfide; and
     
    5) It must contain less than 1 ppmv of each hazardous constituent in the
    target list of constituents listed in Appendix H of this Part.
     
    c) Implementation. Waste that meets the comparable or syngas fuel specifications
    provided by subsection (a) or (b) of this Section (these constituent levels must be
    achieved by the comparable fuel when generated, or as a result of treatment or
    blending, as provided in subsection (c)(3) or (c)(4) of this Section) is excluded
    from the definition of solid waste provided that the following requirements are
    met:
     
    1) Notices. For purposes of this Section, the person claiming and qualifying
    for the exclusion is called the comparable or syngas fuel generator and the
    person burning the comparable or syngas fuel is called the comparable or
    syngas burner. The person that generates the comparable fuel or syngas
    fuel must claim and certify to the exclusion.
     
    A) Notice to the Agency.
     
    i) The generator must submit a one-time notice to the
    Agency, certifying compliance with the conditions of the
    exclusion and providing documentation, as required by
    subsection (c)(1)(A)(iii) of this Section;

     
    189
     
    ii) If the generator is a company that generates comparable or
    syngas fuel at more than one facility, the generator must
    specify at which sites the comparable or syngas fuel will be
    generated;
     
    iii) A comparable or syngas fuel generator’s notification to the
    Agency must contain the items listed in subsection
    (c)(1)(C) of this Section.
     
    B) Public notice. Prior to burning an excluded comparable or syngas
    fuel, the burner must publish in a major newspaper of general
    circulation, local to the site where the fuel will be burned, a notice
    entitled “Notification of Burning a Comparable or Syngas Fuel
    Excluded Under the Resource Conservation and Recovery Act”
    containing the following information:
     
    i) The name, address, and USEPA identification number of
    the generating facility;
     
    ii) The name and address of the units that will burn the
    comparable or syngas fuel;
     
    iii) A brief, general description of the manufacturing,
    treatment, or other process generating the comparable or
    syngas fuel;
     
    iv) An estimate of the average and maximum monthly and
    annual quantity of the waste claimed to be excluded; and
     
    v) The name and mailing address of the Agency office to
    which the claim was submitted.
     
    C) Required content of comparable or syngas notification to the
    Agency.
     
    i) The name, address, and USEPA identification number of
    the person or facility claiming the exclusion;
     
    ii) The applicable USEPA hazardous waste codes for the
    hazardous waste;
     
    iii) The name and address of the units that meet the
    requirements of subsection (c)(2) of this Section that will
    burn the comparable or syngas fuel; and
     

     
    190
    iv) The following statement, signed and submitted by the
    person claiming the exclusion or its authorized
    representative:
     
    Under penalty of criminal and civil prosecution for
    making or submitting false statements,
    representations, or omissions, I certify that the
    requirements of 35 Ill. Adm. Code 721.138 have
    been met for all waste identified in this
    notification. Copies of the records and information
    required by 35 Ill. Adm. Code 721.138(c)(10) are
    available at the comparable or syngas fuel
    generator’s facility. Based on my inquiry of the
    individuals immediately responsible for obtaining
    the information, the information is, to the best of
    my knowledge and belief, true, accurate, and
    complete. I am aware that there are significant
    penalties for submitting false information, including
    the possibility of fine and imprisonment for
    knowing violations.
     
    BOARD NOTE: Subsections (c)(1)(C)(i) through (c)(1)(C)(iv) are
    derived from 40 CFR 261.138(c)(1)(i)(C)(
    1
    ) and (c)(1)(i)(C)(
    4
    ),
    which the Board has codified here to comport with Illinois
    Administrative Code format requirements.
     
    2) Burning. The comparable or syngas fuel exclusion for fuels that meet the
    requirements of subsections (a) or (b) and (c)(1) of this Section applies
    only if the fuel is burned in the following units that also must be subject to
    federal, State, and local air emission requirements, including all applicable
    federal Clean Air Act (CAA) maximum achievable control technology
    (MACT) requirements:
     
    A) Industrial furnaces, as defined in 35 Ill. Adm. Code 720.110;
     
    B) Boilers, as defined in 35 Ill. Adm. Code 720.110, that are further
    defined as follows:
     
    i) Industrial boilers located on the site of a facility engaged in
    a manufacturing process where substances are transformed
    into new products, including the component parts of
    products, by mechanical or chemical processes; or
     
    ii) Utility boilers used to produce electric power, steam,
    heated or cooled air, or other gases or fluids for sale;
     

     
    191
    C) Hazardous waste incinerators subject to regulation under Subpart
    O of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725
    or applicable CAA MACT standards.
     
    D) Gas turbines used to produce electric power, steam, heated or
    cooled air, or other gases or fluids for sale.
     
    3) Blending to meet the viscosity specification. A hazardous waste blended
    to meet the viscosity specification must fulfill the following requirements:
     
    A) As generated and prior to any blending, manipulation, or
    processing, the waste must meet the constituent and heating value
    specifications of subsections (a)(1)(A) and (a)(2) of this Section;
     
    B) The waste must be blended at a facility that is subject to the
    applicable requirements of 35 Ill. Adm. Code 724 and 725 or 35
    Ill. Adm. Code 722.134; and
     
    C) The waste must not violate the dilution prohibition of subsection
    (c)(6) of this Section.
     
    4) Treatment to meet the comparable fuel exclusion specifications.
     
    A) A hazardous waste may be treated to meet the exclusion
    specifications of subsections (a)(1) and (a)(2) of this Section
    provided the treatment fulfills the following requirements:
     
    i) The treatment destroys or removes the constituent listed in
    the specification or raises the heating value by removing or
    destroying hazardous constituents or materials;
     
    ii) The treatment is performed at a facility that is subject to the
    applicable requirements of 35 Ill. Adm. Code 724 and 725
    or 35 Ill. Adm. Code 722.134; and
     
    iii) The treatment does not violate the dilution prohibition of
    subsection (c)(6) of this Section.
     
    B) Residuals resulting from the treatment of a hazardous waste listed
    in Subpart D of this Part to generate a comparable fuel remain a
    hazardous waste.
     
    5) Generation of a syngas fuel.
     
    A) A syngas fuel can be generated from the processing of hazardous
    wastes to meet the exclusion specifications of subsection (b) of this

     
    192
    Section provided the processing fulfills the following
    requirements:
     
    i) The processing destroys or removes the constituent listed in
    the specification or raises the heating value by removing or
    destroying constituents or materials;
     
    ii) The processing is performed at a facility that is subject to
    the applicable requirements of 35 Ill. Adm. Code 724 and
    725 or 35 Ill. Adm. Code 722.134 or is an exempt recycling
    unit pursuant to Section 721.106(c); and
     
    iii) The processing does not violate the dilution prohibition of
    subsection (c)(6) of this Section.
     
    B) Residuals resulting from the treatment of a hazardous waste listed
    in Subpart D of this Part to generate a syngas fuel remain a
    hazardous waste.
     
    6) Dilution prohibition for comparable and syngas fuels. No generator,
    transporter, handler, or owner or operator of a treatment, storage, or
    disposal facility must in any way dilute a hazardous waste to meet the
    exclusion specifications of subsection (a)(1)(A), (a)(2), or (b) of this
    Section.
     
    7) Waste analysis plans. The generator of a comparable or syngas fuel must
    develop and follow a written waste analysis plan that describes the
    procedures for sampling and analysis of the hazardous waste to be
    excluded. The waste analysis plan must be developed in accordance with
    the applicable sections of the “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods” (SW-846). The plan must be followed and
    retained at the facility excluding the waste.
     
    A) At a minimum, the plan must specify the following:
     
    i) The parameters for which each hazardous waste will be
    analyzed and the rationale for the selection of those
    parameters;
     
    ii) The test methods that will be used to test for these
    parameters;
     
    iii) The sampling method that will be used to obtain a
    representative sample of the waste to be analyzed;
     
    iv) The frequency with which the initial analysis of the waste

     
    193
    will be reviewed or repeated to ensure that the analysis is
    accurate and up to date; and
     
    v) If process knowledge is used in the waste determination,
    any information prepared by the generator in making such
    determination.
     
    B) The waste analysis plan must also contain records of the following:
     
    i) The dates and times waste samples were obtained, and the
    dates the samples were analyzed;
     
    ii) The names and qualifications of the persons who obtained
    the samples;
     
    iii) A description of the temporal and spatial locations of the
    samples;
     
    iv) The name and address of the laboratory facility at which
    analyses of the samples were performed;
     
    v) A description of the analytical methods used, including any
    clean-up and sample preparation methods;
     
    vi) All quantitation limits achieved and all other quality
    control results for the analysis (including method blanks,
    duplicate analyses, matrix spikes, etc.), laboratory quality
    assurance data, and description of any deviations from
    analytical methods written in the plan or from any other
    activity written in the plan that occurred;
     
    vii) All laboratory results demonstrating that the exclusion
    specifications have been met for the waste; and
     
    viii) All laboratory documentation that supports the analytical
    results, unless a contract between the claimant and the
    laboratory provides for the documentation to be maintained
    by the laboratory for the period specified in subsection
    (c)(11) of this Section and also provides for the availability
    of the documentation to the claimant upon request.
     
    C) Syngas fuel generators must submit for approval, prior to
    performing sampling, analysis, or any management of a syngas
    fuel as an excluded waste, a waste analysis plan containing the
    elements of subsection (c)(7)(A) of this Section to the Agency.
    The approval of waste analysis plans must be stated in writing and

     
    194
    received by the facility prior to sampling and analysis to
    demonstrate the exclusion of a syngas. The approval of the waste
    analysis plan may contain such provisions and conditions as the
    regulatory authority deems appropriate.
     
    8) Comparable fuel sampling and analysis.
     
    A) General. For each waste for which an exclusion is claimed, the
    generator of the hazardous waste must test for all the constituents
    on Appendix H of this Part, except those that the generator
    determines, based on testing or knowledge, should not be present
    in the waste. The generator is required to document the basis of
    each determination that a constituent should not be present. The
    generator may not determine that any of the following categories
    of constituents should not be present:
     
    i) A constituent that triggered the toxicity characteristic for
    the waste constituents that were the basis of the listing of
    the waste stream, or constituents for which there is a
    treatment standard for the waste code in 35 Ill. Adm. Code
    728.140;
     
    ii) A constituent detected in previous analysis of the waste;
     
    iii) Constituents introduced into the process that generates the
    waste; or
     
    iv) Constituents that are byproducts or side reactions to the
    process that generates the waste.
     
    B) For each waste for which the exclusion is claimed where the
    generator of the comparable or syngas fuel is not the original
    generator of the hazardous waste, the generator of the comparable
    or syngas fuel may not use process knowledge pursuant to
    subsection (c)(8)(A) of this Section and must test to determine that
    all of the constituent specifications of subsections (a)(2) and (b) of
    this Section have been met.
     
    C) The comparable or syngas fuel generator may use any reliable
    analytical method to demonstrate that no constituent of concern is
    present at concentrations above the specification levels. It is the
    responsibility of the generator to ensure that the sampling and
    analysis are unbiased, precise, and representative of the waste. For
    the waste to be eligible for exclusion, a generator must
    demonstrate the following:
     

     
    195
    i) That each constituent of concern is not present in the waste
    above the specification level at the 95 percent upper
    confidence limit around the mean; and
     
    ii) That the analysis could have detected the presence of the
    constituent at or below the specification level at the 95
    percent upper confidence limit around the mean.
     
    D) Nothing in this subsection (c)(8) preempts, overrides, or otherwise
    negates the provision in 35 Ill. Adm. Code 722.111 that requires
    any person that generates a solid waste to determine if that waste is
    a hazardous waste.
     
    E) In an enforcement action, the burden of proof to establish
    conformance with the exclusion specification must be on the
    generator claiming the exclusion.
     
    F) The generator must conduct sampling and analysis in accordance
    with its waste analysis plan developed under subsection (c)(7) of
    this Section.
     
    G) Syngas fuel and comparable fuel that has not been blended in order
    to meet the kinematic viscosity specifications must be analyzed as
    generated.
     
    H) If a comparable fuel is blended in order to meet the kinematic
    viscosity specifications, the generator must undertake the
    following actions:
     
    i) Analyze the fuel as generated to ensure that it meets the
    constituent and heating value specifications; and
     
    ii) After blending, analyze the fuel again to ensure that the
    blended fuel continues to meet all comparable or syngas
    fuel specifications.
     
    I) Excluded comparable or syngas fuel must be retested, at a
    minimum, annually and must be retested after a process change
    that could change the chemical or physical properties of the waste.
     
    Note to subsection (c)(8): Any claim under this Section must be valid and
    accurate for all hazardous constituents; a determination not to test for a
    hazardous constituent will not shield a generator from liability should that
    constituent later be found in the waste above the exclusion specifications.
     
    9) Speculative accumulation. Any persons handling a comparable or syngas

     
    196
    fuel are subject to the speculative accumulation test under Section
    721.102(c)(4).
     
    10) Records. The generator must maintain records of the following
    information on-site:
     
    A) All information required to be submitted to the implementing
    authority as part of the notification of the claim:
     
    i) The owner or operator name, address, and RCRA facility
    USEPA identification number of the person claiming the
    exclusion;
     
    ii) The applicable USEPA hazardous waste codes for each
    hazardous waste excluded as a fuel; and
     
    iii) The certification signed by the person claiming the
    exclusion or his authorized representative;
     
    B) A brief description of the process that generated the hazardous
    waste and process that generated the excluded fuel, if not the same;
     
    C) An estimate of the average and maximum monthly and annual
    quantities of each waste claimed to be excluded;
     
    D) Documentation for any claim that a constituent is not present in the
    hazardous waste, as required under subsection (c)(8)(A) of this
    Section;
     
    E) The results of all analyses and all detection limits achieved, as
    required under subsection (c)(8) of this Section;
     
    F) If the excluded waste was generated through treatment or blending,
    documentation, as required under subsection (c)(3) or (c)(4) of this
    Section;
     
    G) If the waste is to be shipped off-site, a certification from the
    burner, as required under subsection (c)(12) of this Section;
     
    H) A waste analysis plan and the results of the sampling and analysis
    that include the following:
     
    i) The dates and times waste samples were obtained, and the
    dates the samples were analyzed;
     
    ii) The names and qualifications of the persons that obtained

     
    197
    the samples;
     
    iii) A description of the temporal and spatial locations of the
    samples;
     
    iv) The name and address of the laboratory facility at which
    analyses of the samples were performed;
     
    v) A description of the analytical methods used, including any
    clean-up and sample preparation methods;
     
    vi) All quantitation limits achieved and all other quality
    control results for the analysis (including method blanks,
    duplicate analyses, matrix spikes, etc.), laboratory quality
    assurance data, and description of any deviations from
    analytical methods written in the plan or from any other
    activity written in the plan that occurred;
     
    vii) All laboratory analytical results demonstrating that the
    exclusion specifications have been met for the waste; and
     
    viii) All laboratory documentation that supports the analytical
    results, unless a contract between the claimant and the
    laboratory provides for the documentation to be maintained
    by the laboratory for the period specified in subsection
    (c)(11) of this Section and also provides for the availability
    of the documentation to the claimant upon request; and
     
    I) If the generator ships comparable or syngas fuel off-site for
    burning, the generator must retain for each shipment the following
    information on-site:
     
    i) The name and address of the facility receiving the
    comparable or syngas fuel for burning;
     
    ii) The quantity of comparable or syngas fuel shipped and
    delivered;
     
    iii) The date of shipment or delivery;
     
    iv) A cross-reference to the record of comparable or syngas
    fuel analysis or other information used to make the
    determination that the comparable or syngas fuel meets the
    specifications, as required under subsection (c)(8) of this
    Section; and
     

     
    198
    v) A one-time certification by the burner, as required under
    subsection (c)(12) of this Section.
     
    11) Records retention. Records must be maintained for the period of three
    years. A generator must maintain a current waste analysis plan during that
    three-year period.
     
    12) Burner certification. Prior to submitting a notification to the Agency, a
    comparable or syngas fuel generator that intends to ship its fuel off-site for
    burning must obtain a one-time written, signed statement from the burner
    that includes the following:
     
    A) A certification that the comparable or syngas fuel will only be
    burned in an industrial furnace or boiler, utility boiler, or
    hazardous waste incinerator, as required under subsection (c)(2) of
    this Section;
     
    B) Identification of the name and address of the units that will burn
    the comparable or syngas fuel; and
     
    C) A certification that the state in which the burner is located is
    authorized to exclude wastes as comparable or syngas fuel under
    the provisions of this Section.
     
    13) Ineligible waste codes. Wastes that are listed because of presence of
    dioxins or furans, as set out in Appendix G of this Part, are not eligible for
    this exclusion, and any fuel produced from or otherwise containing these
    wastes remains a hazardous waste subject to full RCRA hazardous waste
    management requirements.
     
    d) Table Y of this Part sets forth the table of detection and detection limit values for
    comparable fuel specification.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.Appendix A Representative Sampling Methods
     
    The methods and equipment used for sampling waste materials will vary with the form and
    consistency of the waste materials to be sampled. Samples collected using the sampling
    protocols listed below, for sampling waste with properties similar to the indicated materials, are
    considered by USEPA to be representative of the waste.
     
    Extremely viscous liquid: ASTM Standard D140–70, (Standard Practice for Sampling
    Bituminous Materials), incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(a).
     
    Crushed or powdered material: ASTM Standard D346–75, (Standard Practice for Collection and

     
    199
    Preparation of Coke Samples for Laboratory Analysis), incorporated by reference in 35 Ill. Adm.
    Code 720.111 720.111(a).
     
    Soil or rock-like material: ASTM Standard D420–69, (Guide to Site Characterization for
    Engineering, Design, and Construction Purposes)” incorporated by reference in 35 Ill. Adm.
    Code 720.111 720.111(a).
     
    Soillike Soil-like material: ASTM Standard D1452–65, (Standard Practice for Soil Investigation
    and Sampling by Auger Borings), incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(a).
     
    Fly Ash-like ash-like material: ASTM Standard D2234–76, (Standard Practice for Collection of
    a Gross Sample of Coal), incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(a).
     
    Containerized liquid wastes: “Composite Liquid Waste Sampler (COLIWASA).” described in
    “Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods,” SW-846,
    incorporated by reference in 35 Ill. Adm. Code 720.111.
    BOARD NOTE: This method is also described in “Samplers and Sampling Procedures for
    Hazardous Waste Streams,” EPA 600/2–80–018, January 1980.
     
    Liquid waste in pits, ponds, lagoons, and similar reservoirs: “Pond Sampler,.” described in “Test
    Methods for the Evaluation of Solid Waste, Physical/Chemical Methods,” SW-846, incorporated
    by reference in 35 Ill. Adm. Code 720.111.
    BOARD NOTE: This manual also contains additional information on application of these
    protocols. This method is also described in “Samplers and Sampling Procedures for Hazardous
    Waste Streams,” EPA 600/2–80–018, January 1980, incorporated by reference in 35 Ill. Adm.
    Code 720.111..
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.Appendix B Method 1311 Toxicity Characteristic Leaching Procedure (TCLP)
    (Repealed)
     
    NOTE: The TCLP (Method 1311) is published in “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods,” USEPA Publication SW-846, incorporated by reference in 35 Ill.
    Adm. Code 720.111.
     
    (Source: Repealed at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.Appendix C Chemical Analysis Test Methods (Repealed)
     
    NOTE: Appropriate analytical procedures to determine whether a sample contains a given toxic
    constituent are specified in Chapter Two, “Choosing the Correct Procedure,” found in “Test
    Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA Publication SW-
    846, incorporated by reference in 35 Ill. Adm. Code 720.111. Prior to final sampling and
    analysis method selection, the individual should consult the specific section or method described

     
    200
    in SW-846 for additional guidance on which of the approved methods should be employed for a
    specific sample analysis situation.
     
    (Source: Repealed at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.Appendix G Basis for Listing Hazardous Wastes
     
    USEPA hazard-
    ous waste No.
    Hazardous constituents for which listed
    F001 Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-
    trichloroethane, carbon tetrachloride, chlorinated fluorocarbons.
    F002 Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-
    trichloroethane, 1,1,2-trichlorethane, chlorobenzene, 1,1,2-trichloro-1,2,2-
    trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane.
    F003 N.A.
    F004 Cresols and cresylic acid, nitrobenzene.
    F005 Toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, 2-
    ethoxyethanol, benzene, 2-nitropropane.
    F006 Cadmium, hexavalent chromium, nickel, cyanide (complexed).
    F007 Cyanide (salts).
    F008 Cyanide (salts).
    F009 Cyanide (salts).
    F010 Cyanide (salts).
    F011 Cyanide (salts).
    F012 Cyanide (complexed).
    F019 Hexavalent chromium, cyanide (complexed).
    F020 Tetra- and pentachlorodibenzo-p-dioxins; tetra- and
    pentachlorodibenzofurans; tri- and tetrachlorophenols and their
    clorophenoxy derivative acids, esters, ethers, amines, and other salts.
    F021 Penta- and hexachlorodibenzo-p-dioxins; penta- and
    hexachlorodibenzofurans; pentachlorophenol and its derivatives.
    F022 Tetra-, penta- and hexachlorodibenzo-p-dioxins; tetra-, penta-, and
    hexachlorodibenzofurans.
    F023 Tetra- and pentachlorodibenzo-p-dioxins; tetra- and
    pentachlorodibenzofurans; tri- and tetra- chlorophenols and their
    chlorophenoxy derivative acids, esters, ethers, amines, and other salts.
    F024 Chloromethane, dichloromethane, trichloromethane, carbon tetrachloride,
    chloroethylene, 1,1-dichloroethane, 1,2-dichloroethane, trans-1,2-
    dichloroethylene, 1,1-dichloroethylene, 1,1,1-trichloroethane, 1,1,2-
    trichloroethane, trichloroethylene, 1,1,1,2-tetrachloroethane, 1,1,2,2-
    tetrachloroethane, tetrachloroethylene, pentachloroethane, hexachloroethane,
    allyl chloride (3-chloropropene), dichloropropane, dichloropropene, 2-
    chloro-1,3-butadiene, hexachloro-1,3-butadiene, hexachlorochylopentadiene,
    hexachlorocylohexane, benzene, chlorobenzene, dichlorobenzenes, 1,2,4-
    trichlorobenzene, tetrachlorobenzenes, pentachlorobenzene,
    hexachlorobenzene, toluene, naphthalene.

     
    201
    F025 Chloromethane, dicloromethane, trichloromethane; carbon tetrachloride;
    chloroethylene; 1,1-dichloroethane; 1,2-dichloroethane; trans-1,2-
    dichloroethylene; 1,1-dichloroethylene; 1,1,1-trichloroethane; 1,1,2-
    trichloroethane; trichloroethylene; 1,1,1,2-tetrachloroethane; 1,1,2,2-
    tetrachloroethane; tetrachloroethylene; pentachloroethane; hexachloroethane;
    allyl chloride (3-chloropropene); dichloropropane; dichloropropene; 2-
    chloro-1,3-butadiene; hexachloro-1,3-butadiene; hexachlorocyclopentadiene;
    benzene; chlorobenzene; dichlorobenzene; 1,2,4-trichlorobenzene;
    tetrachlorobenzene; pentachlorobenzene; hexachlorobenzene; toluene;
    naphthalene.
    F026 Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and
    hexachlorodibenzofurans.
    F027 Tetra-, penta, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and
    hexachlorodibenzofurans; tri-, tetra-, and pentachlorophenols and their
    chlorophenoxy derivative acids, esters, ethers, amines, and other salts.
    F028 Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and
    hexachlorodibenzofurans; tri-, tetra-, and pentachlorophenols and their
    chlorophenoxy derivative acids, esters, ethers, amines, and other salts.
    F032 Benz(a)anthracene; benzo(a)pyrene; dibenz(a,h)anthracene; indeno(1,2,3-
    cd)pyrene; pentachlorophenol; arsenic; chromium; tetra-, penta-, hexa-, and
    heptachlorordibenzo-p-dioxins; tetra-, penta-, hexa-, and
    heptachlorodibenzofurans.
    F034 Benz(a)anthracene, benzo(k)fluoranthene, benzo(a)pyrene,
    dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene, naphthalene, arsenic,
    chromium.
    F035 Arsenic, chromium, lead.
    F037 Benzene, benzo(a)pyrene, chrysene, lead, chromium.
    F038 Benzene, benzo(a)pyrene, chrysene, lead, chromium.
    F039 All constituents for which treatment standards are specified for multi-source
    leachate (wastewaters and non-wastewaters nonwastewaters) under Table B
    to 35 Ill. Adm. Code 728 (Constituent Concentrations in Waste).
    K001 Pentachlorophenol, phenol, 2-chlorophenol, p-chloro-m-cresol, 2,4-
    dimethylphenol, 2,4- dinitrophenol, trichlorophenols, tetrachlorophenols,
    2,4- dinitrophenol, creosote, chrysene, naphthalene, fluoranthene,
    benzo(b)fluoranthene, benzo(a)pyrene, indeno(1,2,3-cd)pyrene, benz(a)
    anthracene, dibenz(a)anthracene, acenaphthalene.
    K002 Hexavalent chromium, lead.
    K003 Hexavalent chromium, lead.
    K004 Hexavalent chromium.
    K005 Hexavalent chromium, lead.
    K006 Hexavalent chromium.
    K007 Cyanide (complexed), hexavalent chromium.
    K008 Hexavalent chromium.
    K009 Chloroform, formaldehyde, methylene chloride, methyl chloride,
    paraldehyde, formic acid.

     
    202
    K010 Chloroform, formaldehyde, methylene chloride, methyl chloride,
    paraldehyde, formic acid, chloroacetaldehyde.
    K011 Acrylonitrile, acetonitrile, hydrocyanic acid.
    K013 Hydrocyanic acid, acrylonitrile, acetonitrile.
    K014 Acetonitrile, acrylamide.
    K015 Benzyl chloride, chlorobenzene, toluene, benzotrichloride.
    K016 Hexachlorobenzene, hexachlorobutadiene, carbon tetrachloride,
    hexachloroethane, perchloroethylene.
    K017 Epichlorohydrin, chloroethers (bis(chloromethyl) ether and bis- (2-
    chloroethyl) ethers), trichloropropane, dichloropropanols.
    K018 1,2-dichloroethane, trichloroethylene, hexachlorobutadiene,
    hexachlorobenzene.
    K019 Ethylene dichloride, 1,1,1-trichloroethane, 1,1,2-trichloroethane,
    tetrachloroethanes (1,1,2,2-tetrachloroethane and 1,1,1,2-tetrachloroethane),
    trichloroethylene, tetrachloroethylene, carbon tetrachloride, chloroform,
    vinyl chloride, vinylidene chloride.
    K020 Ethylene dichloride, 1,1,1-trichloroethane, 1,1,2-trichloroethane, tetrachloro-
    ethanes (1,1,2,2-tetrachloroethane and 1,1,1,2-tetrachloroethane),
    trichloroethylene, tetrachloroethylene, carbon tetrachloride, chloroform,
    vinyl chloride, vinylidene chloride.
    K021 Antimony, carbon tetrachloride, chloroform.
    K022 Phenol, tars (polycyclic aromatic hydrocarbons).
    K023 Phthalic anhydride, maleic anhydride.
    K024 Phthalic anhydride, 1,4-naphthoguinone.
    K025 Meta-dinitrobenzene, 2,4-dinitrotoluene.
    K026 Paraldehyde, pyridines, 2-picoline.
    K027 Toluene diisocyanate, toluene-2,4-diamine.
    K028 1,1,1-trichloroethane, vinyl chloride.
    K029 1,2-dichloroethane, 1,1,1-trichloroethane, vinyl chloride, vinylidene
    chloride, chloroform.
    K030 Hexachlorobenzene, hexachlorobutadiene, hexachloroethane, 1,1,1,2-
    tetrachloroethane, 1,1,2,2-tetrachloroethane, ethylene dichloride.
    K031 Arsenic.
    K032 Hexachlorocyclopentadiene.
    K033 Hexachlorocyclopentadiene.
    K034 Hexachlorocyclopentadiene.
    K035 Creosote, chrysene, naphthalene, fluoranthene, benzo(b) fluoranthene,
    benzo(a)-pyrene, indeno(1,2,3-cd) pyrene, benzo(a)anthracene,
    dibenzo(a)anthracene, acenaphthalene.
    K036 Toluene, phosphorodithioic and phosphorothioic acid esters.
    K037 Toluene, phosphorodithioic and phosphorothioic acid esters.
    K038 Phorate, formaldehyde, phosphorodithioic and phosphorothioic acid esters.
    K039 Phosphorodithioic and phosphorothioic acid esters.
    K040 Phorate, formaldehyde, phosphorodithioic and phosphorothioic acid esters.
    K041 Toxaphene.
    K042 Hexachlorobenzene, ortho-dichlorobenzene.

     
    203
    K043 2,4-dichlorophenol, 2,6-dichlorophenol, 2,4,6-trichlorophenol.
    K044 N.A.
    K045 N.A.
    K046 Lead.
    K047 N.A.
    K048 Hexavalent chromium, lead.
    K049 Hexavalent chromium, lead.
    K050 Hexavalent chromium.
    K051 Hexavalent chromium, lead.
    K052 Lead.
    K060 Cyanide, naphthalene, phenolic compounds, arsenic.
    K061 Hexavalent chromium, lead, cadmium.
    K062 Hexavalent chromium, lead.
    K064 Lead, cadmium.
    K065 Lead, cadmium.
    K066 Lead, cadmium.
    K069 Hexavalent chromium, lead, cadmium.
    K071 Mercury.
    K073 Chloroform, carbon tetrachloride, hexachloroethane, trichloroethane,
    tetrachloroethylene, dichloroethylene, 1,1,2,2-tetrachloroethane.
    K083 Aniline, diphenylamine, nitrobenzene, phenylenediamine.
    K084 Arsenic.
    K085 Benzene, dichlorobenzenes, trichlorobenzenes, tetrachlorobenzenes,
    pentachlorobenzene, hexachlorobenzene, benzyl chloride.
    K086 Lead, hexavalent chromium.
    K087 Phenol, naphthalene.
    K088 Cyanide (complexes).
    K090 Chromium.
    K091 Chromium.
    K093 Phthalic anhydride, maleic anhydride.
    K094 Phthalic anhydride.
    K095 1,1,2-trichloroethane, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane.
    K096 1,2-dichloroethane, 1,1,1-trichloroethane, 1,1,2-trichloroethane.
    K097 Chlordane, heptachlor.
    K098 Toxaphene.
    K099 2,4-dichlorophenol, 2,4,6-trichlorophenol.
    K100 Hexavalent chromium, lead, cadmium.
    K101 Arsenic.
    K102 Arsenic.
    K103 Aniline, nitrobenzene, phenylenediamine.
    K104 Aniline, benzene, diphenylamine, nitrobenzene, phynylenediamine.
    K105 Benzene, monochlorobenzene, dichlorobenzenes, 2,4,6-trichlorophenol.
    K106 Mercury.
    K111 2,4-Dinitrotoluene.
    K112 2,4-Toluenediamine, o-toluidine, p-toluidine, aniline.
    K113 2,4-Toluenediamine, o-toluidine, p-toluidine, aniline.

     
    204
    K114 2,4-Toluenediamine, o-toluidine, p-toluidine.
    K115 2,4-Toluenediamine.
    K116 Carbon tetrachloride, tetrachloroethylene, chloroform, phosgene.
    K117 Ethylene dibromide.
    K118 Ethylene dibromide.
    K123 Ethylene thiourea.
    K124 Ethylene thiourea.
    K125 Ethylene thiourea.
    K126 Ethylene thiourea.
    K131 Dimethyl sulfate, methyl bromide.
    K132 Methyl bromide.
    K136 Ethylene dibromide.
    K141 Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene,
    benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.
    K142 Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene,
    benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.
    K143 Benzene, benz(a)anthracene, benzo(b)fluoranthene, benzo(k)fluoranthene.
    K144 Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene,
    benzo(k)fluoranthene, dibenz(a,h)anthracene.
    K145 Benzene, benz(a)anthracene, benzo(a)pyrene, dibenz(a,h)anthracene,
    naphthalene.
    K147 Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene,
    benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.
    K148 Benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene,
    benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.
    K149 Benzotrichloride, benzyl chloride, chloroform, chloromethane,
    chlorobenzene, 1,4-dichlorobenzene, hexachlorobenzene,
    pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, toluene.
    K150 Carbon tetrachloride, chloroform, chloromethane, 1,4-dichlorobenzene,
    hexachlorobenzene, pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, 1,1,2,2-
    tetrachloroethane, tetrachloroethylene, 1,2,4-trichlorobenzene.
    K151 Benzene, carbon tetrachloride, chloroform, hexachlorobenzene,
    pentachlorobenzene, toluene, 1,2,4,5-tetrachlorobenzene,
    tetrachloroethylene.
    K156 Benomyl, carbaryl, carbendazim, carbofuran, carbosulfan, formaldehyde,
    methylene chloride, triethylamine.
    K157 Carbon tetrachloride, formaldehyde, methyl chloride, methylene chloride,
    pyridine, triethylamine.
    K158 Benomyl, carbendazim, carbofuran, carbosulfan, chloroform, methylene
    chloride.
    K159 Benzene, butylate, EPTC, molinate, pebulate, vernolate.
    K161 Antimony, arsenic, metam-sodium, ziram.
    K169 Benzene.
    K170 Benzo(a)pyrene, dibenz(a,h)anthracene, benzo (a) anthracene,
    benzo(b)fluoranthene, benzo(k)fluoranthene, 3-methylcholanthrene, 7,12-
    dimethylbenz(a)anthracene.

     
    205
    K171 Benzene, arsenic.
    K172 Benzene, arsenic.
    K174 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD),
    1,2,3,4,6,7,8-heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF), 1,2,3,4,7,8,9-
    heptachlorodibenzofuran (1,2,3,6,7,8,9-HpCDF), all hexachlorodibenzo-p-
    dioxins (HxCDDs), all hexachlorodibenzofurans (HxCDFs), all
    pentachlorodibenzo-p-dioxins (PeCDDs), 1,2,3,4,6,7,8,9-octachlorodibenzo-
    p-dioxin (OCDD), 1,2,3,4,6,7,8,9- octachlorodibenzofuran (OCDF), all
    pentachlorodibenzofurans (PeCDFs), all tetrachlorodibenzo-p-dioxins
    (TCDDs), all tetrachlorodibenzofurans (TCDFs).
    K175 Mercury.
    K176 Arsenic, lead.
    K177 Antimony.
    K178 Thallium.
    K181 Aniline, o-anisidine, 4-chloroaniline, p-cresidine, 2,4-dimethylaniline,
    1,2-phenylenediamine, 1,3-phenylenediamine.
     
    N.A.--Waste is hazardous because it fails the test for the characteristic of ignitability, corrosivity,
    or reactivity.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.Appendix H Hazardous Constituents
     
    Common Name Chemical Abstracts Name
    Chemical
    Abstracts
    Number
    (CAS No.)
    USEPA
    Hazard-
    ous
    Waste
    Number
    A2213 Ethanimidothioic acid, 2-
    (dimethylamino)-N-hydroxy-2-
    oxo-, methyl ester
    30558-43-1 U394
    Acetonitrile Same 75-05-8 U003
    Acetophenone Ethanone, 1-phenyl- 98-86-2 U004
    2-Acetylaminofluorene Acetamide,
    N-9H-fluoren-2-yl- 53-96-3 U005
    Acetyl chloride Same 75-36-5 U006
    1-Acetyl-2-thiourea Acetamide, N-
    (aminothioxomethyl)-
    591-08-2 P002
    Acrolein 2-Propenal 107-02-8 P003
    Acrylamide 2-Propenamide 79-06-1 U007
    Acrylonitrile 2-Propenenitrile 107-13-1 U009
    Aflatoxins Same 1402-68-2

     
    206
    Aldicarb Propanal, 2-methyl-2-
    (methylthio)-, O-
    [(methylamino)carbonyl]oxime
    O-((methylamino)carbonyl)-
    oxime
    116-06-3 P070
    Aldicarb sulfone Propanal, 2-methyl-2- (methyl-
    sulfonyl)-, O-[(methylamino)-
    carbonyl]oxime O-
    ((methylamino)carbonyl)oxime
    1646-88-4 P203
    Aldrin 1,4,5,8-Dimethanonaphthalene,
    1,2,3,4,10,10-hexachloro-
    1,4,4a,5,8,8a-hexahydro-, (1-
    α
    ,4-
    α
    ,4a-
    β
    ,5-
    α
    ,8-
    α
    ,8a-
    β
    )-
    309-00-2 P004
    Allyl alcohol 2-Propen-1-ol 107-18-6 P005
    Allyl chloride 1-Propene, 3-chloro- 107-18-6
    Aluminum phosphide Same 20859-73-8 P006
    4-Aminobiphenyl [1,1'-Biphenyl]-4-amine
    (1,1'-Biphenyl)-4-amine
    92-67-1
    5-(Aminomethyl)-3-isoxazolol 3(2H)-Isoxazolone, 5-(amino-
    methyl)-
    2763-96-4 P007
    4-Aminopyridine 4-Pyridinamine 504-24-5 P008
    Amitrole 1H-1,2,4-Triazol-3-amine 61-82-5 U011
    Ammonium vanadate Vanadic acid, ammonium salt 7803-55-6 U119
    Aniline Benzenamine 62-53-3 U012
    o-Anisidine (2-methoxyaniline) Benzenamine, 2-Methoxy- 90–04–0
      
    Antimony Same 7440-36-0
    Antimony compounds, N.O.S.
    (not otherwise specified)
     
    Aramite Sulfurous acid, 2-chloroethyl-, 2-
    [4-(1,1-dimethylethyl)phenoxy]-
    1-methylethyl 2-(4-(1,1-
    dimethylethyl)phenoxy)-1-
    methylethyl ester
    140-57-8
    Arsenic Arsenic 7440-38-2
    Arsenic compounds, N.O.S.
    Arsenic acid Arsenic acid H3AsO4 7778-39-4 P010
    Arsenic pentoxide Arsenic oxide As2O5 1303-28-2 P011
    Arsenic trioxide Arsenic oxide As2O3 1327-53-3 P012
    Auramine Benzenamine, 4,4'-carbon-
    imidoylbis[N, N-dimethyl- 4,4'-
    carbonimidoylbis(N, N-dimethyl-
    492-80-8 U014
    Azaserine L-Serine, diazoacetate (ester) 115-02-6 U015
    Barban Carbamic acid, (3-chlorophenyl)-
    , 4-chloro-2-butynyl ester
    101-27-9 U280
    Barium Same 7440-39-3
    Barium compounds, N.O.S.

     
    207
    Barium cyanide Same 542-62-1 P013
    Bendiocarb 1,3-Benzodioxol-4-ol-2,2-
    dimethyl-, methyl carbamate
    22781-23-3 U278
    Bendiocarb phenol 1,3-Benzodioxol-4-ol-2,2-
    dimethyl-,
    22961-82-6 U364
    Benomyl Carbamic acid, [1- [(butylamino)-
    carbonyl]-1H-benzimidazol-2-
    yl]-, (1- ((butylamino)carbonyl)-
    1H-benzimidazol-2-yl)-, methyl
    ester
    17804-35-2 U271
    Benz[c]acridineBenz(c)acridine Same 225-51-4 U016
    Benz[a]anthraceneBenz(a)anthra-
    cene
    Same 56-55-3 U018
    Benzal chloride Benzene, (dichloromethyl)- 98-87-3 U017
    Benzene Same 71-43-2 U018
    Benzenearsonic acid Arsonic acid, phenyl- 98-05-5
    Benzidine [1,1'-Biphenyl]-4,4'-diamine
    (1,1'-Biphenyl)-4,4'-diamine
    92-87-5 U021
    Benzo[b]fluoranthene
    Benzo(b)fluoranthene
    Benz[e]acephenanthrylene
    Benz(e)acephenanthrylene
    205-99-2
    Benzo[j]fluoranthene
    Benzo(j)fluoranthene
    Same 205-82-3
    Benzo(k)fluoranthene Same 207-08-9
    Benzo[a]pyreneBenzo(a)pyrene Same 50-32-8 U022
    p-Benzoquinone 2,5-Cyclohexadiene-1,4-dione 106-51-4 U197
    Benzotrichloride Benzene, (trichloromethyl)- 98-07-7 U023
    Benzyl chloride Benzene, (chloromethyl)- 100-44-7 P028
    Beryllium powder Same 7440-41-7 P015
    Beryllium compounds, N.O.S.
    Bis(pentamethylene)thiuram
    tetrasulfide
    Piperidine, 1,1'-(tetrathio-
    dicarbonothioyl)-bis-
    120-54-7
    Bromoacetone 2-Propanone, 1-bromo- 598-31-2 P017
    Bromoform Methane, tribromo- 75-25-2 U225
    4-Bromophenyl phenyl ether Benzene, 1-bromo-4-phenoxy- 101-55-3 U030
    Brucine Strychnidin-10-one, 2,3-
    dimethoxy-
    357-57-3 P018
    Butylate Carbamothioic acid, bis(2-
    methylpropyl)-, S-ethyl ester
    2008-41-5
    Butyl benzyl phthalate 1,2-Benzenedicarboxylic acid,
    butyl phenylmethyl ester
    85-68-7
    Cacodylic acid Arsenic acid, dimethyl- 75-60-5 U136
    Cadmium Same 7440-43-9
    Cadmium compounds, N.O.S.
    Calcium chromate Chromic acid H2CrO4, calcium
    salt
    13765-19-0 U032
    Calcium cyanide Calcium cyanide Ca(CN)2 592-01-8 P021

     
    208
    Carbaryl 1-Naphthalenol, methylcarbamate 63-25-2 U279
    Carbendazim Carbamic acid, 1H-benzimidazol-
    2-yl, methyl ester
    10605-21-7 U372
    Carbofuran 7-Benzofuranol, 2,3-dihydro-2,2-
    dimethyl-, methylcarbamate
    1563-66-2 P127
    Carbofuran phenol 7-Benzofuranol, 2,3-dihydro-2,2-
    dimethyl-
    1563-38-8 U367
    Carbosulfan Carbamic acid, [(dibutylamino)-
    thio] methyl-, 2,3-dihydro-2,2-
    dimethyl-7-benzofuranyl
    ((dibutylamino)thio)methyl-2,3-
    dihydro-2,2-dimethyl-7-benzo-
    furanyl ester
    55285-14-8 P189
    Carbon disulfide Same 75-15-0 P022
    Carbon oxyfluoride Carbonic difuoride 353-50-4 U033
    Carbon tetrachloride Methane, tetrachloro- 56-23-5 U211
    Chloral Acetaldehyde, trichloro- 75-87-6 U034
    Chlorambucil Benzenebutanoic acid, 4[bis-(2-
    chloroethyl)amino]- 4(bis-(2-
    chloroethyl)amino)-
    305-03-3 U035
    Chlordane 4,7-Methano-1H-indene,
    1,2,4,5,6,7,8,8-octachloro-
    2,3,3a,4,7,7a-hexahydro-
    57-74-9 U036
    Chlordane,
    α
    and
    γ
    isomers
    U036
    Chlorinated benzenes, N.O.S.
    Chlorinated ethane, N.O.S.
    Chlorinated fluorocarbons,
    N.O.S.
     
    Chlorinated naphthalene, N.O.S.
    Chlorinated phenol, N.O.S.
    Chlornaphazine Naphthalenamine, N,N'-bis(2-
    chloroethyl)-
    494-03-1 U026
    Chloroacetaldehyde Acetaldehyde, chloro- 107-20-0 P023
    Chloroalkyl ethers, N.O.S.
    p-Chloroaniline Benzenamine, 4-chloro- 106-47-8 P024
    Chlorobenzene Benzene, chloro- 108-90-7 U037
    Chlorobenzilate
    Benzeneacetic acid, 4-chloro-
    α
    -
    (4-chlorophenyl)-
    α
    -hydroxy-,
    ethyl ester
    510-15-6 U038
    p-Chloro-m-cresol Phenol, 4-chloro-3-methyl- 59-50-7 U039
    2-Chloroethyl vinyl ether Ethene, (2-chloroethoxy)- 110-75-8 U042
    Chloroform Methane, trichloro- 67-66-3 U044
    Chloromethyl methyl ether Methane, chloromethoxy- 107-30-2 U046
    β
    -Chloronaphthalene
    Naphthalene, 2-chloro- 91-58-7 U047
    o-Chlorophenol Phenol, 2-chloro- 95-57-8 U048
    1-(o-Chlorophenyl)thiourea Thiourea, (2-chlorophenyl)- 5344-82-1 P026

     
    209
    Chloroprene 1,3-Butadiene, 2-chloro- 126-99-8
    3-Chloropropionitrile Propanenitrile, 3-chloro- 542-76-7 P027
    Chromium Same 7440-47-3
    Chromium compounds, N.O.S.
    Chrysene Same 218-01-9 U050
    Citrus red No. 2 2-Naphthalenol, 1-[(2,5-
    dimethoxyphenyl)azo]- 1-((2,5-
    dimethoxyphenyl)azo)-
    6358-53-8
    Coal tar creosote Same 8007-45-2
    Copper cyanide Copper cyanide CuCN 544-92-3 P029
    Copper dimethyldithiocarbamate Copper, bis(dimethylcarbamo-
    dithioato-S,S')-,
    137-29-1
    Creosote Same U051
    p-Cresidine 2-Methoxy-5-
    methylbenzenamine
    120–71–8
      
    Cresols (Cresylic acid) Phenol, methyl- 1319-77-3 U052
    Crotonaldehyde 2-Butenal 4170-30-3 U053
    m-Cumenyl methylcarbamate Phenol, 3-(methylethyl)-, methyl
    carbamate
    64-00-6 P202
    Cyanides (soluble salts and
    complexes), N.O.S.
    P030
    Cyanogen Ethanedinitrile 460-19-5 P031
    Cyanogen bromide Cyanogen bromide (CN)Br 506-68-3 U246
    Cyanogen chloride Cyanogen chloride (CN)Cl 506-77-4 P033
    Cycasin
    β
    -D-glucopyranoside, (methyl-
    ONN-azoxy)methyl-
    14901-08-7
    Cycloate Carbamothioic acid, cyclohexyl-
    ethyl-, S-ethyl ester
    1134-23-2
    2-Cyclohexyl-4,6-dinitrophenol Phenol, 2-cyclohexyl-4,6-dinitro- 131-89-5 P034
    Cyclophosphamide 2H-1,3,2-Oxazaphosphorin-2-
    amine, N,N-bis(2-chloro-
    ethyl)tetrahydro-, 2-oxide N,N-
    bis(2-chloroethyl)tetrahydro-2-
    oxide
    50-18-0 U058
    2,4-D Acetic acid, (2,4-dichloro-
    phenoxy)-
    94-75-7 U240
    2,4-D, salts and esters Acetic acid, (2,4-
    dichlorophenoxy)-, salts and
    esters
    U240

     
    210
    Daunomycin 5, 12-Naphthacenedione, 8-
    acetyl-10-[(3-amino-2,3,6-
    trideoxy-
    α
    -L-lyxo-hexo-
    pyranosyl)oxy]-7,8,9,10-
    tetrahydro-6,8,11-trihydroxy-l-
    methoxy-, 8S-cis)- 8-acetyl-10-
    ((3-amino-2,3,6-trideoxy-
    α
    -L-
    lyxo-hexopyranosyl)oxy)-
    7,8,9,10-tetrahydro-6,8,11-tri-
    hydroxy-l-methoxy-, 8S-cis)-
    20830-81-3 U059
    Dazomet 2H-1,3,5-thiadiazine-2-thione,
    tetrahydro-3,5-dimethyl
    533-74-4
    DDD Benzene, 1,1'-(2,2-dichloroethyl-
    idene)bis[4-chloro- 1,1'-(2,2-
    dichloroethylidene)bis(4-chloro-
    72-54-8 U060
    DDE Benzene, 1,1'-(dichloroethenyl-
    idene)bis[4-chloro- 1,1'-
    (dichloroethenylidene)bis(4-
    chloro-
    72-55-9
    DDT Benzene, 1,1'-(2,2,2-trichloro-
    ethylidene)bis[4-chloro- 1,1'-
    (2,2,2-trichloroethylidene)bis(4-
    chloro-
    50-29-3 U061
    Diallate Carbamothioic acid, bis(1-
    methylethyl)-, S-(2,3-dichloro-2-
    propenyl) ester
    2303-16-4 U062
    Dibenz[a,h]acridine
    Dibenz(a,h)acridine
    Same 226-36-8
    Dibenz[a,j]acridine
    Dibenz(a,j)acridine
    Same 224-42-0
    Dibenz[a,h]anthracene
    Dibenz(a,h)anthracene
    Same 53-70-3 U063
    7H-Dibenzo[c,g]carbazole
    7H-Dibenzo(c,g)carbazole
    Same 194-59-2
    Dibenzo[a,e]pyrene
    Dibenzo(a,e)pyrene
    Naphtho[1,2,3,4-def]chrysene
    Naphtho(1,2,3,4-def)chrysene
    192-65-4
    Dibenzo[a,h]pyrene
    Dibenzo(a,h)pyrene
    Dibenzo[b,def]chryseneDibenzo(
    b,def)chrysene
    189-64-0
    Dibenzo[a,i]pyrene
    Dibenzo(a,i)pyrene
    Benzo[rst]pentaphene
    Benzo(rst)pentaphene
    189-55-9 U064
    1,2-Dibromo-3-chloropropane Propane, 1,2-dibromo-3-chloro- 96-12-8 U066
    Dibutyl phthalate 1,2-Benzenedicarboxylic acid,
    dibutyl ester
    84-74-2 U069
    o-Dichlorobenzene Benzene, 1,2-dichloro- 95-50-1 U070
    m-Dichlorobenzene Benzene, 1,3-dichloro- 541-73-1 U071
    p-Dichlorobenzene Benzene, 1,4-dichloro- 106-46-7 U072

     
    211
    Dichlorobenzene, N.O.S. Benzene, dichloro- 25321-22-6
    3,3'-Dichlorobenzidine [1,1'-Biphenyl]-4,4'-diamine,
    (1,1'-Biphenyl)-4,4'-diamine,
    3,3'-dichloro-
    91-94-1 U073
    1,4-Dichloro-2-butene 2-Butene, 1,4-dichloro- 764-41-0 U074
    Dichlorodifluoromethane Methane, dichlorodifluoro- 75-71-8 U075
    Dichloroethylene, N.O.S. Dichloroethylene 25323-30-2
    1,1-Dichloroethylene Ethene, 1,1-dichloro- 75-35-4 U078
    1,2-Dichloroethylene Ethene, 1,2-dichloro-, (E)- 156-60-5 U079
    Dichloroethyl ether Ethane, 1,1'-oxybis[2-chloro-
    1,1'-oxybis(2-chloro-
    111-44-4 U025
    Dichloroisopropyl ether Propane, 2,2'-oxybis[2-chloro-
    2,2'-oxybis(2-chloro-
    108-60-1 U027
    Dichloromethoxyethane Ethane, 1,1'-[methylenebis(oxy)-
    bis[2-chloro- 1,1'-(methylenebis-
    (oxy)bis(2-chloro-
    111-91-1 U024
    Dichloromethyl ether Methane, oxybis[chloro-
    oxybis(chloro-
    542-88-1 P016
    2,4-Dichlorophenol Phenol, 2,4-dichloro- 120-83-2 U081
    2,6-Dichlorophenol Phenol, 2,6-dichloro- 87-65-0 U082
    Dichlorophenylarsine Arsonous dichloride, phenyl- 696-28-6 P036
    Dichloropropane, N.O.S. Propane, dichloro- 26638-19-7
    Dichloropropanol, N.O.S. Propanol, dichloro- 26545-73-3
    Dichloropropene, N.O.S. 1-Propene, dichloro- 26952-23-8
    1,3-Dichloropropene 1-Propene, 1,3-dichloro- 542-75-6 U084
    Dieldrin 2,7:3,6-Dimethanonaphth[2, 3-b]-
    oxirene, 2,7:3,6-
    Dimethanonaphth(2, 3-b)oxirene,
    3,4,5,6,9,9-hexachloro-
    1a,2,2a,3,6, 6a,7,7a-octahydro-,
    (1a
    α
    ,2
    β
    ,2a
    α
    ,3
    β
    ,6
    β
    ,6a
    α
    ,7
    β
    ,7a
    α
    )-
    60-57-1 P037
    1,2:3,4-Diepoxybutane 2,2'-Bioxirane 1464-53-5 U085
    Diethylarsine Arsine, diethyl- 692-42-2 P038
    Diethylene glycol, dicarbamate Ethanol, 2,2'-oxybis-,
    dicarbamate
    5952-26-1 U395
    1,4-Diethyleneoxide 1,4-Dioxane 123-91-1 U108
    Diethylhexyl phthalate 1,2-Benzenedicarboxylic acid,
    bis(2-ethylhexyl) ester
    117-81-7 U028
    N,N'-Diethylhydrazine Hydrazine, 1,2-diethyl- 1615-80-1 U086
    O,O-Diethyl-S-methyl dithio-
    phosphate
    Phosphorodithioic acid, O,O-
    diethyl S-methyl ester
    3288-58-2 U087
    Diethyl-p-nitrophenyl phosphate Phosphoric acid, diethyl 4-nitro-
    phenyl ester
    311-45-5 P041
    Diethyl phthalate 1,2-Benzenedicarboxylic acid,
    diethyl ester
    84-66-2 U088

     
    212
    O,O-Diethyl O-pyrazinyl
    phosphorothioate
    Phosphorothioic acid, O,O-
    diethyl O-pyrazinyl ester
    297-97-2 P040
    Diethylstilbestrol Phenol, 4,4'-(1,2-diethyl-1,2-
    ethenediyl)bis-, (E)-
    56-53-1 U089
    Dihydrosafrole 1,3-Benzodioxole, 5-propyl- 94-58-6 U090
    Diisopropylfluorophosphate
    (DFP)
    Phosphorofluoridic acid, bis(1-
    methylethyl) ester
    55-91-4 P043
    Dimethoate Phosphorodithioic acid, O,O-
    dimethyl S-[2-(methylamino)-2-
    oxoethyl] O,O-dimethyl S-(2-
    (methylamino)-2-oxoethyl) ester
    60-51-5 P044
    Dimetilan Carbamic acid, dimethyl-, 1-
    [(dimethylamino) carbonyl]-5-
    methyl-1H-pyrazol-3-yl ester
    644-64-4 P191
    3,3'-Dimethoxybenzidine [1,1'-Biphenyl]-4,4'-diamine,
    (1,1'-Biphenyl)-4,4'-diamine,
    3,3'-dimethoxy-
    119-90-4 U091
    p-Dimethylaminoazobenzene Benzenamine, N,N-dimethyl-4-
    (phenylazo)-
    60-11-7 U093
    2,4-Dimethylaniline (2,4-xylidine) Benzenamine, 2,4-dimethyl- 95–68–1
      
    7,12-Dimethylbenz[a]anthracene
    7,12-Dimethylbenz(a)anthracene
    Benz[a]anthracene,
    Benz(a)anthracene, 7,12-
    dimethyl-
    57-97-6 U094
    3,3'-Dimethylbenzidine [1,1'-Biphenyl]-4,4'-diamine,
    (1,1'-Biphenyl)-4,4'-diamine,
    3,3'-dimethyl-
    119-93-7 U095
    Dimethylcarbamoyl chloride Carbamic chloride, dimethyl- 79-44-7 U097
    1,1-Dimethylhydrazine Hydrazine, 1,1-dimethyl- 57-14-7 U098
    1,2-Dimethylhydrazine Hydrazine, 1,2-dimethyl- 540-73-8 U099
    α
    ,
    α
    -Dimethylphenethylamine Benzeneethanamine,
    α
    ,
    α
    -
    dimethyl-
    122-09-8 P046
    2,4-Dimethylphenol Phenol, 2,4-dimethyl- 105-67-9 U101
    Dimethylphthalate 1,2-Benzenedicarboxylic acid,
    dimethyl ester
    131-11-3 U102
    Dimethyl sulfate Sulfuric acid, dimethyl ester 77-78-1 U103
    Dimetilan Carbamic acid, dimethyl-, 1-
    ((dimethylamino) carbonyl)-5-
    methyl-1H-pyrazol-3-yl ester
    644-64-4 P191
    Dinitrobenzene, N.O.S. Benzene, dinitro- 25154-54-5
    4,6-Dinitro-o-cresol Phenol, 2-methyl-4,6-dinitro- 534-52-1 P047
    4,6-Dinitro-o-cresol salts P047
    2,4-Dinitrophenol Phenol, 2,4-dinitro- 51-28-5 P048
    2,4-Dinitrotoluene Benzene, 1-methyl-2,4-dinitro- 121-14-2 U105
    2,6-Dinitrotoluene Benzene, 2-methyl-1,3-dinitro- 606-20-2 U106
    Dinoseb Phenol, 2-(1-methylpropyl)-4,6-
    dinitro-
    88-85-7 P020

     
    213
    Di-n-octyl phthalate 1,2-Benzenedicarboxylic acid,
    dioctyl ester
    117-84-0 U107
    Diphenylamine Benzenamine, N-phenyl- 122-39-4
    1,2-Diphenylhydrazine Hydrazine, 1,2-diphenyl- 122-66-7 U109
    Di-n-propylnitrosamine 1-Propanamine, N-nitroso-N-
    propyl-
    621-64-7 U111
    Disulfiram Thioperoxydicarbonic diamide,
    tetraethyl
    97-77-8
    Disulfoton Phosphorodithioic acid, O,O-
    diethyl S-[2-(ethylthio)ethyl] S-
    (2-(ethylthio)ethyl) ester
    298-04-4 P039
    Dithiobiuret Thioimidodicarbonic diamide
    [(H2N)C(S)]2NH((H2N)C(S))2NH
    541-53-7 P049
    Endosulfan 6, 9-Methano-2,4,3-benzodioxa-
    thiepen,6,7,8,9,10,10-hexachloro-
    1,5,5a,6,9,9a-hexahydro-, 3-
    oxide,
    115-29-7 P050
    Endothal 7-Oxabicyclo[2.2.1]heptane-2,3-
    dicarboxylic acid
    7-Oxabicyclo(2.2.1)heptane-2,3-
    dicarboxylic acid
    145-73-3 P088
    Endrin 2,7:3,6-Dimethanonaphth[2,3-b]-
    oxirene, 2,7:3,6-
    Dimethanonaphth(2,3-b)oxirene,
    3,4,5,6,9,9-hexachloro-
    1a,2,2a,3,6,6a,7,7a-octahydro-,
    (1a
    α
    ,2
    β
    ,2a
    β
    ,3
    α
    ,6
    α
    ,6a
    β
    ,7
    β
    ,7a
    α
    )-
    ,
    72-20-8 P051
    Endrin metabolites P051
    Epichlorohydrin Oxirane, (chloromethyl)- 106-89-8 U041
    Epinephrine 1,2-Benzenediol, 4-[1-hydroxy-2-
    (methylamino)ethyl]-, 4-(1-
    hydroxy-2-(methylamino)ethyl)-,
    (R)-
    51-43-4 P042
    EPTC Carbamothioic acid, dipropyl-, S-
    ethyl ester
    759-94-4
    Ethyl carbamate (urethane) Carbamic acid, ethyl ester 51-79-6 U238
    Ethyl cyanide Propanenitrile 107-12-0 P101
    Ethylenebisdithiocarbamic acid Carbamodithioic acid, 1,2-
    ethanediylbis-
    111-54-6 U114
    Ethylenebisdithiocarbamic acid,
    salts and esters
    U114
    Ethylene dibromide Ethane, 1,2-dibromo- 106-93-4 U067
    Ethylene dichloride Ethane, 1,2-dichloro- 107-06-2
    Ethylene glycol monoethyl ether Ethanol, 2-ethoxy- 110-80-5 U359
    Ethyleneimine Aziridine 151-56-4 P054

     
    214
    Ethylene oxide Oxirane 75-21-8 U115
    Ethylenethiourea 2-Imidazolidinethione 96-45-7 U116
    Ethylidine dichloride Ethane, 1,1-dichloro- 75-34-3 U076
    Ethyl methacrylate 2-Propenoic acid, 2-methyl-,
    ethyl ester
    97-63-2 U118
    Ethyl methanesulfonate Methanesulfonic acid, ethyl ester 62-50-0 U119
    Ethyl Ziram Zinc, bis(diethylcarbamo-
    dithioato-S,S')-
    14324-55-1 U407
    Famphur Phosphorothioc acid, O-[4-
    [(dimethylamino)sulfonyl]-
    phenyl] O-(4-
    ((dimethylamino)sulfonyl)-
    phenyl) O,O-dimethyl ester
    52-85-7 P097
    Ferbam Iron, tris(dimethylcarbamo-
    dithioato-S,S')-,
    14484-64-1
    Fluoranthene Same 206-44-0 U120
    Fluorine Same 7782-41-4 P056
    Fluoroacetamide Acetamide, 2-fluoro- 640-19-7 P057
    Fluoroacetic acid, sodium salt Acetic acid, fluoro-, sodium salt 62-74-8 P058
    Formaldehyde Same 50-00-0 U122
    Formetanate hydrochloride Methanimidamide, N,N-
    dimethyl-N'-[3-[[(methylamino)-
    carbonyl]oxy]phenyl]- N,N-
    dimethyl-N'-(3-(((methylamino)-
    carbonyl)oxy)phenyl)-, mono-
    hydrochloride
    23422-53-9 P198
    Formic acid Same 64-18-16 U123
    Formparanate Methanimidamide, N,N-
    dimethyl-N'-[2-methyl-4-
    [[(methylamino)carbonyl]oxy]-
    phenyl]- N,N-dimethyl-N'-(2-
    methyl-4-(((methylamino)-
    carbonyl)oxy)phenyl)-
    17702-57-7 P197
    Glycidylaldehyde Oxiranecarboxaldehyde 765-34-4 U126
    Halomethanes, N.O.S.
    Heptachlor 4,7-Methano-1H-
    indene,1,4,5,6,7,8,8-heptachloro-
    3a,4,7,7a-tetrahydro-
    76-44-8 P059
    Heptachlor epoxide 2,5-Methano-2H-indeno[1,
    2b]oxirene, 2,5-Methano-2H-
    indeno(1, 2b)oxirene,
    2,3,4,5,6,7,7-heptachloro-
    1a,1b,5,5a,6,6a-hexahydro-,
    (1a
    α
    ,1b
    β
    ,2
    α
    ,5
    α
    ,5a
    β
    ,6
    β
    ,6a
    α
    )-
    1024-57-3
    Heptachlor epoxide (
    α
    ,
    β
    , and
    γ
     
    isomers)
     

     
    215
    Heptachlorodibenzofurans
    Heptachlorodibenzo-p-dioxins
    Hexachlorobenzene Benzene, hexachloro- 118-74-1 U127
    Hexachlorobutadiene 1,3-Butadiene, 1,1,2,3,4,4-hexa-
    chloro-
    87-68-3 U128
    Hexachlorocyclo-pentadiene 1,3-Cyclopentadiene, 1,2,3,4,5,5-
    hexachloro-
    77-47-4 U130
    Hexachlorodibenzo-p-dioxins
    Hexachlorodibenzofurans
    Hexachloroethane Ethane, hexachloro- 67-72-1 U131
    Hexachlorophene Phenol, 2,2'-methylenebis[3,4,6-
    trichloro- 2,2'-methylene-
    bis(3,4,6-trichloro-
    70-30-4 U132
    Hexachloropropene 1-Propene, 1,1,2,3,3,3-
    hexachloro-
    1888-71-7 U243
    Hexaethyltetraphosphate Tetraphosphoric acid, hexaethyl
    ester
    757-58-4 P062
    Hydrazine Same 302-01-2 U133
    Hydrogen cyanide Hydrocyanic acid 74-90-8 P063
    Hydrogen fluoride Hydrofluoric acid 7664-39-3 U134
    Hydrogen sulfide Hydrogen sulfide H2S 7783-06-4 U135
    Indeno[1,2,3-cd]pyrene
    Indeno(1,2,3-cd)pyrene
    Same 193-39-5 U137
    3-Iodo-2-propynyl-n-butyl-
    carbamate
    Carbamic acid, butyl-, 3-iodo-2-
    propynyl ester
    55406-53-6
    Isobutyl alcohol 1-Propanol, 2-methyl- 78-83-1 U140
    Isodrin 1,4:5,8-Dimethanonaph-
    thalene,1,2,3,4,10,10-hexachloro-
    1,4,4a,5,8,8a-hexahydro-,
    (1
    α
    ,4
    α
    ,4a
    β
    ,5
    β
    ,8
    β
    ,8a
    β
    )-,
    465-73-6 P060
    Isolan Carbamic acid, dimethyl-, 3-
    methyl-1-(1-methylethyl)-1H-
    pyrazol-5-yl ester
    119-38-0 P192
    Isosafrole 1,3-Benzodioxole, 5-(1-
    propenyl)-
    120-58-1 U141
    Kepone 1,3,4-Metheno-2H-cyclobuta[cd]-
    pentalen-2-one, 1,3,4-Metheno-
    2H-cyclobuta(cd)pentalen-2-one,
    1,1a,3,3a,4,5,5,5a,5b,6-
    decachlorooctahydro-,
    143-50-0 U142

     
    216
    Lasiocarpine 2-Butenoic acid, 2-methyl-, 7-
    [[2,3-dihydroxy-2-(1-
    methoxyethyl)-3-methyl-1-
    oxobutoxy]methyl]-2,3,5,7a-
    tetrahydro-1H-pyrrolizin-l-yl
    ester, [1S-[1-
    α
    (Z),7(2S*,3R*),7a
    α
    ]]- 2-
    methyl-, 7-((2,3-dihydroxy-2-(1-
    methoxyethyl)-3-methyl-1-
    oxobutoxy)methyl)-2,3,5,7a-
    tetrahydro-1H-pyrrolizin-l-yl
    ester, (1S-(1-
    α
    (Z),7(2S*,3R*),7a
    α
    ))-
    303-34-1 U143
    Lead Same 7439-92-1
    Lead and compounds, N.O.S.
    Lead acetate Acetic acid, lead (2+) salt 301-04-2 U144
    Lead phosphate Phosphoric acid, lead (2+) salt
    (2:3)
    7446-27-7 U145
    Lead subacetate Lead, bis(acetato-O)tetra-
    hydroxytri-
    1335-32-6 U146
    Lindane Cyclohexane, 1,2,3,4,5,6-hexa-
    chloro-, 1
    α
    ,2
    α
    ,3
    β
    ,4
    α
    ,5
    α
    ,6
    β
    )-
    58-89-9 U129
    Maleic anhydride 2,5-Furandione 108-31-6 U147
    Maleic hydrazide 3,6-Pyridazinedione, 1,2-dihydro- 123-33-1 U148
    Malononitrile Propanedinitrile 109-77-3 U149
    Manganese dimethyldithio-
    carbamate
    Manganese, bis(dimethyl-
    carbamodithioato-S,S')-,
    15339-36-3 P196
    Melphalan L-Phenylalanine, 4-[bis(2-chloro-
    ethyl)amino]- 4-(bis(2-chloro-
    ethyl)amino)-
    148-82-3 U150
    Mercury Same 7439-97-6 U151
    Mercury compounds, N.O.S.
    Mercury fulminate Fulminic acid, mercury (2+) salt 628-86-4 P065
    Metam Sodium Carbamodithioic acid, methyl-,
    monosodium salt
    137-42-8
    Methacrylonitrile 2-Propenenitrile, 2-methyl- 126-98-7 U152
    Methapyrilene 1,2-Ethanediamine, N,N-
    dimethyl-N'-2-pyridinyl-N'-(2-
    thienylmethyl)-
    91-80-5 U155
    Methiocarb Phenol, (3,5-dimethyl-4-
    (methylthio)-, methylcarbamate
    2032-65-7 P199
    Metholmyl Ethanimidothioic acid, N-
    [[(methylamino)carbonyl]oxy]-,
    N-(((methyl-
    amino)carbonyl)oxy)-, methyl
    ester
    16752-77-5 P066

     
    217
    Methoxychlor Benzene, 1,1'-(2,2,2-trichloro-
    ethylidene)bis[4-methoxy- 1,1'-
    (2,2,2-trichloroethylidene)bis(4-
    methoxy-
    72-43-5 U247
    Methyl bromide Methane, bromo- 74-83-9 U029
    Methyl chloride Methane, chloro- 74-87-3 U045
    Methylchlorocarbonate Carbonochloridic acid, methyl
    ester
    79-22-1 U156
    Methyl chloroform Ethane, 1,1,1-trichloro- 71-55-6 U226
    3-Methylcholanthrene Benz[j]aceanthrylene,
    Benz(j)aceanthrylene, 1,2-
    dihydro-3-methyl-
    56-49-5 U157
    4,4'-Methylenebis(2-chloro-
    aniline)
    Benzenamine, 4,4'-methylene-
    bis[2-chloro- 4,4'-methylene-
    bis(2-chloro-
    101-14-4 U158
    Methylene bromide Methane, dibromo- 74-95-3 U068
    Methylene chloride Methane, dichloro- 75-09-2 U080
    Methyl ethyl ketone (MEK) 2-Butanone 78-93-3 U159
    Methyl ethyl ketone peroxide
    2-Butanone, peroxide 1338-23-4 U160
    Methyl hydrazine Hydrazine, methyl- 60-34-4 P068
    Methyl iodide Methane, iodo- 74-88-4 U138
    Methyl isocyanate Methane, isocyanato- 624-83-9 P064
    2-Methyllactonitrile Propanenitrile, 2-hydroxy-2-
    methyl-
    75-86-5 P069
    Methyl methacrylate 2-Propenoic acid, 2-methyl-,
    methyl ester
    80-62-6 U162
    Methyl methanesulfonate Methanesulfonic acid, methyl
    ester
    66-27-3
    Methyl parathion Phosphorothioic acid, O,O-
    dimethyl O-(4-nitrophenyl) ester
    298-00-0 P071
    Methylthiouracil 4-(1H)-Pyrimidinone, 2,3-
    dihydro-6-methyl-2-thioxo-
    56-04-2 U164
    Metolcarb Carbamic acid, methyl-, 3-
    methylphenyl ester
    1129-41-5 P190
    Mexacarbate Phenol, 4-(dimethylamino)-3,5-
    dimethyl-, methylcarbamate
    (ester)
    315-18-4 P128

     
    218
    Mitomycin C Azirino[2', 3':3, 4]pyrrolo[1, 2-
    a]indole-4, 7-dione, 6-amino-8-
    [[(aminocarbonyl)oxy]methyl]-
    1,1a,2,8,8a,8b-hexahydro-8a-
    methoxy-5-methyl-, [1a-S-
    (1a
    α
    ,8
    β
    ,8a
    α
    ,8b
    α
    )]-,Azirino(2',
    3':3, 4)pyrrolo(1, 2-a)indole-4, 7-
    dione, 6-amino-8-(((amino-
    carbonyl)oxy)methyl)-
    1,1a,2,8,8a,8b-hexahydro-8a-
    methoxy-5-methyl-, (1a-S-
    (1a
    α
    ,8
    β
    ,8a
    α
    ,8b
    α
    ))-,
    50-07-7 U010
    Molinate 1H-Azepine-1-carbothioic acid,
    hexahydro-, S-ethyl ester
    2212-67-1
    MNNG Guanidine, N-methyl-N'-nitro-N-
    nitroso-
    70-25-7 U163
    Mustard gas Ethane, 1,1'-thiobis[2-chloro-
    1,1'-thiobis(2-chloro-
    505-60-2 U165
    Naphthalene Same 91-20-3 U165
    1,4-Naphthoquinone 1,4-Naphthalenedione 130-15-4 U166
    α
    -Naphthylamine
    1-Naphthalenamine 134-32-7 U167
    β
    -Naphthylamine
    2-Naphthalenamine 91-59-8 U168
    α
    -Naphthylthiourea
    Thiourea, 1-naphthalenyl- 86-88-4 P072
    Nickel Same 7440-02-0
    Nickel compounds, N.O.S.
    Nickel carbonyl Nickel carbonyl Ni(CO)4, (T-4)- 13463-39-3 P073
    Nickel cyanide Nickel cyanide Ni(CN)2 557-19-7 P074
    Nicotine Pyridine, 3-(1-methyl-2-
    pyrrolidinyl)-, (S)-
    54-11-5 P075
    Nicotine salts P075
    Nitric oxide Nitrogen oxide NO 10102-43-9 P076
    p-Nitroaniline Benzenamine, 4-nitro- 100-01-6 P077
    Nitrobenzene Benzene, nitro- 98-95-3 P078
    Nitrogen dioxide Nitrogen oxide NO2 10102-44-0 P078
    Nitrogen mustard Ethanamine, 2-chloro-N-(2-
    chloroethyl)-N-methyl-
    51-75-2
    Nitrogen mustard, hydrochloride
    salt
     
    Nitrogen mustard N-oxide Ethanamine, 2-chloro-N-(2-
    chloroethyl)-N-methyl-, N-oxide
    126-85-2
    Nitrogen mustard, N-oxide,
    hydrochloride salt
     
    Nitroglycerin 1,2,3-Propanetriol, trinitrate 55-63-0 P081
    p-Nitrophenol Phenol, 4-nitro- 100-02-7 U170
    2-Nitropropane Propane, 2-nitro- 79-46-9 U171
    Nitrosamines, N.O.S. 35576-91-1

     
    219
    N-Nitrosodi-n-butylamine 1-Butanamine, N-butyl-N-
    nitroso-
    924-16-3 U172
    N-Nitrosodiethanolamine Ethanol, 2,2'-(nitrosoimino)bis- 1116-54-7 U173
    N-Nitrosodiethylamine Ethanamine, N-ethyl-N-nitroso- 55-18-5 U174
    N-Nitrosodimethylamine Methanamine, N-methyl-N-
    nitroso-
    62-75-9 P082
    N-Nitroso-N-ethylurea Urea, N-ethyl-N-nitroso- 759-73-9 U176
    N-Nitrosomethylethylamine Ethanamine, N-methyl-N-nitroso- 10595-95-6
    N-Nitroso-N-methylurea Urea, N-methyl-N-nitroso- 684-93-5 U177
    N-Nitroso-N-methylurethane Carbamic acid, methylnitroso-,
    ethyl ester
    615-53-2 U178
    N-Nitrosomethylvinylamine Vinylamine, N-methyl-N-nitroso- 4549-40-0 P084
    N-Nitrosomorpholine Morpholine, 4-nitroso- 59-89-2
    N-Nitrosonornicotine Pyridine, 3-(1-nitroso-2-
    pyrrolidinyl)-, (S)-
    16543-55-8
    N-Nitrosopiperidine Piperidine, 1-nitroso- 100-75-4 U179
    N-Nitrosopyrrolidine Pyrrolidine, 1-nitroso- 930-55-2 U180
    N-Nitrososarcosine Glycine, N-methyl-N-nitroso- 13256-22-9
    5-Nitro-o-toluidine Benzenamine, 2-methyl-5-nitro- 99-55-8 U181
    Octachlorodibenzo-p-dioxin
    (OCDD)
    1,2,3,4,6,7,8,9-Octachloro-
    dibenzo-p-dioxin.
    3268-87-9
    Octachlorodibenzofuran (OCDF) 1,2,3,4,6,7,8,9-Octachloro-
    dibenzofuran.
    39001-02-0
    Octamethylpyrophosphoramide Diphosphoramide, octamethyl- 152-16-9 P085
    Osmium tetroxide Osmium oxide OsO4, (T-4) 20816-12-0 P087
    Oxamyl Ethanimidothioc acid, 2-
    (dimethylamino)-N-[[(methyl-
    amino)carbonyl]oxy]-2-oxo-, 2-
    (dimethylamino)-N-(((methyl-
    amino)carbonyl)oxy)-2-oxo-,
    methyl ester
    23135-22-0 P194
    Paraldehyde 1,3,5-Trioxane, 2,4,6-trimethyl- 123-63-7 U182
    Parathion Phosphorothioic acid, O,O-
    diethyl O-(4-nitrophenyl) ester
    56-38-2 P089
    Pebulate Carbamothioic acid, butylethyl-,
    S-propyl ester
    1114-71-2
    Pentachlorobenzene Benzene, pentachloro- 608-93-5 U183
    Pentachlorodibenzo-p-dioxins
    Pentachlorodibenzofurans
    Pentachloroethane Ethane, pentachloro- 76-01-7 U184
    Pentachloronitrobenzene (PCNB) Benzene, pentachloronitro- 82-68-8 U185
    Pentachlorophenol Phenol, pentachloro- 87-86-5 See F027
    Phenacetin Acetamide, N-(4-ethoxyphenyl)- 62-44-2 U187
    Phenol Same 108-95-2 U188
    Phenylenediamine Benzenediamine 25265-76-3
    1,2-Phenylenediamine 1,2-Benzenediamine 95–54–5
      

     
    220
    1,3-Phenylenediamine 1,3-Benzenediamine 108–45–2
      
    Phenylmercury acetate Mercury, (acetato-O)phenyl- 62-38-4 P092
    Phenylthiourea Thiourea, phenyl- 103-85-5 P093
    Phosgene Carbonic dichloride 75-44-5 P095
    Phosphine Same 7803-51-2 P096
    Phorate Phosphorodithioic acid, O,O-
    diethyl S-[(ethylthio)methyl]
    O,O-diethyl S-((ethylthio)methyl)
    ester
    298-02-2 P094
    Phthalic acid esters, N.O.S.
    Phthalic anhydride 1,3-Isobenzofurandione 85-44-9 U190
    Physostigmine Pyrrolo[2,3-b]indol-5-ol, Pyrrolo-
    (2,3-b)indol-5-ol, 1,2,3,3a,8,8a-
    hexahydro-1,3a,8-trimethyl-,
    methylcarbamate (ester), (3aS-
    cis)-
    57-47-6 P204
    Physostigmine salicylate Benzoic acid, 2-hydroxy-,
    compound with (3aS-cis)-
    1,2,3,3a,8,8a-hexahydro-1,3a,8-
    trimethylpyrrolo[2,3-b]indol-5-yl
    methylcarbamate (3aS-cis)-
    1,2,3,3a,8,8a-hexahydro-1,3a,8-
    trimethylpyrrolo(2,3-b)indol-5-yl
    methylcarbamate ester (1:1)
    57-64-7 P188
    2-Picoline Pyridine, 2-methyl- 109-06-8 U191
    Polychlorinated biphenyls,
    N.O.S.
     
    Potassium cyanide Same 151-50-8 P098
    Potassium dimethyldithio-
    carbamate
    Carbamodithioc acid, dimethyl,
    potassium salt
    128-03-0
    Potassium n-hydroxymethyl-n-
    methyl-dithiocarbamate
    Carbamodithioc acid, (hydroxy-
    methyl)methyl-, monopotassium
    salt
    51026-28-9
    Potassium n-methyldithio-
    carbamate
    Carbamodithioc acid, methyl-
    monopotassium salt
    137-41-7
    Potassium silver cyanide Argentate(1-), bis(cyano-C)-,
    potassium)
    506-61-6 P099
    Potassium pentachlorophenate Pentachlorophenol, potassium
    salt
    7778736 None
    Promecarb Phenol, 3-methyl-5-(1-methyl-
    ethyl)-, methyl carbamate
    2631-37-0 P201
    Pronamide Benzamide, 3,5-dichloro-N-(1,1-
    dimethyl-2-propynyl)-
    23950-58-5 U192
    1,3-Propane sultone 1,2-Oxathiolane, 2,2-dioxide 1120-71-4 U193
    Propham Carbamic acid, phenyl-, 1-
    methylethyl ester
    122-42-9 U373

     
    221
    Propoxur Phenol, 2-(1-methylethoxy)-,
    methylcarbamate
    114-26-1 U411
    n-Propylamine 1-Propanamine 107-10-8 U194
    Propargyl alcohol 2-Propyn-1-ol 107-19-7 P102
    Propylene dichloride Propane, 1,2-dichloro- 78-87-5 U083
    1,2-Propylenimine Aziridine, 2-methyl- 75-55-8 P067
    Propylthiouracil 4(1H)-Pyrimidinone, 2,3-
    dihydro-6-propyl-2-thioxo-
    51-52-5
    Prosulfocarb Carbamothioic acid, dipropyl-, S-
    (phenylmethyl) ester
    52888-80-9 U387
    Pyridine Same 110-86-1 U196
    Reserpine Yohimban-16-carboxylic acid,
    11,17-dimethoxy-18-[(3,4,5-tri-
    methoxybenzoyl)oxy]-, 11,17-
    dimethoxy-18-((3,4,5-trimeth-
    oxybenzoyl)oxy)-, methyl ester,
    (3
    β
    ,16
    β
    ,17
    α
    ,18
    β
    ,20
    α
    )-,
    50-55-5 U200
    Resorcinol 1,3-Benzenediol 108-46-3 U201
    Saccharin 1,2-Benzisothiazol-3(2H)-one,
    1,1-dioxide
    81-07-2 U202
    Saccharin salts U202
    Safrole 1,3-Benzodioxole, 5-(2-
    propenyl)-
    94-59-7 U203
    Selenium Same 7782-49-2
    Selenium compounds, N.O.S.
    Selenium dioxide Selenious acid 7783-00-8 U204
    Selenium sulfide Selenium sulfide SeS2 7488-56-4 U205
    Selenium, tetrakis(dimethyl-
    dithiocarbamate
    Carbamodithioic acid, dimethyl-,
    tetraanhydrosulfide with ortho-
    thioselenious acid
    144-34-3
    Selenourea Same 630-10-4 P103
    Silver Same 7440-22-4
    Silver compounds, N.O.S.
    Silver cyanide Silver cyanide AgCN 506-64-9 P104
    Silvex (2,4,5-TP) Propanoic acid, 2-(2,4,5-
    trichlorophenoxy)-
    93-72-1 See F027
    Sodium cyanide Sodium cyanide NaCN 143-33-9 P106
    Sodium dibutyldithiocarbamate Carbamodithioic acid, dibutyl-,
    sodium salt
    136-30-1
    Sodium diethyldithiocarbamate Carbamodithioic acid, diethyl-,
    sodium salt
    148-18-5
    Sodium dimethyldithiocarbamate Carbamodithioic acid, dimethyl-,
    sodium salt
    128-04-1
    Sodium pentachlorophenate Pentachlorophenol, sodium salt 131522 None

     
    222
    Streptozotocin D-Glucose, 2-deoxy-2-[[(methyl-
    nitrosoamino)carbonyl]amino]-
    2-deoxy-2-(((methylnitroso-
    amino)carbonyl)amino)-
    18883-66-4 U206
    Strychnine Strychnidin-10-one 57-24-9 P108
    Strychnine salts P108
    Sulfallate Carbamodithioic acid, diethyl-, 2-
    chloro-2-propenyl ester
    95-06-7
    TCDD Dibenzo[b,e][1,4]dioxin,
    Dibenzo(b,e)(1,4)dioxin, 2,3,7,8-
    tetrachloro-
    1746-01-6
    Tetrabutylthiuram disulfide Thioperoxydicarbonic diamide,
    tetrabutyl
    1634-02-2
    Tetramethylthiuram monosulfide Bis(dimethylthiocarbamoyl)
    sulfide
    97-74-5
    1,2,4,5-Tetrachlorobenzene Benzene, 1,2,4,5-tetrachloro- 95-94-3 U207
    Tetrachlorodibenzo-p-dioxins
    Tetrachlorodibenzofurans
    Tetrachloroethane, N.O.S. Ethane, tetrachloro-, N.O.S. 25322-20-7
    1,1,1,2-Tetrachloroethane Ethane, 1,1,1,2-tetrachloro- 630-20-6 U208
    1,1,2,2-Tetrachloroethane Ethane, 1,1,2,2-tetrachloro- 79-34-5 U209
    Tetrachloroethylene Ethene, tetrachloro- 127-18-4 U210
    2,3,4,6-Tetrachlorophenol Phenol, 2,3,4,6-tetrachloro- 58-90-2 See F027
    2,3,4,6-Tetrachlorophenol,
    potassium salt
    Same 53535276 None
    2,3,4,6-Tetrachlorophenol,
    sodium salt
    Same 25567559 None
    Tetraethyldithiopyrophosphate Thiodiphosphoric acid, tetraethyl
    ester
    3689-24-5 P109
    Tetraethyl lead Plumbane, tetraethyl- 78-00-2 P110
    Tetraethylpyrophosphate Diphosphoric acid, tetraethyl
    ester
    107-49-3 P111
    Tetranitromethane Methane, tetranitro- 509-14-8 P112
    Thallium Same 7440-28-0
    Thallium compounds
    Thallic oxide Thallium oxide Tl2O3 1314-32-5 P113
    Thallium (I) acetate Acetic acid, thallium (1+) salt 563-68-8 U214
    Thallium (I) carbonate Carbonic acid, dithallium (1+)
    salt
    6533-73-9 U215
    Thallium (I) chloride Thallium chloride TlCl 7791-12-0 U216
    Thallium (I) nitrate Nitric acid, thallium (1+) salt 10102-45-1 U217
    Thallium selenite Selenious acid, dithallium (1+)
    salt
    12039-52-0 P114
    Thallium (I) sulfate Sulfuric acid, dithallium (1+) salt 7446-18-6 P115
    Thioacetamide Ethanethioamide 62-55-5 U218

     
    223
    Thiodicarb Ethanimidothioic acid, N,N'-
    [thiobis[(methylimino)-
    carbonyloxy]]-bis-, N,N'-
    (thiobis((methylimino)-
    carbonyloxy))-bis-, dimethyl
    ester
    59669-26-0 U410
    Thiofanox 2-Butanone, 3,3-dimethyl-1-
    (methylthio)-, O-
    [(methylamino)carbonyl]oxime
    O-((methylamino)carbonyl)-
    oxime
    39196-18-4 P045
    Thiophanate-methyl Carbamic acid, [1,2-
    phyenylenebis(iminocarbono-
    thioyl)]-bis-, (1,2-
    phyenylenebis(iminocarbono-
    thioyl))-bis-, dimethyl ester
    23564-05-8 U409
    Thiomethanol Methanethiol 74-93-1 U153
    Thiophenol Benzenethiol 108-98-5 P014
    Thiosemicarbazide Hydrazinecarbothioamide 79-19-6 P116
    Thiourea Same 62-56-6 P219
    Thiram Thioperoxydicarbonic diamide
    [(H2N)C(S)]2S2, ((H2N)C(S))2S2,
    tetramethyl-
    137-26-8 U244
    Tirpate 1,3-Dithiolane-2-carboxaldehyde,
    2,4-dimethyl-, O-[(methylamino)-
    carbonyl] oxime O-((methyl-
    amino)carbonyl)oxime
    26419-73-8 P185
    Toluene Benzene, methyl- 108-88-3 U220
    Toluenediamine Benzenediamine, ar-methyl- 25376-45-8 U221
    Toluene-2,4-diamine 1,3-Benzenediamine, 4-methyl- 95-80-7
    Toluene-2,6-diamine 1,3-Benzenediamine, 2-methyl- 823-40-5
    Toluene-3,4-diamine 1,2-Benzenediamine, 4-methyl- 496-72-0
    Toluene diisocyanate Benzene, 1,3-diisocyanato-
    methyl-
    26471-62-5 U223
    o-Toluidine Benzenamine, 2-methyl- 95-53-4 U328
    o-Toluidine hydrochloride Benzeneamine, 2-methyl-, hydro-
    chloride
    636-21-5 U222
    p-Toluidine Benzenamine, 4-methyl- 106-49-0 U353
    Toxaphene Same 8001-35-2 P123
    Triallate Carbamothioic acid, bis(1-
    methylethyl)-, S-(2,3,3-trichloro-
    2-propenyl) ester
    2303-17-5 U389
    1,2,4-Trichlorobenzene Benzene, 1,2,4-trichloro- 120-82-1
    1,1,2-Trichloroethane Ethane, 1,1,2-trichloro- 79-00-5 U227
    Trichloroethylene Ethene, trichloro- 79-01-6 U228
    Trichloromethanethiol Methanethiol, trichloro- 75-70-7 P118

     
    224
    Trichloromonofluoromethane Methane, trichlorofluoro- 75-69-4 U121
    2,4,5-Trichlorophenol Phenol, 2,4,5-trichloro- 95-95-4 See F027
    2,4,6-Trichlorophenol Phenol, 2,4,6-trichloro- 88-06-2 See F027
    2,4,5-T Acetic acid, (2,4,5-trichloro-
    phenoxy)-
    93-76-5 See F027
    Trichloropropane, N.O.S. 25735-29-9
    1,2,3-Trichloropropane Propane, 1,2,3-trichloro- 96-18-4
    Triethylamine Ethanamine, N,N-diethyl- 121-44-8 U404
    O,O,O-Triethylphosphorothioate
    Phosphorothioic acid, O,O,O-
    triethyl ester
    126-68-1
    1,3,5-Trinitrobenzene Benzene, 1,3,5-trinitro- 99-35-4 U234
    Tris(l-aziridinyl)phosphine
    sulfide
    Aziridine, 1,1',1”-phosphino-
    thioylidynetris-
    52-24-4
    Tris(2,3-dibromopropyl)
    phosphate
    1-Propanol, 2,3-dibromo-,
    phosphate (3:1)
    126-72-7 U235
    Trypan blue 2,7-Naphthalenedisulfonic acid,
    3,3'-[(3,3'-dimethyl[1,1'-
    biphenyl]-4,4'-diyl)-
    bis(azo)]bis[5-amino-4-
    hydroxy]-, 3,3'-((3,3'-dimethyl-
    (1,1'-biphenyl)-4,4'-diyl)-
    bis(azo))bis(5-amino-4-
    hydroxy)-, tetrasodium salt
    72-57-1 U236
    Uracil mustard 2,4-(1H,3H)-Pyrimidinedione, 5-
    [bis(2-chloroethyl)amino]- 5-
    (bis(2-chloroethyl)amino)-
    66-75-1 U237
    Vanadium pentoxide Vanadium oxide V2O5 1314-62-1 P120
    Vernolate Carbamothioc acid, dipropyl-, S-
    propyl ester
    1929-77-7
    Vinyl chloride Ethene, chloro- 75-01-4 U043
    Warfarin 2H-1-Benzopyran-2-one, 4-
    hydroxy-3-(3-oxo-1-phenyl-
    butyl)-, when present at
    concentrations less than 0.3
    percent
    81-81-2 U248
    Warfarin 2H-1-Benzopyran-2-one, 4-
    hydroxy-3-(3-oxo-1-phenyl-
    butyl)-, when present at
    concentrations greater than 0.3
    percent
    81-81-2 P001
    Warfarin salts, when present at
    concentrations less than 0.3
    percent
    U248
    Warfarin salts, when present at
    concentrations greater than 0.3
    percent
    P001

     
    225
    Zinc cyanide Zinc cyanide Zn(CN)2 557-21-1 P121
    Zinc phosphide Zinc phosphide P2Zn3, when
    present at concentrations greater
    than 10 percent
    1314-84-7 P122
    Zinc phosphide Zinc phosphide P2Zn3, when
    present at concentrations of 10
    percent or less
    1314-84-7 U249
    Ziram Zinc, bis(dimethylcarbamo-
    dithioato-S,S')- (T-4)-
    137-30-4 P205
     
    Note: The abbreviation N.O.S. (not otherwise specified) signifies those members of the general
    class that are not specifically listed by name in this Section.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.Appendix I Wastes Excluded by Administrative Action
     
    Table A Wastes Excluded by USEPA under pursuant to 40 CFR 260.20 and 260.22 from
    Non-Specific Sources
     
     
    Facility Address Waste Description
     
     
    (None excluded from an Illinois source at this time)
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.Appendix I Wastes Excluded by Administrative Action
     
    Table B Wastes Excluded by USEPA under pursuant to 40 CFR 260.20 and 260.22 from
    Specific Sources
     
     
    Facility Address Waste Description
     
    Amoco Oil Company
    Wood River, Illinois
    150 million gallons of DAF float from petroleum refining
    contained in four surge ponds after treatment with the
    Chemfix stabilization process. This waste contains USEPA
    hazardous waste number K048. This exclusion applies to
    the 150 million gallons of waste after chemical stabilization
    as long as the mixing ratios of the reagent with the waste
    are monitored continuously and do not vary outside of the
    limits presented in the demonstration samples and one grab
    sample is taken each hour from each treatment unit,
    composited, and TCLP tests performed on each sample. If

     
    226
    the levels of lead or total chromium exceed 0.5 ppm in the
    EP extract, then the waste that was processed during the
    compositing period is considered hazardous; the treatment
    residue must be pumped into bermed cells to ensure that
    the waste is identifiable in the event that removal is
    necessary.
     
    Conversion Systems, Inc.
    Horsham, Pennsylvania
    (Sterling, Illinois operations)
    Chemically stabilized electric arc furnace dust (CSEAFD)
    that is generated by Conversion Systems, Inc. (CSI) (using
    the Super Detox
    ®
    treatment process, as modified by CSI to
    treat electric arc furnace dust (EAFD) (USEPA hazardous
    waste no. K061)), at the following site and which is
    disposed of in a RCRA Subtitle D municipal solid waste
    landfill (MSWLF): Northwestern Steel, Sterling, Illinois.
     
    CSI must implement a testing program for each site that
    meets the following conditions:
     
    1. Verification testing requirements: Sample collection and
    analyses, including quality control procedures, must be
    performed according to according to using appropriate
    methods. As applicable to the method-defined parameters
    of concern, analyses requiring the use of SW-846
    methodologies, methods in “Test Methods for Evaluating
    Solid Waste, Physical/Chemical Methods,” USEPA
    publication number EPA-530/SW-846, incorporated by
    reference in 35 Ill. Adm. Code 720.111 720.111(a), must be
    used without substitution. As applicable, the EPA-
    530/SW-846 methods might include Methods 0010, 0011,
    0020, 0023A, 0030, 0031, 0040, 0050, 0051, 0060, 0061,
    1010A, 1020B, 1110A, 1310B, 1311, 1312, 1320, 1330A,
    9010C, 9012B, 9040C, 9045D, 9060A, 9070A (uses
    USEPA Method 1664, Rev. A), 9071B, and 9095 B.
     
    A. Initial verification testing: During the first 20
    days of full-scale operation of a newly-constructed
    Super Detox
    ®
    treatment facility, CSI must analyze a
    minimum of four composite samples of CSEAFD
    representative of the full 20-day period. Composite
    samples must be composed of representative
    samples collected from every batch generated. The
    CSEAFD samples must be analyzed for the
    constituents listed in condition 3 below. CSI must
    report the operational and analytical test data,
    including quality control information, obtained
    during this initial period no later than 60 days after

     
    227
    the generation of the first batch of CSEAFD.
     
    B. Addition of new Super Detox
    ®
    treatment
    facilities to the exclusion:
     
    Option 1: If USEPA approves additional facilities,
    CSI may petition the Board for identical-in
    substance amendment of this exclusion pursuant to
    Section 22.4 for the Act and 35 Ill. Adm. Code 102
    and 720.120(a), or
     
    Option 2: If USEPA has not approved such
    amendment, CSI may petition the Board for
    amendment pursuant to the general rulemaking
    procedures of Section 27 of the Act and 35 Ill.
    Adm. Code 102 and 720.120(b); or
     
    Option 3: Alternatively to options 1 or 2 above,
    CSI may petition the Board for a hazardous waste
    delisting pursuant to Section 28.1 of the Act and
    Subpart D of 35 Ill. Adm. Code 104 and 35 Ill.
    Adm. Code 720.122.
     
    If CSI pursues general rulemaking (option 2 above)
    or hazardous waste delisting (option 3 above), it
    must demonstrate that the CSEAFD generated by a
    specific Super Detox
    ®
    treatment facility
    consistently meets the delisting levels specified in
    condition 3 below.
     
    C. Subsequent verification testing: For the
    approved facility, CSI must collect and analyze at
    least one composite sample of CSEAFD each
    month. The composite samples must be composed
    of representative samples collected from all batches
    treated in each month. These monthly
    representative samples must be analyzed, prior to
    the disposal of the CSEAFD, for the constituents
    listed in condition 3 below. CSI may, at its
    discretion, analyze composite samples gathered
    more frequently to demonstrate that smaller batches
    of waste are nonhazardous.
     
    2. Waste holding and handling: CSI must store as
    hazardous all CSEAFD generated until verification testing,
    as specified in condition 1A or 1C above, as appropriate, is

     
    228
    completed and valid analyses demonstrate that condition 3
    below is satisfied. If the levels of constituents measured in
    the samples of CSEAFD do not exceed the levels set forth
    in condition 3, then the CSEAFD is nonhazardous and may
    be disposed of in a RCRA Subtitle D municipal solid waste
    landfill. If constituent levels in a sample exceed any of the
    delisting levels set forth in condition 3 below, the CSEAFD
    generated during the time period corresponding to this
    sample must be retreated until it meets these levels or
    managed and disposed of as hazardous waste, in
    accordance with 35 Ill. Adm. Code 702 through 705, 720
    through 726, 728, and 733. CSEAFD generated by a new
    CSI treatment facility must be managed as a hazardous
    waste prior to the addition of the name and location of the
    facility to this exclusion pursuant to condition 1C above.
    After addition of the new facility to the exclusion pursuant
    to condition 1B above, CSEAFD generated during the
    verification testing in condition 1A is also non-hazardous if
    the delisting levels in condition 3 are satisfied.
     
    3. Delisting levels: All leachable concentrations for metals
    must not exceed the following levels (in parts per million
    (ppm)): antimony--0.06; arsenic--0.50; barium--7.6;
    beryllium--0.010; cadmium--0.050; chromium--0.33; lead--
    0.15; mercury--0.009; nickel--1; selenium--0.16; silver--
    0.30; thallium--0.020; vanadium--2; and zinc--70. Metal
    concentrations must be measured in the waste leachate by
    the method specified in Section 721.124.
     
    4. Changes in operating conditions: After initiating
    subsequent testing, as described in condition 1C, if CSI
    significantly changes the stabilization process established
    under condition 1 (e.g., use of new stabilization reagents),
    CSI must seek amendment of this exclusion using one of
    the options set forth in condition 1B above. After written
    amendment of this exclusion, CSI may manage CSEAFD
    wastes generated from the new process as nonhazardous if
    the wastes meet the delisting levels set forth in condition 3
    above.
     
    5. Data submittals: At least one month prior to operation of
    a new Super Detox
    ®
    treatment facility, CSI must notify the
    Agency in writing when the Super Detox
    ®
    treatment
    facility is scheduled to be on-line. The data obtained
    through condition 1A must be submitted to the Agency
    within the time period specified. Records of operating

     
    229
    conditions and analytical data from condition 1 must be
    compiled, summarized, and maintained on site for a
    minimum of five years. These records and data must be
    furnished to the Agency upon request and made available
    for inspection. Failure to submit the required data within
    the specified time period or to maintain the required
    records on site for the specified time will be considered a
    violation of the Act and Board regulations. All data
    submitted must be accompanied by a signed copy of the
    following certification statement to attest to the truth and
    accuracy of the data submitted:
     
    “Under civil and criminal penalty of law for the making or
    submission of false or fraudulent statements or
    representations, I certify that the information contained in
    or accompanying this document is true, accurate, and
    complete.
     
    “As to (those) identified section(s) of this document for
    which I cannot personally verify its (their) truth and
    accuracy, I certify as the company official having
    supervisory responsibility for the persons who, acting
    under my direct instructions, made the verification that this
    information is true, accurate, and complete.
     
    “In the event that any of this information is determined by
    the Board or a court of law to be false, inaccurate, or
    incomplete, and upon conveyance of this fact to the
    company, I recognize and agree that this exclusion of waste
    will be void as if it never had effect or to the extent
    directed by the Board or court and that the company will be
    liable for any actions taken in contravention of the
    company’s obligations under the federal RCRA and
    Comprehensive Environmental Response, Compensation
    and Liability Act (42 U.S.C. §§ USC 9601 et seq.) and
    corresponding provisions of the Act premised upon the
    company’s reliance on the void exclusion.”
     
    BOARD NOTE: The obligations of this exclusion are
    derived from but also distinct from the obligations under
    the corresponding federally-granted exclusion of table 2 of
    Appendix IX to 40 CFR 261, Appendix IX, Table 2.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    230
    Section 721.Appendix I Wastes Excluded by Administrative Action
     
    Table C Wastes Excluded by USEPA under pursuant to 40 CFR 260.20 and 260.22 from
    Commercial Chemical Products, Off-Specification Species, Container Residues,
    and Soil Residues Thereof
     
     
    Facility Address Waste Description
     
    (None excluded from an Illinois source at this time)
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.Appendix I Wastes Excluded by Administrative Action
     
    Table D Wastes Excluded by the Board by Adjusted Standard
     
    The Board has entered the following orders on petitions for adjusted standards for delisting,
    pursuant to 35 Ill. Adm. Code 720.122.
     
    AS91-1 Petition of Keystone Steel and Wire Co. for Hazardous Waste Delisting,
    February 6, 1992, and modified at 133 PCB 189, April 23, 1992. (Treated
    K061 waste)
     
    AS91-3 Petition of Peoria Disposal Co. for an Adjusted Standard from Subpart D
    of 35 Ill. Adm. Code 721, February 6 and March 11, 1993. (Treated F006
    waste)
     
    AS93-7 Petition of Keystone Steel & Wire Co. for an Adjusted Standard from
    Subpart D of 35 Ill. Adm. Code 721, February 17, 1994, as modified
    March 17, 1994. (Treated K062 waste)
     
    AS94-10 Petition of Envirite Corporation for an Adjusted Standard from Subpart D
    of 35 Ill. Adm. Code 721, December 14, 1994, as modified on February
    16, 1995. (Treated F006, F007, F008, F009, F011, F012, F019, K002,
    K003, K004, K005, K006, K007, K008, and K062 wastes)
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 721.Appendix Y Table to Section 721.138
     
    Chemical name CAS No
    Composite
    value
    (mg/kg)
    Heating
    value
    (BTU/lb)
    Concentra-
    tion limit
    (mg/kg at
    10,000
    Btu/lb)
    Minimum
    required
    detection
    limit
    (mg/kg)

     
    231
    Total Nitrogen as N NA 90009,000 18400
    18,400
    49004,900
      
    Total Halogens as Cl NA 10001,000 18400
    18,400
    540
    Total Organic Halogens as
    Cl
    NA -- -- (Note 1)
    Polychlorinated biphenyls,
    total (Arocolors, total)
    1336-36-3 ND -- ND 1.4
    Cyanide, total 57-12-5 ND -- ND 1.0
    Metals:
    Antimony, total 7440-36-0 ND -- 12
    Arsenic, total 7440-38-2 ND -- 0.23
    Barium, total 7440-39-3 ND -- 23
    Beryllium, total 7440-41-7 ND -- 1.2
    Cadmium, total 7440-43-9 -- ND 1.2
    Chromium, total 7440-47-3 ND -- 2.3
    Cobalt 7440-48-4 ND -- 4.6
    Lead, total 7439-92-1 57 18100
    18,100
    31
    Manganese 7439-96-5 ND -- 1.2
    Mercury, total 7439-97-6 ND -- 0.25
    Nickel, total 7440-02-0 106 18400
    18,400
    58
    Selenium, total 7782-49-2 ND -- 0.23
    Silver, total 7440-22-4 ND -- 2.3
    Thallium, total 7440-28-0 ND -- 23
    Hydrocarbons:
    Benzo(a)anthracene 56-55-3 ND -- 24002,400
      
    Benzene 71-43-2 80008,000 19600
    19,600
    41004,100
      
    Benzo(b)fluoranthene 205-99-2 ND -- 24002,400
      
    Benzo(k)fluoranthene 207-08-9 ND -- 24002,400
      
    Benzo(a)pyrene 50-32-8 ND -- 24002,400
      
    Chrysene 218-01-9 ND -- 24002,400
      
    Dibenzo(a,h)anthracene 53-70-3 ND -- 24002,400
      
    7,12-Dimethylbenz(a)-
    anthracene
    57-97-6 ND -- 24002,400
      
    Fluoranthene 206-44-0 ND -- 24002,400
      
    Indeno(1,2,3-cd)pyrene 193-39-5 ND -- 24002,400
      
    3-Methylcholanthrene 56-49-5 ND -- 24002,400
      
    Naphthalene 91-20-3 62006,200 19400
    19,400
    32003,200
      
    Toluene 108-88-3 69000
    69,000
    19400
    19,400
    36000
    36,000
     

     
    232
    Oxygenates:
    Acetophenone 98-86-2 ND -- 24002,400
      
    Acrolein 107-02-8 ND -- 39
    Allyl alcohol 107-18-6 ND -- 30
    Bis(2-ethylhexyl)-
    phthalate (Di-2-ethyl-
    hexyl phthalate)
    117-81-7 ND -- 24002,400
      
    Butyl benzyl phthalate 85-68-7 ND -- 24002,400
      
    o-Cresol (2-Methyl
    phenol)
    95-48-7 ND -- 24002,400
      
    m-Cresol (3-M ethyl
    phenol)
    108-39-4 ND -- 24002,400
      
    p-Cresol (4-Methyl
    phenol)
    106-44-5 ND -- 24002,400
      
    Di-n-butyl phthalate 84-74-2 ND -- 24002,400
      
    Diethyl phthalate 84-66-2 ND -- 24002,400
      
    2,4-Dimethylphenol 105-67-9 ND -- 24002,400
      
    Dimethyl phthalate 131-11-3 ND -- 24002,400
      
    Di-n-octyl phthalate 117-84-0 ND -- 24002,400
      
    Endothall 145-73-3 ND -- 100
    Ethyl methacrylate 97-63-2 ND -- 39
    2-Ethoxyethanol
    (Ethylene glycol
    monoethyl ether)
    110-80-5 ND -- 100
    Isobutyl alcohol 78-83-1 ND -- 39
    Isosafrole 120-58-1 ND -- 24002,400
      
    Methyl ethyl ketone (2-
    Butanone)
    78-93-3 ND -- 39
    Methyl methacrylate 80-62-6 ND -- 39
    1,4-Naphthoquinone 130-15-4 ND -- 24002,400
      
    Phenol 108-95-2 ND -- 24002,400
      
    Propargyl alcohol (2-
    Propyn-l-ol)
    107-19-7 ND -- 30.
    Safrole 94-59-7 ND -- 24002,400
      
    Sulfonated Organics:
    Carbon disulfide 75-15-0 ND -- ND 39
    Disulfoton 298-04-4 ND -- ND 24002,400
    Ethyl methanesulfonate 62-50-0 ND -- ND 24002,400
    Methyl methane-
    sulfonate
    66-27-3 ND -- ND 24002,400
    Phorate 298-02-2 ND -- ND 24002,400
    1,3-Propane sultone 1120-71-4 ND -- ND 100
    Tetraethyldithiopyro-
    phosphate (Sulfotepp)
    3689-24-5 ND -- ND 24002,400

     
    233
    Thiophenol (Benzene-
    thiol)
    108-98-5 ND -- ND 30
    O,O,O-Triethyl
    phosphorothioate
    126-68-1 ND -- ND 24002,400
    Nitrogenated Organics:
    Acetonitrile (Methyl
    cyanide)
    75-05-8 ND -- ND 39
    2-Acetylaminofluorene
    (2-AAF)
    53-96-3 ND -- ND 24002,400
    Acrylonitrile 107-13-1 ND -- ND 39
    4-Aminobiphenyl 92-67-1 ND -- ND 24002,400
    4-Aminopyridine 504-24-5 ND -- ND 100
    Aniline 62-53-3 ND -- ND 24002,400
    Benzidine 92-87-5 ND -- ND 24002,400
    Dibenz(a,j)acridine 224-42-0 ND -- ND 24002,400
    O,O-Diethyl O-
    pyrazinyl phophoro-
    thioate (Thionazin)
    297-97-2 ND -- ND 24002,400
    Dimethoate 60-51-5 ND -- ND 24002,400
    p-(Dimethylamino)azo-
    benzene (4-Dimethyl-
    aminoazobenzene)
    60-11-7 ND -- ND 24002,400
    3,3'-Dimethylbenzidine 119-93-7 ND -- ND 24002,400
    a,a-Dimethylphenethyl-
    amine
    122-09-8 ND -- ND 24002,400
    3,3'-Dimethoxy-
    benzidine
    119-90-4 ND -- ND 100
    1,3-Dinitrobenzene (m-
    Dinitrobenzene)
    99-65-0 ND -- ND 24002,400
    4,6-Dinitro-o-cresol 534-52-1 ND -- ND 24002,400
    2,4-Dinitrophenol 51-28-5 ND -- ND 24002,400
    2,4-Dinitrotoluene 121-14-2 ND -- ND 24002,400
    2,6-Dinitrotoluene 606-20-2 ND -- ND 24002,400
    Dinoseb (2-sec-Butyl-
    4,6-dinitrophenol)
    88-85-7 ND -- ND 24002,400
    Diphenylamine 122-39-4 ND -- ND 24002,400
    Ethyl carbamate
    (Urethane)
    51-79-6 ND -- ND 100
    Ethylenethiourea (2-
    Imidazolidinethione)
    96-45-7 ND -- ND 110
    Famphur 52-85-7 ND -- ND 24002,400
    Methacrylonitrile 126-98-7 ND -- ND 39
    Methapyrilene 91-80-5 ND -- ND 24002,400
    Methomyl 16752-77-5 ND -- ND 57

     
    234
    2-Methyllactonitrile
    (Acetone cyanohydrin )
    75-86-5 ND -- ND 100
    Methyl parathion 298-00-0 ND -- ND 24002,400
    MNNG (N-Metyl-N-
    nitroso-N'-nitro-
    guanidine)
    70-25-7 ND -- ND 110
    1-Naphthylamine (
    α
    -
    Naphthylamine]
    134-32-7 ND -- ND 24002,400
    2-Naphthylamine (
    β
    -
    Naphthylamine)
    91-59-8 ND -- ND 24002,400
    Nicotine 54-11-5 ND -- ND 100
    4-Nitroaniline (p-
    Nitroaniline)
    100-01-6 ND -- ND 24002,400
    Nitrobenzene 98-95-3 ND -- ND 24002,400
    p-Nitrophenol (p-Nitro-
    phenol)
    100-02-7 ND -- ND 24002,400
    5-Nitro-o-toluidine 99-55-8 ND -- ND 24002,400
    N-Nitrosodi-n-butyl-
    amine
    924-16-3 ND -- ND 24002,400
    N-Nitrosodiethylamine 55-18-5 ND -- ND 24002,400
    N-Nitrosodiphenyl-
    amine (Diphenylnitros-
    amine)
    86-30-6 ND -- ND 24002,400
    N-Nitroso-N-methyl-
    ethylamine
    10595-95-6 ND -- ND 24002,400
    N-Nitrosomorpholine 59-89-2 ND -- ND 24002,400
    N-Nitrosopiperidine 100-75-4 ND -- ND 24002,400
    N-Nitrosopyrrolidine 930-55-2 ND -- ND 24002,400
    2-Nitropropane 79-46-9 ND -- ND 30
    Parathion 56-38-2 ND -- ND 24002,400
    Phenacetin 62-44-2 ND -- ND 24002,400
    1,4-Phenylene diamine,
    (p-Phenylenediamine)
    106-50-3 ND -- ND 24002,400
    N-Phenylthiourea 103-85-5 ND -- ND 57
    2-Picoline (alpha-
    Picoline)
    109-06-8 ND -- ND 24002,400
    Propythioracil (6-
    Propyl-2-thiouracil)
    51-52-5 ND -- ND 100
    Pyridine 110-86-1 ND -- ND 24002,400
    Strychnine 57-24-9 ND -- ND 100
    Thioacetamide 62-55-5 ND -- ND 57
    Thiofanox 39196-18-4 ND -- ND 100
    Thiourea 62-56-6 ND -- ND 57

     
    235
    Toluene-2,4-diamine
    (2,4-Diaminotoluene)
    95-80-7 ND -- ND 57
    Toluene-2,6-diamine
    (2,6-Diaminotoluene)
    823-40-5 ND -- ND 57
    o-Toluidine 95-53-4 ND -- ND 24002,400
    p-Toluidine 106-49-0 ND -- ND 100
    1,3,5-Trinitrobenzne,
    1,3,5-Trinitrobenzene,
    (sym-Trinitrobenzene)
    99-35-4 ND -- ND 24002,400
    Halogenated Organics:
    Allyl chloride 107-05-1 ND -- ND 39
    Aramite 140-57-8 ND -- ND 24002,400
    Benzal chloride (Di-
    chloromethyl benzene)
    98-87-3 ND -- ND 100
    Benzyl chloride 100-44-77 ND -- ND 100
    Bis(2-chloroethyl)ether
    (Dichloroethyl ether)
    111-44-4 ND -- ND 24002,400
    Bromoform (Tribromo-
    methane)
    75-25-2 ND -- ND 39
    Bromomethane
    (Methyl bromide)
    74-83-9 ND -- ND 39
    4-Bromophenyl phenyl
    ether (p-Bromodi-
    phenyl ether)
    101-55-3 ND -- ND 24002,400
    Carbon tetrachloride 56-23-5 ND -- ND 39
    Chlordane 57-74-9 ND -- ND 14
    p-Chloroaniline 106-47-8 ND -- ND 24002,400
    Chlorobenzene 108-90-7 ND -- ND 39
    Chlorobenzilate 510-15-6 ND -- ND 24002,400
    p-Chloro-m-cresol 59-50-7 ND -- ND 24002,400
    2-Chloroethyl vinyl
    ether
    110-75-8 ND -- ND 39
    Chloroform 67-66-3 ND -- ND 39
    Chloromethane
    (Methyl chloride)
    74-87-3 ND -- ND 39
    2-Chloronaphthalene
    (
    β
    -Chlorophthalene)
    91-58-7 ND -- ND 24002,400
    2-Chlorophenol (o-
    Chlorophenol)
    95-57-8 ND -- ND 24002,400
    Chloroprene (2-Chloro-
    1,3-butadiene)
    1126-99-8 ND -- ND 39
    2,4-D (2,4-Dichloro-
    phenoxyacetic acid)
    94-75-7 ND -- ND 7.0
    Diallate 2303-16-4 ND -- ND 24002,400

     
    236
    1,2-Dibromo-3-chloro-
    propane
    96-12-8 ND -- ND 39
    1,2-Dichlorobenzene
    (o-Dichlorobenzene)
    95-50-1 ND -- ND 24002,400
    1,3-Dichlorobenzene
    (m-Dichlorobenzene)
    541-73-1 ND -- ND 24002,400
    1,4-Dichlorobenzene
    (p-Dichlorobenzene)
    106-46-7 ND -- ND 24002,400
    3,3'-Dichlorobenzidine 91-94-1 ND -- ND 24002,400
    Dichlorodifluoro-
    methane (CFC-12)
    75-71-8 ND -- ND 39
    1,2-Dichloroethane
    (Ethylene dichloride)
    107-06-2 ND -- ND 39
    1,1-Dichloroethylene
    (Vinylidene chloride)
    75-35-4 ND -- ND 39
    Dichloromethoxy
    ethane (Bis(2-chloro-
    ethoxy)methane)
    111-91-1 ND -- ND 24002,400
    2,4-Dichlorophenol 120-83-2 ND -- ND 24002,400
    2,6-Dichlorophenol 87-65-0 ND -- ND 24002,400
    1,2-Dichloropropane
    (Propylene dichloride)
    78-87-5 ND -- ND 39
    cis-1,3-Dichloro-
    propylene
    10061-01-5 ND -- ND 39
    trans-1,3-Dichloro-
    propylene
    10061-02-6 ND -- ND 39
    1,3-Dichloro-2-
    propanol
    96-23-1 ND -- ND 30
    Endosulfan I 959-98-8 ND -- ND 1.4
    Endosulfan II 33213-65-9 ND -- ND 1.4
    Endrin 72-20-8 ND -- ND 1.4
    Endrin aldehyde 7421-93-4 ND -- ND 1.4
    Endrin Ketone 53494-70-5 ND -- ND 1.4
    Epichlorohydrin (1-
    Chloro-2,3-epoxy
    propane)
    106-89-8 ND -- ND 30
    Ethylidene dichloride
    (1,1-Dichloroethane)
    75-34-3 ND -- ND 39
    2-Fluoroacetamide 640-19-7 ND -- ND 100
    Heptachlor 76-44-8 ND -- ND 1.4
    Heptachlor epoxide 1024-57-3 ND -- ND 2.8
    Hexachlorobenzene 118-74-1 ND -- ND 24002,400

     
    237
    Hexachloro-1,3-buta-
    diene (Hexachlorobuta-
    diene)
    87-68-3 ND -- ND 24002,400
    Hexachlorocyclopenta-
    diene
    77-47-4 ND -- ND 24002,400
    Hexachloroethane 67-72-1 ND -- ND 24002,400
    Hexachlorophene 70-30-4 ND -- ND 59000
    59,000
    Hexachloropropene
    (Hexachloropropylene)
    1888-71-7 ND -- ND 24002,400
    Isodrin 465-73-6 ND -- ND 24002,400
    Kepone (Chlordecone) 143-50-0 ND -- ND 47004,700
    Lindane (gamma-Hexa-
    chlorocyclohexane) (
    γ
    -
    BHC)
    58-89-9 ND -- ND 1.4
    Methylene chloride
    (Dichloromethane)
    75-09-2 ND -- ND 39
    4,4'-methylene-bis(2-
    chloroaniline)
    101-14-4 ND -- ND 100
    Methyl iodide (Iodo-
    methane)
    74-88-4 ND -- ND 39
    Pentachlorobenzene 608-93-5 ND -- ND 24002,400
    Pentachloroethane 76-01-7 ND -- ND 39
    Pentachloronitro-
    benzene (PCNB)
    (Quintobenzene)
    (Quintozene)
    82-68-8 ND -- ND 24002,400
    Pentachlorophenol 87-86-5 ND -- ND 24002,400
    Pronamide 23950-58-5 ND -- ND 24002,400
    Silvex (2,4,5-Trichloro-
    phenoxypropionic acid)
    93-72-1 ND -- ND 7.0
    2,3,7,8-Tetrachloro-
    dibenzo-p-dioxin
    (2,3,7,8-TCDD)
    1746-01-6 ND -- ND 30
    1,2,4,5-Tetrachloro-
    benzene
    95-94-3 ND -- ND 24002,400
    1,1,2,2-Tetrachloro-
    ethane
    79-34-5 ND -- ND 39
    Tetrachloroethylene
    (Perchloroethylene)
    127-18-4 ND -- ND 39
    2,3,4,6-Tetrachloro-
    phenol
    58-90-2 ND -- ND 24002,400
    1,2,4-Trichlorobenzene 120-82-1 ND -- ND 24002,400

     
    238
    1,1,1-Trichloroethane
    (Methyl chloroform)
    71-55-6 ND -- ND 39
    1,1,2-Trichloroethane
    (Vinyl trichloride)
    79-00-5 ND -- ND 39
    Trichloroethylene 79-01-6 ND -- ND 39
    Trichlorofluoro-
    methane (Trichloro-
    monofluoromethane)
    75-69-4 ND -- ND 39
    2,4,5-Trichlorophenol 95-95-4 ND -- ND 24002,400
    2,4,6-Trichlorophenol 88-06-2 ND -- ND 24002,400
    1,2,3-Trichloropropane 96-18-4 ND -- ND 39
    Vinyl Chloride 75-01-4 ND -- ND 39
     
    NA means not applicable.
    ND means nondetect.
    Note 1: 25 (mg/kg at 10,000 Btu/lb) as organic halogen or as the individual halogenated
    organics listed in the table at the levels indicated.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
     
    PART 722
    STANDARDS APPLICABLE TO GENERATORS OF HAZARDOUS WASTE
     
    SUBPART A: GENERAL
    Section
    722.110 Purpose, Scope, and Applicability
    722.111 Hazardous Waste Determination
    722.112 USEPA Identification Numbers
     
    SUBPART B: THE MANIFEST
    Section
    722.120 General Requirements
    722.121 Acquisition of Manifest Tracking Numbers, Manifest Printing, and Obtaining
    Manifests
    722.122 Number of Copies
    722.123 Use of the Manifest
    722.127 Waste Minimization Certification
     

     
    239
    SUBPART C: PRE-TRANSPORT REQUIREMENTS
    Section
    722.130 Packaging
    722.131 Labeling
    722.132 Marking
    722.133 Placarding
    722.134 Accumulation Time
     
    SUBPART D: RECORDKEEPING AND REPORTING
    Section
    722.140 Recordkeeping
    722.141 Annual Reporting
    722.142 Exception Reporting
    722.143 Additional Reporting
    722.144 Special Requirements for Generators of between 100 and 1,000 kilograms per
    month
     
    SUBPART E: EXPORTS OF HAZARDOUS WASTE
    Section
    722.150 Applicability
    722.151 Definitions
    722.152 General Requirements
    722.153 Notification of Intent to Export
    722.154 Special Manifest Requirements
    722.155 Exception Report
    722.156 Annual Reports
    722.157 Recordkeeping
    722.158 International Agreements
     
    SUBPART F: IMPORTS OF HAZARDOUS WASTE
    Section
    722.160 Imports of Hazardous Waste
     
    SUBPART G: FARMERS
    Section
    722.170 Farmers
     
    SUBPART H: TRANSFRONTIER SHIPMENTS OF HAZARDOUS WASTE
    FOR RECOVERY WITHIN THE OECD
    Section
    722.180 Applicability
    722.181 Definitions
    722.182 General Conditions
    722.183 Notification and Consent
    722.184 Tracking Document
    722.185 Contracts

     
    240
    722.186 Provisions Relating to Recognized Traders
    722.187 Reporting and Recordkeeping
    722.189 OECD Waste Lists
     
    722.Appendix A Hazardous Waste Manifest
     
    AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the
    Environmental Protection Act [415 ILCS 5/7.2, 22.4, and 27].
     
    SOURCE: Adopted in R81-22 at 5 Ill. Reg. 9781, effective May 17, 1982; amended and
    codified in R81-22 at 6 Ill. Reg. 4828, effective May 17, 1982; amended in R82-18 at 7 Ill. Reg.
    2518, effective February 22, 1983; amended in R84-9 at 9 Ill. Reg. 11950, effective July 24,
    1985; amended in R85-22 at 10 Ill. Reg. 1131, effective January 2, 1986; amended in R86-1 at
    10 Ill. Reg. 14112, effective August 12, 1986; amended in R86-19 at 10 Ill. Reg. 20709,
    effective December 2, 1986; amended in R86-46 at 11 Ill. Reg. 13555, effective August 4, 1987;
    amended in R87-5 at 11 Ill. Reg. 19392, effective November 12, 1987; amended in R87-39 at 12
    Ill. Reg. 13129, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 452, effective
    December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18523, effective November 13, 1989;
    amended in R90-10 at 14 Ill. Reg. 16653, effective September 25, 1990; amended in R90-11 at
    15 Ill. Reg. 9644, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14562, effective
    October 1, 1991; amended in R91-13 at 16 Ill. Reg. 9833, effective June 9, 1992; amended in
    R92-1 at 16 Ill. Reg. 17696, effective November 6, 1992; amended in R93-4 at 17 Ill. Reg.
    20822, effective November 22, 1993; amended in R95-6 at 19 Ill. Reg. 9935, effective June 27,
    1995; amended in R95-20 at 20 Ill. Reg. 11236, effective August 1, 1996; amended in R96-
    10/R97-3/R97-5 at 22 Ill. Reg. 603, effective December 16, 1997; amended in R97-21/R98-
    3/R98-5 at 22 Ill. Reg. 17950, effective September 28, 1998; amended in R00-5 at 24 Ill. Reg.
    1136, effective January 6, 2000; amended in R00-13 at 24 Ill. Reg. 9822, effective June 20,
    2000; expedited correction at 25 Ill. Reg. 5105, effective June 20, 2000; amended in R05-2 at 29
    Ill. Reg. 6312, effective April 22, 2005; amended in R06-5/R06-6/R06-7 at 30 Ill. Reg.
    ________, effective ______________________.
     
    SUBPART B: THE MANIFEST
     
    Section 722.120 General Requirements
     
    a) Manifest use.
     
    1)
    A generator that transports hazardous waste or offers a hazardous waste
    for transportation for off-site treatment, storage, or disposal or, effective
    September 5, 2006, a treatment, storage, or disposal facility that offers for
    transport a rejected load of hazardous waste must prepare a manifest
    before transporting the waste off-site on USEPA Form 8700-22 (and, if
    necessary on USEPA Form 8700-22A) according to the instructions
    included in the appendix to 40 CFR 262 (Uniform Hazardous Waste
    Manifest and Instructions (EPA Forms 8700–22 and 8700–22a and Their
    Instructions)), incorporated by reference in 35 Ill. Adm. Code 720.111(b).

     
    241
     
    2) Manifest amendments effective dates.
     
    A) The revised manifest form and procedures in 35 Ill. Adm. Code
    720.110 and 721.107, this Section, and Sections 722.121, 722.127,
    722.132 through 722.134, 722.154 and in Appendix A to this Part,
    as amended at 70 Fed. Reg. 10776 (March 4, 2005), will not apply
    until September 5, 2006.
     
    B) The existing manifest form and procedures in 35 Ill. Adm. Code
    720.110 and 721.107, this Section, and Sections 722.121, 722.127,
    722.132 through 722.134, 722.154 and in Appendix A to this Part
    (2004) will apply until September 5, 2006.
     
    b) A generator must designate on the manifest one receiving facility that is permitted
    to handle the waste described on the manifest.
     
    c) A generator may also designate on the manifest one alternate receiving facility
    that is permitted to handle his waste in the event an emergency prevents delivery
    of the waste to the primary designated facility.
     
    d) If the transporter is unable to deliver the hazardous waste to the designated
    receiving facility or the alternate facility, the generator must either designate
    another receiving facility or instruct the transporter to return the waste.
     
    e) The requirements of this Subpart B do not apply to hazardous waste produced by
    generators of greater than 100 kg but less than 1,000 kg in a calendar month
    where the following conditions are fulfilled:
     
    1) The waste is reclaimed under a contractual agreement that specifies the
    type of waste and frequency of shipments;
     
    2) The vehicle used to transport the waste to the recycling facility and to
    deliver regenerated material back to the generator is owned and operated
    by the reclaimer of the waste; and
     
    3) The generator maintains a copy of the reclamation agreement in his files
    for a period of at least three years after termination or expiration of the
    agreement.
     
    f) The requirements of this Subpart B and Section 722.132(b) do not apply to the
    transport of hazardous wastes on a public or private right-of-way within or along
    the border of contiguous property under the control of the same person, even if
    such contiguous property is divided by a public or private right-of-way.
    Notwithstanding 35 Ill. Adm. Code 723.110(a), the generator or transporter must
    comply with the requirements for transporters set forth in 35 Ill. Adm. Code

     
    242
    723.130 and 723.131 in the event of a discharge of hazardous waste on a public or
    private right-of-way.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 722.121 Acquisition of Manifest Tracking Numbers, Manifest Printing, and
    Obtaining Manifests
     
    a) The following requirements apply until September 5, 2006:
     
    a1) If the State of Illinois is the state to which the shipment is manifested
    (designated receiving state), the generator must use the manifest supplied by
    the Agency.
     
    b2) If the State of Illinois is not the designated receiving state, the generator
    must use the manifest required by the designated receiving state. If the
    designated receiving state does not supply and require the manifest, then the
    generator must use the manifest supplied by the Agency.
     
    b) The following requirements apply effective September 5, 2006:
     
    1) USEPA approval of manifest.
     
    A) A registrant may not print the manifest or have the manifest
    printed for use or distribution, unless it has received approval from
    the USEPA Director of the Office of Solid Waste to do so pursuant
    to 40 CFR 262.21(c) and (e), as described in subsections (b)(3) and
    (b)(5) of this Section.
     
    B) The approved registrant is responsible for ensuring that the
    organizations identified in its application are in compliance with
    the procedures of its approved application and the requirements of
    40 CFR 262.21, as described in this subsection (b). The registrant
    is responsible for assigning manifest tracking numbers to its
    manifests.
     
    2) A registrant must submit an initial application to the USEPA Director of
    the Office of Solid Waste that contains the following information:
     
    A) The name and mailing address of registrant;
     
    B) The name, telephone number and email address of contact person;
     
    C) A brief description of registrant’s government or business activity;
     
    D) The USEPA identification number of the registrant, if applicable;

     
    243
     
    E) A description of the scope of the operations that the registrant
    plans to undertake in printing, distributing, and using its manifests,
    including the following:
     
    i) A description of the printing operation. The description
    should include an explanation of whether the registrant
    intends to print its manifests in-house (
    i.e.
    , using its own
    printing establishments) or through a separate (
    i.e.
    ,
    unaffiliated) printing company. If the registrant intends to
    use a separate printing company to print the manifest on its
    behalf, the application must identify this printing company
    and discuss how the registrant will oversee the company. If
    this includes the use of intermediaries (
    e.g.
    , prime and
    subcontractor relationships), the role of each must be
    discussed. The application must provide the name and
    mailing address of each company. It also must provide the
    name and telephone number of the contact person at each
    company;
     
    ii) A description of how the registrant will ensure that its
    organization and unaffiliated companies, if any, comply
    with the requirements of 40 CFR 262.21, as described in
    this subsection (b). The application must discuss how the
    registrant will ensure that a unique manifest tracking
    number will be preprinted on each manifest. The
    application must describe the internal control procedures to
    be followed by the registrant and unaffiliated companies to
    ensure that numbers are tightly controlled and remain
    unique. In particular, the application must describe how
    the registrant will assign manifest tracking numbers to its
    manifests. If computer systems or other infrastructure will
    be used to maintain, track, or assign numbers, these should
    be indicated. The application must also indicate how the
    printer will pre-print a unique number on each form (
    e.g.
    ,
    crash or press numbering). The application also must
    explain the other quality procedures to be followed by each
    establishment and printing company to ensure that all
    required print specifications are consistently achieved and
    that printing violations are identified and corrected at the
    earliest practicable time; and
     
    iii) An indication of whether the registrant intends to use the
    manifests for its own business operations or to distribute
    the manifests to a separate company or to the general
    public (
    e.g.
    , for purchase);

     
    244
     
    F) A brief description of the qualifications of the company that will
    print the manifest. The registrant may use readily available
    information to do so (
    e.g.
    , corporate brochures, product samples,
    customer references, documentation of ISO certification), so long
    as such information pertains to the establishments or company
    being proposed to print the manifest;
     
    G) Proposed unique three-letter manifest tracking number suffix. If
    the registrant is approved to print the manifest, the registrant must
    use this suffix to pre-print a unique manifest tracking number on
    each manifest; and
     
    H) A signed certification by a duly authorized employee of the
    registrant that the organizations and companies in its application
    will comply with the procedures of its approved application and
    the requirements of 40 CFR 262.21, as described in this subsection
    (b) and that it will notify the Agency and the USEPA Director of
    the Office of Solid Waste of any duplicated manifest tracking
    numbers on manifests that have been used or distributed to other
    parties as soon as this becomes known.
     
    3) USEPA will review the application submitted under subsection (b)(2) of
    this Section and either approve it or request additional information or
    modification before approving it.
     
    4) Submission of document samples.
     
    A) Upon USEPA approval of the application pursuant to 40 CFR
    262.21(c), as described in subsection (b)(3) of this Section,
    USEPA will provide the registrant an electronic file of the
    manifest, continuation sheet, and manifest instructions and ask the
    registrant to submit three fully assembled manifests and
    continuation sheet samples, except as noted in 40 CFR
    262.21(d)(3), as described in subsection (b)(4)(C) of this Section.
    The registrant’s samples must meet all of the specifications in 40
    CFR 262.21(f), as described in subsection (b)(6) of this Section,
    and be printed by the company that will print the manifest as
    identified in the application approved by USEPA pursuant to 40
    CFR 262.21(c), as described in subsection (b)(3) of this Section.
     
    B) The registrant must submit a description of the manifest samples as
    follows:
     
    i) The paper type (
    i.e.
    , manufacturer and grade of the
    manifest paper);

     
    245
     
    ii) The paper weight of each copy;
     
    iii) The ink color of the manifest’s instructions. If screening of
    the ink was used, the registrant must indicate the extent of
    the screening; and
     
    iv) The method of binding the copies.
     
    C) The registrant need not submit samples of the continuation sheet if
    it will print its continuation sheet using the same paper type, paper
    weight of each copy, ink color of the instructions, and binding
    method as its manifest form samples.
     
    5) USEPA will evaluate the forms and either approve the registrant to print
    them as proposed or request additional information or modification to
    them before approval. USEPA will notify the registrant of its decision by
    mail. The registrant cannot use or distribute its forms until USEPA
    approves them. An approved registrant must print the manifest and
    continuation sheet according to its application approved by USEPA
    pursuant to 40 CFR 262.21(c), as described in subsection (b)(3) of this
    Section and the manifest specifications in 40 CFR 262.21(f), as described
    in subsection (b)(6) of this Section. It also must print the forms according
    to the paper type, paper weight, ink color of the manifest instructions and
    binding method of its approved forms.
     
    6) Paper manifests and continuation sheets must be printed according to the
    following specifications:
     
    A) The manifest and continuation sheet must be printed with the exact
    format and appearance as USEPA Forms 8700–22 and 8700–22A,
    respectively. However, information required to complete the
    manifest may be preprinted on the manifest form.
     
    B) A unique manifest tracking number assigned in accordance with a
    numbering system approved by USEPA must be pre-printed in
    Item 4 of the manifest. The tracking number must consist of a
    unique three-letter suffix following nine digits.
     
    C) The manifest and continuation sheet must be printed on 8½ x 11-
    inch white paper, excluding common stubs (
    e.g.
    , top- or side-
    bound stubs). The paper must be durable enough to withstand
    normal use.
     
    D) The manifest and continuation sheet must be printed in black ink
    that can be legibly photocopied, scanned, and faxed, except that

     
    246
    the marginal words indicating copy distribution must be in red ink.
     
    E) The manifest and continuation sheet must be printed as six-copy
    forms. Copy-to-copy registration must be exact within 1
    32nd of
    an inch. Handwritten and typed impressions on the form must be
    legible on all six copies. Copies must be bound together by one or
    more common stubs that reasonably ensure that they will not
    become detached inadvertently during normal use.
     
    F) Each copy of the manifest and continuation sheet must indicate
    how the copy must be distributed, as follows:
     
    i) Page 1 (top copy): “Designated facility to destination State
    (if required).”
     
    ii) Page 2: “Designated facility to generator State (if
    required).”
     
    iii) Page 3: “Designated facility to generator.”
     
    iv) Page 4: “Designated facility’s copy.”
     
    v) Page 5: “Transporter’s copy.”
     
    vi) Page 6 (bottom copy): “Generator’s initial copy.”
     
    G) The instructions in the Appendix to 40 CFR 262 (Uniform
    Hazardous Waste Manifest and Instructions (EPA Forms 8700–22
    and 8700–22a and Their Instructions)), incorporated by reference
    in 35 Ill. Adm. Code 720.111(b), must appear legibly on the back
    of the copies of the manifest and continuation sheet as provided in
    40 CFR 262.21(f), as described in this subsection (b)(6) and
    subsection (b)(14) of this Section. The instructions must not be
    visible through the front of the copies when photocopied or faxed.
     
    BOARD NOTE: Subsection (b)(6)(G) corresponds with 40 CFR
    262.21(f)(7) (2004), as amended at 70 Fed. Reg. 10776 (March 4,
    2005). The Board has moved 40 CFR 262.21(f)(7)(i) and (f)(7)(ii)
    to appear as subsections (b)(14)(A) and (b)(14)(B) to comport with
    Illinois Administrative Code codification requirements.
     
    7) Use of approved manifests.
     
    A) A generator may use manifests printed by any source so long as
    the source of the printed form has received approval from USEPA
    to print the manifest pursuant to 40 CFR 262.21(c) and (e), as

     
    247
    described in subsections (b)(3) and (b)(5) of this Section. A
    registered source may be any of the following:
     
    i) A state agency;
     
    ii) A commercial printer;
     
    iii) A hazardous waste generator, transporter, or treatment,
    storage, or disposal facility; or
     
    iv) A hazardous waste broker or other preparer who prepares
    or arranges shipments of hazardous waste for
    transportation.
     
    B) The waste generator must determine whether the generator state or
    the consignment state for a shipment regulates any additional
    wastes (beyond those regulated federally) as hazardous wastes
    under these states’ authorized programs. The generator must also
    determine whether the consignment state or generator state
    requires the generator to submit any copies of the manifest to these
    states. In cases where the generator must supply copies to either
    the generator’s state or the consignment state, the generator is
    responsible for supplying legible photocopies of the manifest to
    these states.
     
    8) Manifest revisions.
     
    A) If an approved registrant would like to update any of the
    information provided in its application approved by USEPA
    pursuant to 40 CFR 262.21(c), as described in subsection (b)(3) of
    this Section (
    e.g.
    , to update a company phone number or name of
    contact person), the registrant must revise the application and
    submit it to the USEPA Director of the Office of Solid Waste,
    along with an indication or explanation of the update, as soon as
    practicable after the change occurs. The USEPA will either
    approve or deny the revision. If USEPA denies the revision, it will
    explain the reasons for the denial, and it will contact the registrant
    and request further modification before approval.
     
    B) If the registrant would like a new tracking number suffix, the
    registrant must submit a proposed suffix to the USEPA Director of
    the Office of Solid Waste, along with the reason for requesting it.
    USEPA will either approve the suffix or deny the suffix and
    provide an explanation why it is not acceptable.
     
    C) If a registrant would like to change the paper type, paper weight,

     
    248
    ink color of the manifest instructions, or binding method of its
    manifest or continuation sheet subsequent to approval by USEPA
    pursuant to 40 CFR 262.21(e), as described in this subsection
    (b)(5) of this Section, then the registrant must submit three samples
    of the revised form for USEPA review and approval. If the
    approved registrant would like to use a new printer, the registrant
    must submit three manifest samples printed by the new printer,
    along with a brief description of the printer’s qualifications to print
    the manifest. USEPA will evaluate the manifests and either
    approve the registrant to print the forms as proposed or request
    additional information or modification to them before approval.
    USEPA will notify the registrant of its decision by mail. The
    registrant cannot use or distribute its revised forms until USEPA
    approves them.
     
    9) If, subsequent to its approval by USEPA pursuant to 40 CFR 262.21(e), as
    described in subsection (b)(5) of this Section, a registrant typesets its
    manifest or continuation sheet instead of using the electronic file of the
    forms provided by USEPA, it must submit three samples of the manifest
    or continuation sheet to the registry for approval. USEPA will evaluate
    the manifests or continuation sheets and either approve the registrant to
    print them as proposed or request additional information or modification
    to them before approval. USEPA will notify the registrant of its decision
    by mail. The registrant cannot use or distribute its typeset forms until
    USEPA approves them.
     
    10) USEPA may exempt a registrant from the requirement to submit form
    samples pursuant to 40 CFR 262.21(d) or (h)(3), as described in
    subsection (b)(4) or (b)(8)(C) of this Section, if USEPA is persuaded that
    a separate review of the registrant’s forms would serve little purpose in
    informing an approval decision (
    e.g.
    , a registrant certifies that it will print
    the manifest using the same paper type, paper weight, ink color of the
    instructions, and binding method of the form samples approved for some
    other registrant). A registrant may request an exemption from USEPA by
    indicating why an exemption is warranted.
     
    11) An approved registrant must notify USEPA by phone or email as soon as
    it becomes aware that it has duplicated tracking numbers on any manifests
    that have been used or distributed to other parties.
     
    12) If, subsequent to approval of a registrant by USEPA pursuant to 40 CFR
    262.21(e), as described in subsection (b)(5) of this Section, USEPA
    becomes aware that the approved paper type, paper weight, ink color of
    the instructions, or binding method of the registrant’s form is
    unsatisfactory, USEPA will contact the registrant and require
    modifications to the form.

     
    249
     
    13) Effects of non-compliance.
     
    A) USEPA may suspend and, if necessary, revoke printing privileges
    if we find that the registrant has done either of the following:
     
    i) The registrant has used or distributed forms that deviate
    from its approved form samples in regard to paper weight,
    paper type, ink color of the instructions, or binding method;
    or
     
    ii) The registrant exhibits a continuing pattern of behavior in
    using or distributing manifests that contain duplicate
    manifest tracking numbers.
     
    B) USEPA will send a warning letter to the registrant that specifies
    the date by which it must come into compliance with the
    requirements. If the registrant does not come in compliance by the
    specified date, USEPA will send a second letter notifying the
    registrant that USEPA has suspended or revoked its printing
    privileges. An approved registrant must provide information on its
    printing activities to the Agency and USEPA if requested.
     
    14) Required manifest instructions.
     
    A) Manifest Form 8700–22.
     
    i) The “Instructions for Generators” on Copy 6;
     
    ii) The “Instructions for International Shipment Block” and
    “Instructions for Transporters” on Copy 5; and
     
    iii) The “Instructions for Treatment, Storage, and Disposal
    Facilities” on Copy 4.
     
    B) Manifest Form 8700–22A.
     
    i) The “Instructions for Generators” on Copy 6;
     
    ii) The “Instructions for Transporters” on Copy 5; and
     
    iii) The “Instructions for Treatment, Storage, and Disposal
    Facilities” on Copy 4.
     
    BOARD NOTE: Subsection (b)(14)(A) and (b)(14)(B) are derived from
    40 CFR 262.21(f)(7)(i) and (f)(7)(ii) (2004), as amended at 70 Fed. Reg.

     
    250
    10776 (March 4, 2005). These provisions would normally correspond
    with subsections (b)(6)(G)(i) and (b)(6)(G)(ii) of this Section. The Board
    has moved 40 CFR 262.21(f)(7)(i) and (f)(7)(ii) to appear as subsections
    (b)(14)(A) and (b)(14)(B) of this Section to comport with Illinois
    Administrative Code codification requirements.
     
    BOARD NOTE: Subsection (a) is derived from 40 CFR 262.21 (2004), effective until
    September 5, 2006. Subsection (b) is derived from 40 CFR 262.21 (2005), effective September
    5, 2006.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 722.127 Waste Minimization Certification
     
    Effective September 5, 2006, a generator that initiates a shipment of hazardous waste must
    certify to one of the following statements in Item 15 of the uniform hazardous waste manifest:
     
    a) “I am a large quantity generator. I have a program in place to reduce the volume
    and toxicity of waste generated to the degree I have determined to be
    economically practicable and I have selected the practicable method of treatment,
    storage, or disposal currently available to me which minimizes the present and
    future threat to human health and the environment”; or
     
    b) “I am a small quantity generator. I have made a good faith effort to minimize my
    waste generation and select the best waste management method that is available
    to me and that I can afford.”
     
    BOARD NOTE: 35 Ill. Adm. Code 720.110 defines a “small quantity generator” as a generator
    that generates less than 1,000 kilograms of hazardous waste in any calendar month. There is no
    corresponding definition of “large quantity generator” in the federal regulations, but the Board
    interprets the term to mean a hazardous waste generator that is not a small quantity generator.
     
    (Source: Added at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART C: PRE-TRANSPORT REQUIREMENTS
     
    Section 722.130 Packaging
     
    Before transporting hazardous waste or offering hazardous waste for transportation off-site, a
    generator must package the waste in accordance with the applicable U.S. Department of
    Transportation (USDOT) regulations on packaging under 49 CFR 173 (Shippers--General
    Requirements for Shipments and Packages), 178 (Specifications for Packagings), and 179
    (Specifications for Tank Cars), each incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    251
    Section 722.131 Labeling
     
    Before transporting or offering hazardous waste for transportation off-site, a generator must label
    each package in accordance with the applicable USDOT regulations on hazardous materials under
    49 CFR 172 (Hazardous Materials Table, Special Provisions, Hazardous Materials
    Communications, Emergency Response Information, and Training Requirements), incorporated
    by reference in 35 Ill. Adm. Code 720.111(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 722.132 Marking
     
    a) Before transporting or offering hazardous waste for transportation off-site, a
    generator must mark each package of hazardous waste in accordance with the
    applicable USDOT regulations on hazardous materials under 49 CFR 172
    (Hazardous Materials Table, Special Provisions, Hazardous Materials
    Communications, Emergency Response Information, and Training
    Requirements), incorporated by reference in 35 Ill. Adm. Code 720.111(b);
     
    b) Marking small containers.
     
    1) Until September 5, 2006, before transporting hazardous waste or offering
    hazardous waste for transportation off-site, a generator must mark each
    container of 416 liters (110 gallons) or less that is used in such transportation
    with the following words and information displayed in accordance with the
    requirements of 49 CFR 172.304 (Marking Requirements), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b):
     
    HAZARDOUS WASTE -- Federal Law Prohibits Improper Disposal.
    If found, contact the nearest police or public safety authority or the
    U.S. Environmental Protection Agency.
     
    Generator’s Name and Address _______________________.
     
    Manifest Document Number _________________________.
     
    2) Effective September 5, 2006, before transporting hazardous waste or
    offering hazardous waste for transportation off-site, a generator must mark
    each container of 450 liters (110 gallons) or less that is used in such
    transportation with the following words and information displayed in
    accordance with the requirements of 49 CFR 172.304 (Marking
    Requirements), incorporated by reference in 35 Ill. Adm. Code
    720.111(b):
     
    HAZARDOUS WASTE--Federal Law Prohibits Improper Disposal.
    If found, contact the nearest police or public safety authority or the

     
    252
    U.S. Environmental Protection Agency.
     
    Generator’s Name and Address _______________________.
     
    Generator’s USEPA Identification Number ______________.
     
    Manifest Tracking Number ___________________________.
     
    BOARD NOTE: Subsection (b)(1) is derived from 40 CFR 262.32(b) (2004),
    effective until September 5, 2006. Subsection (b)(2) is derived from 40 CFR
    262.32(b) (2005), effective September 5, 2006.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 722.133 Placarding
     
    a) Until September 5, 2006, before transporting hazardous waste or offering hazardous
    waste for transportation off-site, a generator must placard or offer the initial
    transporter the appropriate placards according to Department of Transportation
    USDOT regulations for hazardous materials under subpart F of 49 CFR 172
    (Placarding), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    b) Effective September 5, 2006, before transporting hazardous waste or offering
    hazardous waste for transportation off-site, a generator must placard or offer the
    initial transporter the appropriate placards according to USDOT regulations for
    hazardous materials under subpart F of 49 CFR 172 (Placarding), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b). If placards are not required, a
    generator must mark each motor vehicle according to 49 CFR 171.3(b)(1)
    (Hazardous Waste), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    BOARD NOTE: Subsection (a) is derived from 40 CFR 262.33 (2004), effective until
    September 5, 2006. Subsection (b) is derived from 40 CFR 262.33 (2005), effective September
    5, 2006.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 722.134 Accumulation Time
     
    a) Except as provided in subsection (d), (e), (f), (g), (h), or (i) of this Section, a
    generator is exempt from all the requirements in Subparts G and H of 35 Ill. Adm.
    Code 725, except for 35 Ill. Adm. Code 725.211 and 725.214, and may
    accumulate hazardous waste on-site for 90 days or less without a permit or
    without having interim status, provided that the following conditions are fulfilled:
     
    1) The waste is placed in or on one of the following types of units, and the
    generator complies with the applicable requirements:

     
    253
     
    A) In containers, and the generator complies with Subparts I, AA, BB,
    and CC of 35 Ill. Adm. Code 725;
     
    B) In tanks, and the generator complies with Subparts J, AA, BB, and
    CC of 35 Ill. Adm. Code 725, except 35 Ill. Adm. Code 725.297(c)
    and 725.300;
     
    C) On drip pads, and the generator complies with Subpart W of 35 Ill.
    Adm. Code 725 and maintains the following records at the facility:
     
    i) A description of the procedures that will be followed to
    ensure that all wastes are removed from the drip pad and
    associated collection system at least once every 90 days;
    and
     
    ii) Documentation of each waste removal, including the
    quantity of waste removed from the drip pad and the sump
    or collection system and the date and time of removal; or
     
    D) In containment buildings, and the generator complies with Subpart
    DD of 35 Ill. Adm. Code 725 (has placed its Professional Engineer
    (PE) certification that the building complies with the design
    standards specified in 35 Ill. Adm. Code 725.1101 in the facility’s
    operating record prior to the date of initial operation of the unit).
    The owner or operator must maintain the following records at the
    facility:
     
    i) A written description of procedures to ensure that each
    waste volume remains in the unit for no more than 90 days,
    a written description of the waste generation and
    management practices for the facility showing that they are
    consistent with respect to the 90 day limit, and
    documentation that the procedures are complied with; or
     
    ii) Documentation that the unit is emptied at least once every
    90 days;
     
    BOARD NOTE: The Board placed the “in addition” hanging subsection
    that appears in the Federal federal rules after 40 CFR 262.34(a)(1)(iv)(B)
    in the introduction to subsection (a) of this Section.
     
    2) The date upon which each period of accumulation begins is clearly
    marked and visible for inspection on each container;
     
    3) While being accumulated on-site, each container and tank is labeled or

     
    254
    marked clearly with the words “Hazardous Waste”; and
     
    4) The generator complies with the requirements for owners or operators in
    Subparts C and D of 35 Ill. Adm. Code 725 and with 35 Ill. Adm. Code
    725.116 and 728.107(a)(5).
     
    b) A generator that accumulates hazardous waste for more than 90 days is an
    operator of a storage facility. Such a generator is subject to the requirements of
    35 Ill. Adm. Code 724 and 725 and the permit requirements of 35 Ill. Adm. Code
    702, 703, and 705, unless the generator has been granted an extension of the 90-
    day period. If hazardous wastes must remain on-site for longer than 90 days due
    to unforeseen, temporary, and uncontrollable circumstances, the generator may
    seek an extension of up to 30 days by means of a variance or provisional variance,
    pursuant to Sections 35(b), 36(c), and 37(b) of the Environmental Protection Act
    [415 ILCS 5/35(b), 36(c), and 37(b)] and 35 Ill. Adm. Code 180 (Agency
    procedural regulations).
     
    c) Accumulation near the point of generation.
     
    1) A generator may accumulate as much as 55 gallons of hazardous waste or
    one quart of acutely hazardous waste listed in 35 Ill. Adm. Code
    721.133(e) in containers at or near any point of generation where wastes
    initially accumulate that is under the control of the operator of the process
    generating the waste without a permit or interim status and without
    complying with subsection (a) of this Section, provided the generator does
    the following:
     
    A) The generator complies with 35 Ill. Adm. Code 725.271, 725.272,
    and 725.273(a); and
     
    B) The generator marks the containers either with the words
    “Hazardous Waste” or with other words that identify the contents
    of the containers.
     
    2) A generator that accumulates either hazardous waste or acutely hazardous
    waste listed in 35 Ill. Adm. Code 721.133(e) in excess of the amounts
    listed in subsection (c)(1) of this Section at or near any point of generation
    must, with respect to that amount of excess waste, comply within three
    days with subsection (a) of this Section or other applicable provisions of
    this Chapter. During the three day period the generator must continue to
    comply with subsection (c)(1) of this Section. The generator must mark
    the container holding the excess accumulation of hazardous waste with the
    date the excess amount began accumulating.
     
    d) A generator that generates greater than 100 kilograms but less than 1,000
    kilograms of hazardous waste in a calendar month may accumulate hazardous

     
    255
    waste on-site for 180 days or less without a permit or without having interim
    status provided that the following conditions are fulfilled:
     
    1) The quantity of waste accumulated on-site never exceeds 6,000 kilograms;
     
    2) The generator complies with the requirements of Subpart I of 35 Ill. Adm.
    Code 725 (except 35 Ill. Adm. Code 725.276 and 725.278);
     
    3) The generator complies with the requirements of 35 Ill. Adm. Code
    725.301;
     
    4) The generator complies with the requirements of subsections (a)(2) and
    (a)(3) of this Section, Subpart C of 35 Ill. Adm. Code 725, and 35 Ill.
    Adm. Code 728.107(a)(5); and
     
    5) The generator complies with the following requirements:
     
    A) At all times there must be at least one employee either on the
    premises or on call (i.e., available to respond to an emergency by
    reaching the facility within a short period of time) with the
    responsibility for coordinating all emergency response measures
    specified in subsection (d)(5)(D) of this Section. The employee is
    the emergency coordinator.
     
    B) The generator must post the following information next to the
    telephone:
     
    i) The name and telephone number of the emergency
    coordinator;
     
    ii) Location of fire extinguishers and spill control material
    and, if present, fire alarm; and
     
    iii) The telephone number of the fire department, unless the
    facility has a direct alarm.
     
    C) The generator must ensure that all employees are thoroughly
    familiar with proper waste handling and emergency procedures,
    relevant to their responsibilities during normal facility operations
    and emergencies.
     
    D) The emergency coordinator or designee must respond to any
    emergencies that arise. The following are applicable responses:
     
    i) In the event of a fire, call the fire department or attempt to
    extinguish it using a fire extinguisher;

     
    256
     
    ii) In the event of a spill, contain the flow of hazardous waste
    to the extent possible and, as soon as is practicable, clean
    up the hazardous waste and any contaminated materials or
    soil; and
     
    iii) In the event of a fire, explosion, or other release that could
    threaten human health outside the facility, or when the
    generator has knowledge that a spill has reached surface
    water, the generator must immediately notify the National
    Response Center (using its 24-hour toll free number 800-
    424-8802).
     
    E) A report to the National Response Center pursuant to subsection
    (d)(5)(D)(iii) of this Section must include the following
    information:
     
    i) The name, address, and USEPA identification number
    (Section 722.112 of this Part) of the generator;
     
    ii) The date, time, and type of incident (e.g., spill or fire);
     
    iii) The quantity and type of hazardous waste involved in the
    incident; the extent of injuries, if any; and
     
    iv) The estimated quantity and disposition of recoverable
    materials, if any.
     
    BOARD NOTE: The Board has codified 40 CFR
    262.34(d)(5)(iv)(C)(1) through (d)(5)(iv)(C)(5) as subsections
    (d)(5)(E)(i) through (d)(5)(E)(iv) because Illinois Administrative
    Code codification requirements do not allow the use of a fifth level
    of subsection indents.
     
    e) A generator that generates greater than 100 kilograms but less than 1,000
    kilograms of hazardous waste in a calendar month and that must transport the
    waste or offer the waste for transportation over a distance of 200 miles or more
    for off-site treatment, storage, or disposal may accumulate hazardous waste on-
    site for 270 days or less without a permit or without having interim status,
    provided that the generator complies with the requirements of subsection (d) of
    this Section.
     
    f) A generator that generates greater than 100 kilograms but less than 1,000
    kilograms of hazardous waste in a calendar month and that accumulates
    hazardous waste in quantities exceeding 6,000 kg or accumulates hazardous waste
    for more than 180 days (or for more than 270 days if the generator must transport

     
    257
    the waste or offer the waste for transportation over a distance of 200 miles or
    more) is an operator of a storage facility and is subject to the requirements of 35
    Ill. Adm. Code 724 and 725 and the permit requirements of 35 Ill. Adm. Code
    703, unless the generator has been granted an extension to the 180-day (or 270-
    day if applicable) period. If hazardous wastes must remain on-site for longer than
    180 days (or 270 days if applicable) due to unforeseen, temporary, and
    uncontrollable circumstances, the generator may seek an extension of up to 30
    days by means of variance or provisional variance pursuant to Sections 35(b),
    36(c), and 37(b) of the Environmental Protection Act [415 ILCS 5/35(b), 36(c),
    and 37(b)].
     
    g) A generator that generates 1,000 kilograms or greater of hazardous waste per
    calendar month which also generates wastewater treatment sludges from
    electroplating operations that meet the listing description for the RCRA hazardous
    waste code F006, may accumulate F006 waste on-site for more than 90 days, but
    not more than 180 days, without a permit or without having interim status
    provided that the generator fulfills the following conditions:
     
    1) The generator has implemented pollution prevention practices that reduce
    the amount of any hazardous substances, pollutants, or contaminants
    entering F006 or otherwise released to the environment prior to its
    recycling;
     
    2) The F006 waste is legitimately recycled through metals recovery;
     
    3) No more than 20,000 kilograms of F006 waste is accumulated on-site at
    any one time; and
     
    4) The F006 waste is managed in accordance with the following conditions:
     
    A) The F006 waste is placed in one of the following containing
    devices:
     
    i) In containers and the generator complies with the
    applicable requirements of Subparts I, AA, BB, and CC of
    35 Ill. Adm. Code 725;
     
    ii) In tanks and the generator complies with the applicable
    requirements of Subparts J, AA, BB, and CC of 35 Ill.
    Adm. Code 725, except 35 Ill. Adm. Code 725.297(c) and
    725.300; or
     
    iii) In containment buildings, and the generator complies with
    Subpart DD of 35 Ill. Adm. Code 725 and has placed its
    professional engineer certification that the building
    complies with the design standards specified in 35 Ill.

     
    258
    Adm. Code 725.1101 in the facility’s operating record prior
    to operation of the unit. The owner or operator must
    maintain the records listed in subsection (g)(4)(F) of this
    Section at the facility.
     
    B) In addition, such a generator is exempt from all the requirements in
    Subparts G and H of 35 Ill. Adm. Code 725, except for 35 Ill.
    Adm. Code 725.211 and 725.214;
     
    C) The date upon which each period of accumulation begins is clearly
    marked and visible for inspection on each container;
     
    D) While being accumulated on-site, each container and tank is
    labeled or marked clearly with the words, “Hazardous Waste”; and
     
    E) The generator complies with the requirements for owners or
    operators in Subparts C and D of 35 Ill. Adm. Code 725, with 35
    Ill. Adm. Code 725.116, and with 35 Ill. Adm. Code 728.107(a)(5).
     
    F) Required records for a containment building:
     
    i) A written description of procedures to ensure that the F006
    waste remains in the unit for no more than 180 days, a
    written description of the waste generation and
    management practices for the facility showing that they are
    consistent with the 180-day limit, and documentation that
    the generator is complying with the procedures; or
     
    ii) Documentation that the unit is emptied at least once every
    180 days.
     
    BOARD NOTE: The Board has codified 40 CFR
    262.34(g)(4)(i)(C)(
    1
    ) and (g)(4)(i)(C)(
    2
    ) as subsections
    (g)(4)(F)(i) and (g)(4)(F)(ii) because Illinois Administrative Code
    codification requirements do not allow the use of a fifth level of
    subsection indents.
     
    h) A generator that generates 1,000 kilograms or greater of hazardous waste per
    calendar month, which also generates wastewater treatment sludges from
    electroplating operations that meet the listing description for the RCRA hazardous
    waste code F006, and which must transport this waste or offer this waste for
    transportation over a distance of 200 miles or more for off-site metals recovery
    may accumulate F006 waste on-site for more than 90 days, but not more than 270
    days, without a permit or without having interim status if the generator complies
    with the requirements of subsections (g)(1) through (g)(4) of this Section.
     

     
    259
    i) A generator accumulating F006 in accordance with subsections (g) and (h) of this
    Section that accumulates F006 waste on-site for more than 180 days (or for more
    than 270 days if the generator must transport this waste or offer this waste for
    transportation over a distance of 200 miles or more) or which accumulates more
    than 20,000 kilograms of F006 waste on-site is an operator of a storage facility,
    and such a generator is subject to the requirements of 35 Ill. Adm. Code 724 and
    725 and the permit requirements of 35 Ill. Adm. Code 702 and 703, unless the
    generator has been granted an extension to the 180-day (or 270-day if applicable)
    period or an exception to the 20,000 kilogram accumulation limit.
     
    1) On a case-by-case basis, the Agency must grant a provisional variance that
    allows an extension of the accumulation time up to an additional 30 days
    pursuant to Sections 35(b), 36(c), and 37(b) of the Act [415 ILCS 5/35(b),
    36(c), and 37(b)] if it finds that the F006 waste must remain on-site for
    longer than 180 days (or 270 days if applicable) due to unforeseen,
    temporary, and uncontrollable circumstances.
     
    2) On a case-by-case basis, the Agency must grant a provisional variance
    pursuant to Sections 35(b), 36(c), and 37(b) of the Act [415 ILCS 5/35(b),
    36(c), and 37(b)] that allows an exception to the 20,000 kilogram
    accumulation limit if the Agency finds that more than 20,000 kilograms of
    F006 waste must remain on-site due to unforeseen, temporary, and
    uncontrollable circumstances.
     
    3) A generator must follow the procedure of 35 Ill. Adm. Code 180 (Agency
    procedural rules) when seeking a provisional variance under subsection
    (i)(1) or (i)(2) of this Section.
     
    j) A member of the federal National Environmental Performance Track program
    that generates 1,000 kg or greater of hazardous waste per month (or one kilogram
    or more of acute hazardous waste) may accumulate hazardous waste on-site
    without a permit or interim status for an extended period of time, provided that
    the following conditions are fulfilled:
     
    1) The generator accumulates the hazardous waste for no more than 180
    days, or for no more than 270 days if the generator must transport the
    waste (or offer the waste for transport) more than 200 miles from the
    generating facility;
     
    2) The generator first notifies USEPA Region 5 and the Agency in writing of
    its intent to begin accumulation of hazardous waste for extended time
    periods under the provisions of this Section. Such advance notice must
    include the following information:
     
    A) The name and USEPA ID number of the facility and specification
    of when the facility will begin accumulation of hazardous wastes

     
    260
    for extended periods of time in accordance with this Section;
     
    B) A description of the types of hazardous wastes that will be
    accumulated for extended periods of time and the units that will be
    used for such extended accumulation;
     
    C) A statement that the facility has made all changes to its operations;
    procedures, including emergency preparedness procedures; and
    equipment, including equipment needed for emergency
    preparedness, that will be necessary to accommodate extended
    time periods for accumulating hazardous wastes; and
     
    D) If the generator intends to accumulate hazardous wastes on-site for
    up to 270 days, a certification that a facility that is permitted (or
    operating under interim status) under 35 Ill. Adm. Code 702 and
    703, federal 40 CFR 270, or the corresponding regulations of a
    sister state to receive these wastes is not available within 200 miles
    of the generating facility;
     
    3) The waste is managed in the following types of units:
     
    A) Containers, in accordance with the applicable requirements of
    Subparts I, AA, BB, and CC of 35 Ill. Adm. Code 725 and 35 Ill.
    Adm. Code 724.275;
     
    B) Tanks, in accordance with the requirements of Subparts J, AA, BB,
    and CC of 35 Ill. Adm. Code 725, except for Sections 725.297(c)
    and Section 725.300;
     
    C) Drip pads, in accordance with Subpart W of 35 Ill. Adm. Code
    725; or
     
    D) Containment buildings, in accordance with Subpart DD of 35 Ill.
    Adm. Code 725;
     
    4) The quantity of hazardous waste that is accumulated for extended time
    periods at the facility does not exceed 30,000 kg;
     
    5) The generator maintains the following records at the facility for each unit
    used for extended accumulation times:
     
    A) A written description of procedures to ensure that each waste
    volume remains in the unit for no more than 180 days (or 270
    days, as applicable), a description of the waste generation and
    management practices at the facility showing that they are
    consistent with the extended accumulation time limit, and

     
    261
    documentation that the procedures are complied with; or
     
    B) Documentation that the unit is emptied at least once every 180
    days (or 270 days, if applicable);
     
    6) Each container or tank that is used for extended accumulation time periods
    is labeled or marked clearly with the words “Hazardous Waste,” and for
    each container the date upon which each period of accumulation begins is
    clearly marked and visible for inspection;
     
    7) The generator complies with the requirements for owners and operators in
    Subparts C and D of 35 Ill. Adm. Code 725, 35 Ill. Adm. Code 725.116,
    and 35 Ill. Adm. Code 728.107(a)(5). In addition, such a generator is
    exempt from all the requirements in Subparts G and H of 35 Ill. Adm.
    Code 725, except for 35 Ill. Adm. Code 725.211 and 725.214;
     
    8) The generator has implemented pollution prevention practices that reduce
    the amount of any hazardous substances, pollutants, or contaminants
    released to the environment prior to its recycling, treatment, or disposal;
    and
     
    9) The generator includes the following information with its federal National
    Environmental Performance Track Annual Performance Report, which
    must be submitted to the USEPA Region 5 and the Agency:
     
    A) Information on the total quantity of each hazardous waste
    generated at the facility that has been managed in the previous year
    according to extended accumulation time periods;
     
    B) Information for the previous year on the number of off-site
    shipments of hazardous wastes generated at the facility, the types
    and locations of destination facilities, how the wastes were
    managed at the destination facilities (e.g., recycling, treatment,
    storage, or disposal), and what changes in on-site or off-site waste
    management practices have occurred as a result of extended
    accumulation times or other pollution prevention provisions of this
    Section;
     
    C) Information for the previous year on any hazardous waste spills or
    accidents occurring at extended accumulation units at the facility,
    or during off-site transport of accumulated wastes; and
     
    D) If the generator intends to accumulate hazardous wastes on-site for
    up to 270 days, a certification that a facility that is permitted (or
    operating under interim status) under 35 Ill. Adm. Code 702 and
    703, federal 40 CFR 270, or the corresponding regulations of a

     
    262
    sister state to receive these wastes is not available within 200 miles
    of the generating facility.
     
    BOARD NOTE: The National Environmental Performance Track program is
    operated exclusively by USEPA. USEPA established the program in 2000 (see
    65 Fed. Reg. 41655 (July 6, 2000)) and amended it in 2004 (see 69 Fed. Reg.
    27922 (May 17, 2004)). USEPA confers membership in the program on
    application of interested and eligible entities. Information about the program is
    available from a website maintained by USEPA:
    www.epa.gov/performancetrack.
     
    k) If the Agency finds that hazardous wastes must remain on-site at a federal
    National Environmental Performance Track member facility for longer than the
    180 days (or 270 days, if applicable) allowed under subsection (j) of this Section
    due to unforeseen, temporary, and uncontrollable circumstances, it must grant an
    extension to the extended accumulation time period of up to 30 days on a case-by-
    case basis by a provisional variance pursuant to Sections 35(b), 36(c), and 37(b)
    of the Act [415 ILCS 5/35(b), 36(c), and 37(b)].
     
    1) If a generator that is a member of the federal National Environmental
    Performance Track program withdraws from the National Environmental
    Performance Track program or if USEPA Region 5 terminates a generator’s
    membership, the generator must return to compliance with all otherwise
    applicable hazardous waste regulations as soon as possible, but no later than six
    months after the date of withdrawal or termination.
     
    m) Effective September 5, 2006, a generator that sends a shipment of hazardous
    waste to a designated facility with the understanding that the designated facility
    can accept and manage the waste and which later receives that shipment back as a
    rejected load or residue in accordance with the manifest discrepancy provisions of
    35 Ill. Adm. Code 724.172 or 725.172 may accumulate the returned waste on-site
    in accordance with subsections (a) and (b) or (d), (e), and (f) of this Section,
    depending on the amount of hazardous waste on-site in that calendar month.
    Upon receipt of the returned shipment, the generator must sign the appropriate of
    the following:
     
    1) Item 18c of the manifest, if the transporter returned the shipment using the
    original manifest; or
     
    2) Item 20 of the manifest, if the transporter returned the shipment using a
    new manifest.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    263
    SUBPART E: EXPORTS OF HAZARDOUS WASTE
     
    Section 722.153 Notification of Intent to Export
     
    a) A primary exporter of hazardous waste must notify USEPA in accordance with
    federal 40 CFR 262.53 (Notification of Intent to Export), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    b) The primary exporter must send the Agency a copy of each notice sent to USEPA
    pursuant to subsection (b) of this Section.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 722.154 Special Manifest Requirements
     
    a) A primary exporter must comply with the manifest requirements as specified in
    federal 40 CFR 262.54 (Special Manifest Requirements), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    b) The primary exporter must send a copy of the manifest to the Agency.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 722.155 Exception Report
     
    a) In lieu of the requirements of Section 722.142, a primary exporter must file an
    exception report with USEPA as provided by federal 40 CFR 262.55 (Exception
    Reports), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    b) The primary exporter must send a copy of the exception report to the Agency.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 722.156 Annual Reports
     
    a) Primary exporters of hazardous waste must file with USEPA, no later than March
    1 of each year, a report as specified in federal 40 CFR 262.56 (Annual Reports),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    b) The primary exporter must send the Agency a copy of each report sent to USEPA.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 722.157 Recordkeeping
     
    For all exports a primary exporter must comply with the recordkeeping requirements of federal 40

     
    264
    CFR 262.57 (Recordkeeping), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    (Source: Amended at 29 Ill. Reg. 6312, effective April 22, 2005)
     
    SUBPART F: IMPORTS OF HAZARDOUS WASTE
     
    Section 722.160 Imports of Hazardous Waste
     
    a) Any person that imports hazardous waste from a foreign country into the United
    States must comply with the requirements of this Part and the special requirements of
    this Subpart F.
     
    b) When importing hazardous waste, a person must meet all the requirements of Section
    722.120(a) for the manifest, except that the following information items are
    substituted:
     
    1) In place of the generator’s name, address, and USEPA identification number,
    the name and address of the foreign generator and the importer’s name,
    address, and USEPA identification number must be used.
     
    2) In place of the generator’s signature on the certification statement, the United
    States importer or the importer’s agent must sign and date the certification
    and obtain the signature of the initial transporter.
     
    c) A person that imports hazardous waste must obtain the manifest form, as provided in
    Section 722.121(a) or (b)(7).
     
    d) Effective September 5, 2006, in the International Shipments block of the
    manifest, the importer must check the import box and enter the point of entry (city
    and State) into the United States.
     
    e) Effective September 5, 2006, the importer must provide the transporter with an
    additional copy of the manifest to be submitted by the receiving facility to
    USEPA in accordance with 35 Ill. Adm. Code 724.171(a)(2)(C) or
    725.171(a)(2)(C).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART H: TRANSFRONTIER SHIPMENTS OF HAZARDOUS WASTE
    FOR RECOVERY WITHIN THE OECD
     
    Section 722.181 Definitions
     
    The following definitions apply to this Subpart H:
     
    “Amber-list controls” means the controls listed in Section section IV of the

     
    265
    Annex annex to the OECD Council Decision C(92)39/FINAL, incorporated by
    reference in 35 Ill. Adm. Code 720.111(a).
     
    “Amber-list waste” means a waste listed in the OECD “Amber List of Wastes,”
    Appendix 4 to the OECD Council Decision C(92)39/FINAL, incorporated by
    reference in 35 Ill. Adm. Code 720.111(a).
     
    “Competent authorities” means the regulatory authorities of concerned countries
    having jurisdiction over transfrontier movements of wastes destined for recovery
    operations.
     
    “Concerned countries” means the exporting and importing OECD member
    countries and any OECD member countries of transit.
     
    “Consignee” means the person to whom possession or other form of legal control
    of the waste is assigned at the time the waste is received in the importing country.
     
    “Country of transit” means any designated OECD country in Section
    722.158(a)(1) and (a)(2) other than the exporting or importing country across
    which a transfrontier movement of wastes is planned or takes place.
     
    “Exporting country” means any designated OECD member country in Section
    722.158(a)(1) from which a transfrontier movement of wastes is planned or has
    commenced.
     
    “Green-list controls” means the controls listed in Section section III of the Annex
    annex to the OECD Council Decision C(92)39/FINAL, incorporated by reference
    in 35 Ill. Adm. Code 720.111(a).
     
    “Green-list waste” means a waste listed in the OECD “Green List of Wastes,”
    Appendix 3 to the OECD Council Decision C(92)39/FINAL, incorporated by
    reference in 35 Ill. Adm. Code 720.111(a).
     
    “Importing country” means any designated OECD country in Section
    722.158(a)(1) to which a transfrontier movement of wastes is planned or takes
    place for the purpose of submitting the wastes to recovery operations therein.
     
    “Notifier” means the person under the jurisdiction of the exporting country that
    has, or will have at the time the planned transfrontier movement commences,
    possession or other forms of legal control of the wastes and that proposes their
    transfrontier movement for the ultimate purpose of submitting them to recovery
    operations. When the United States (U.S.) is the exporting country, notifier is
    interpreted to mean a person domiciled in the U.S.
     
    “OECD area” means all land or marine areas under the national jurisdiction of
    any designated OECD member country in Section 722.158. When the regulations

     
    266
    refer to shipments to or from an OECD country, this means OECD area.
     
    “Recognized trader” means a person that, with appropriate authorization of
    concerned countries, acts in the role of principal to purchase and subsequently sell
    wastes; this person has legal control of such wastes from time of purchase to time
    of sale; such a person may act to arrange and facilitate transfrontier movements of
    wastes destined for recovery operations.
     
    “Recovery facility” means an entity that, under applicable domestic law, is
    operating or is authorized to operate in the importing country to receive wastes
    and to perform recovery operations on them.
     
    “Recovery operations” means activities leading to resource recovery, recycling,
    reclamation, direct re-use, or alternative uses, as listed in Table 2.B of the Annex
    annex of OECD Council Decision C(88)90(Final), incorporated by reference in
    35 Ill. Adm. Code 720.111(a), which include the following activities:
     
    R1 Use as a fuel (other than in direct incineration) or other means to
    generate energy,
     
    R2 Solvent reclamation or regeneration,
     
    R3 Recycling or reclamation of organic substances that are not used as
    solvents,
     
    R4 Recycling or reclamation of metals and metal compounds,
     
    R5 Recycling or reclamation of other inorganic materials,
     
    R6 Regeneration of acids or bases,
     
    R7 Recovery of components used for pollution control,
     
    R8 Recovery of components from catalysts,
     
    R9 Used oil re-refining or other reuses of previously used oil,
     
    R10 Land treatment resulting in benefit to agriculture or ecological
    improvement,
     
    R11 Uses of residual materials obtained from any of the operations
    numbered R1 through R10,
     
    R12 Exchange of wastes for submission to any of the operations
    numbered R1 through R11, and
     

     
    267
    R13 Accumulation of material intended for any operation in Table 2.B.
     
    “Red-list controls” means the controls listed in Section section V of the Annex
    annex to the OECD Council Decision C(92)39/FINAL, incorporated by reference
    in 35 Ill. Adm. Code 720.111(a).
     
    “Red-list waste” means a waste listed in the OECD Green “Red List of Wastes,”
    Appendix 5 to the OECD Council Decision C(92)39/FINAL, incorporated by
    reference in 35 Ill. Adm. Code 720.111(a).
     
    “Transfrontier movement” means any shipment of wastes destined for recovery
    operations from an area under the national jurisdiction of one OECD member
    country to an area under the national jurisdiction of another OECD member
    country.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 722.187 Reporting and Recordkeeping
     
    a) Annual reports. For all waste movements subject to this Subpart H, persons (e.g.,
    notifiers, recognized traders, etc.) that meet the definition of primary exporter in
    Section 722.151 must file an annual report with the Office of Enforcement and
    Compliance Assurance, Office of Compliance, Enforcement Planning, Targeting
    and Data Division (2222A), U.S. Environmental Protection Agency, 401 M St.,
    SW, Washington, DC 20460 and the Illinois Environmental Protection Agency,
    Bureau of Land, Division of Land Pollution Control, P.O. Box 19276,
    Springfield, IL 62794, no later than March 1 of each year summarizing the types,
    quantities, frequency, and ultimate destination of all such hazardous waste
    exported during the previous calendar year. (If the primary exporter is required to
    file an annual report for waste exports that are not covered under this Subpart H,
    the person filing may include all export information in one report provided the
    following information on exports of waste destined for recovery within the
    designated OECD member countries is contained in a separate Section). Such
    reports must include the following information:
     
    1) The USEPA identification number, name, and mailing and site address of
    the notifier filing the report;
     
    2) The calendar year covered by the report;
     
    3) The name and site address of each final recovery facility;
     
    4) By final recovery facility, for each hazardous waste exported, a
    description of the hazardous waste, the USEPA hazardous waste number
    (from Subpart C or D of 35 Ill. Adm. Code 721); the designation of waste
    types from the OECD waste list and applicable waste code from the

     
    268
    OECD lists, as described in the annex to OECD Council Decision
    C(88)90/FINAL, as amended by C(94)152/FINAL, incorporated by
    reference in 35 Ill. Adm. Code 720.111(a), USDOT hazard class; the name
    and USEPA identification number (where applicable) for each transporter
    used; the total amount of hazardous waste shipped pursuant to this Subpart
    H; and number of shipments pursuant to each notification;
     
    5) In even numbered years, for each hazardous waste exported, except for
    hazardous waste produced by exporters of greater than 100 kilograms (kg)
    but less than 1,000 kg in a calendar month, and except for hazardous waste
    for which information was already provided pursuant to Section 722.141:
     
    A) A description of the efforts undertaken during the year to reduce
    the volume and toxicity of waste generated; and
     
    B) A description of the changes in volume and toxicity of the waste
    actually achieved during the year in comparison to previous years
    to the extent such information is available for years prior to 1984;
    and
     
    6) A certification signed by the person acting as primary exporter that states
    as follows:
     
    “I certify under penalty of law that I have personally examined and am
    familiar with the information submitted in this and all attached documents,
    and that based on my inquiry of those individuals immediately responsible
    for obtaining the information, I believe that the submitted information is
    true, accurate, and complete. I am aware that there are significant
    penalties for submitting false information including the possibility of fine
    and imprisonment.”
     
    b) Exception reports. Any person that meets the definition of primary exporter in
    Section 722.151 must file with USEPA and the Agency an exception report in lieu
    of the requirements of Section 722.142 if any of the following occurs:
     
    1) The person has not received a copy of the tracking documentation signed
    by the transporter stating point of departure of the waste from the United
    States within 45 days from the date it was accepted by the initial
    transporter;
     
    2) Within 90 days from the date the waste was accepted by the initial
    transporter, the notifier has not received written confirmation from the
    recovery facility that the hazardous waste was received; or
     
    3) The waste is returned to the United States.
     

     
    269
    c) Recordkeeping.
     
    1) Persons that meet the definition of primary exporter in Section 722.151
    must keep the following records:
     
    A) A copy of each notification of intent to export and all written
    consents obtained from the competent authorities of concerned
    countries, for a period of at least three years from the date the
    hazardous waste was accepted by the initial transporter;
     
    B) A copy of each annual report, for a period of at least three years
    from the due date of the report; and
     
    C) A copy of any exception reports and a copy of each confirmation
    of delivery (i.e., tracking documentation) sent by the recovery
    facility to the notifier, for at least three years from the date the
    hazardous waste was accepted by the initial transporter or received
    by the recovery facility, whichever is applicable.
     
    2) The periods of retention referred to in this Section are extended
    automatically during the course of any unresolved enforcement action
    regarding the regulated activity or as requested by USEPA or the Agency.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 722.Appendix A Hazardous Waste Manifest
     
    The Agency must prepare manifest forms based on the appendix to federal 40 CFR 262, Appendix,
    incorporated by reference in 35 Ill. Adm. Code 720.111(b), with such changes as are necessary
    under Illinois law.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
     
    PART 723
    STANDARDS APPLICABLE TO TRANSPORTERS OF HAZARDOUS
    WASTE
     
    SUBPART A: GENERAL
    Section
    723.110 Scope
    723.111 USEPA Identification Number

     
    270
    723.112 Transfer Facility Requirements
     
    SUBPART B: COMPLIANCE WITH THE MANIFEST SYSTEM AND
    RECORDKEEPING
    Section
    723.120 The Manifest System
    723.121 Compliance with the Manifest
    723.122 Recordkeeping
     
    SUBPART C: HAZARDOUS WASTE DISCHARGES
    Section
    723.130 Immediate Action
    723.131 Discharge Clean Up Cleanup
     
    AUTHORITY: Implementing Section 22.4 and authorized by Section 27 of the Environmental
    Protection Act [415 ILCS 5/22.4 and 27].
     
    SOURCE: Adopted in R81-22, 43 PCB 427, at 5 Ill. Reg. 9781, effective May 17, 1982;
    amended and codified in R81-22, 45 PCB 17, at 6 Ill. Reg. 4828, effective May 17, 1982;
    amended in R84-9, at 9 Ill. Reg. 11961, effective July 24, 1985; amended in R86-19, at 10 Ill.
    Reg. 20718, effective December 2, 1986; amended in R86-46 at 11 Ill. Reg. 13570, effective
    August 4, 1987; amended in R87-5 at 11 Ill. Reg. 19412, effective November 12, 1987; amended
    in R95-6 at 19 Ill. Reg. 9945, effective June 27, 1995; amended in R96-10/R97-3/R97-5 at 22 Ill.
    Reg. 589, effective December 16, 1997; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17965,
    effective September 28, 1998; amended in R06-5/R06-6/R06-7 at 30 Ill. Reg. ________,
    effective ______________________.
     
     
    SUBPART A: GENERAL
     
    Section 723.110 Scope
     
    a) These regulations establish standards which apply to persons transporting
    hazardous waste into, out of or through Illinois if the transportation requires a
    manifest under 35 Ill. Adm. Code 722.
     
    b) These regulations do not apply to on-site transportation of hazardous waste by
    generators or by owners or operators of permitted hazardous waste management
    facilities.
     
    c) A transporter of hazardous waste must also comply with 35 Ill. Adm. Code 722,
    “Standards Applicable to Generators of Hazardous Waste,”, if he either of the
    following occurs:
     
    1) Transports
    It transports hazardous waste into the United States from
    abroad; or

     
    271
     
    2) Mixes
    It mixes hazardous waste of different DOT shipping descriptions by
    placing them into a single container.
     
    BOARD NOTE: Transporters that store hazardous waste are required to
    comply with the storage standards in 35 Ill. Adm. Code 724 and 725 and
    the permit requirements of 40 CFR 122.
     
    d) A transporter of hazardous waste subject to the manifesting requirements of 35 Ill.
    Adm. Code 722 or the waste management standards of 35 Ill. Adm. Code 733 that
    is being imported from or exported to any of the countries listed in 35 Ill. Adm.
    Code 722.158(a)(1) for purposes of recovery is subject to this Subpart and to all
    other relevant requirements of 35 Ill. Adm. Code 722.Subpart H, including, but
    not limited to, 35 Ill. Adm. Code 722.184 for tracking documents.
     
    e) The regulations in this Part do not apply to transportation during an explosives or
    munitions emergency response, conducted in accordance with 35 Ill. Adm. Code
    724.101(g)(8)(A)(iv) or (g)(8)(D) or 35 Ill. Adm. Code 725.101(c)(11)(A)(iv) or
    (c)(11)(D), and 35 Ill. Adm. Code 703.121(a)(4) or (c).
     
    f) 35 Ill. Adm. Code 726.303 identifies how the requirements of this Part apply to
    military munitions classified as solid waste under 35 Ill. Adm. Code 726.302.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART B: COMPLIANCE WITH THE MANIFEST SYSTEM AND
    RECORDKEEPING
     
    Section 723.120 The Manifest System
     
    a) No acceptance without a manifest.
     
    1) The following manifest requirements apply until September 5, 2006:
     
    1A) A transporter shall may not accept hazardous waste from a
    generator unless it is accompanied by a manifest signed in
    accordance with the provisions of 35 Ill. Adm. Code 722.120. In
    the case of exports other than those subject to 35 Ill. Adm. Code
    722.Subpart H, a transporter shall may not accept such waste from
    a primary exporter or other person:
     
    Ai) If the transporter knows the shipment does not conform
    with the USEPA Acknowledgement of Consent (as defined
    in 35 Ill. Adm. Code 722.151); and
     
    Bii) Unless, in addition to a manifest signed in accordance with

     
    272
    35 Ill. Adm. Code 722.120, the waste is also accompanied
    by a USEPA Acknowledgement of Consent which, except
    for shipment by rail, is attached to the manifest (or shipping
    paper for exports by water (bulk shipment)).
     
    2B) For exports of hazardous waste subject to the requirements of
    Subpart H of 35 Ill. Adm. Code 722.Subpart H, a transporter may
    not accept hazardous waste without a tracking document that
    includes all information required by 35 Ill. Adm. Code 722.184.
     
    2) The following manifest requirements apply effective September 5, 2006:
     
    A) Manifest requirement. A transporter may not accept hazardous
    waste from a generator unless the transporter is also provided with
    a manifest signed in accordance with the provisions of 35 Ill. Adm.
    Code 723.123.
     
    B) Exports.
     
    i) In the case of exports other than those subject to Subpart H
    of 35 Ill. Adm. Code 722, a transporter may not accept
    such waste from a primary exporter or other person if the
    transporter knows that the shipment does not conform to
    the USEPA Acknowledgement of Consent; and unless, in
    addition to a manifest signed by the generator as provided
    in this Section, the transporter must also be provided with a
    USEPA Acknowledgement of Consent which, except for
    shipment by rail, is attached to the manifest (or shipping
    paper for exports by water (bulk shipment)).
     
    ii) For exports of hazardous waste subject to the requirements
    of 35 Ill. Adm. Code 722.Subpart H, a transporter may not
    accept hazardous waste without a tracking document that
    includes all information required by 35 Ill. Adm. Code
    722.184.
     
    BOARD NOTE: Subsection (a)(1) corresponds with 40 CFR 263.20(a) (2004),
    effective until September 5, 2006. Subsection (a)(2) corresponds with 40 CFR
    263.20(a) (2005), effecctive September 5, 2006. The Board omitted 40 CFR
    263.20(a)(3) (2005), since that provision merely stated the September 5, 2006
    effective date for the newer manifest requirements.
     
    b) Before transporting the hazardous waste, the transporter shall must sign and date
    the manifest acknowledging acceptance of the hazardous waste from the
    generator. The transporter shall must return a signed copy to the generator before
    leaving the generator’s property.

     
    273
     
    c) The transporter shall must ensure that the manifest accompanies the hazardous
    waste. In the case of exports, the transporter shall must ensure that a copy of the
    USEPA Acknowledgement of Consent also accompanies the hazardous waste.
     
    d) A transporter that delivers a hazardous waste to another transporter or to the
    designated facility shall must do the following:
     
    1) Obtain
    It must obtain the date of delivery and the handwritten signature of
    that transporter or of the owner or operator of the designated facility on
    the manifest; and
     
    2) Retain
    It must retain one copy of the manifest in accordance with Section
    723.122; and
     
    3) Give
    It must give the remaining copies of the manifest to the accepting
    transporter or designated facility.
     
    e) The requirements of subsections (c), (d), and (f) do not apply to water (bulk
    shipment) transporters if all of the following are true:
     
    1) The hazardous waste is delivered by water (bulk shipment) to the
    designated facility; and
     
    2) A shipping paper containing all the information required on the manifest
    (excluding the USEPA identification numbers, generator certification and
    signatures) accompanies the hazardous waste and, for exports, a USEPA
    Acknowledgement of Consent accompanies the hazardous waste; and
     
    3) The delivering transporter obtains the date of delivery and handwritten
    signature of the owner or operator designated facility on either the
    manifest or the shipping paper; and
     
    4) The person delivering the hazardous waste to the initial water (bulk
    shipment) transporter obtains the date of delivery and signature of the
    water (bulk shipment) transporter on the manifest and forwards it to the
    designated facility; and
     
    5) A copy of the shipping paper or manifest is retained by each water (bulk
    shipment) transporter in accordance with Section 723.122.
     
    f) For shipments involving rail transportation, the following requirements apply
    instead of the requirements of subsections (c), (d) and (e), which do not apply and
    the following requirements do apply:
     
    1) When accepting hazardous waste from a non-rail transporter, the initial

     
    274
    rail transporter shall must do the following:
     
    A) Sign
    It must sign and date the manifest acknowledging acceptance
    of the hazardous waste;
     
    B) Return
    It must return a signed copy of the manifest to the non-rail
    transporter;
     
    C) Forward
    It must forward at least three copies of the manifest to the
    following entities:
     
    i) The next non-rail transporter, if any;
     
    ii) The designated facility, if the shipment is delivered to that
    facility by rail; or
     
    iii) The last rail transporter designated to handle the waste in
    the United States;
     
    D) Retain
    It must retain one copy of the manifest and rail shipping
    paper in accordance with Section 723.122.
     
    2) Rail transporters shall must ensure that a shipping paper containing all the
    information required on the manifest (excluding the USEPA identification
    numbers, generator certification and signatures) and, for exports, a
    USEPA Acknowledgement of Consent accompanies the hazardous waste
    at all times.
     
    BOARD NOTE: Intermediate rail transporters are not required to sign
    either the manifest or shipping paper.
     
    3) When delivering hazardous waste to the designated facility, a rail
    transporter shall must do the following:
     
    A) Obtain It must obtain the date of delivery and handwritten
    signature of the owner or operator of the designated facility on the
    manifest or the shipping paper (if the manifest has not been
    received by the facility); and
     
    B) Retain
    It must retain a copy of the manifest or signed shipping
    paper in accordance with Section 723.122.
     
    4) When delivering hazardous waste to a non-rail transporter a rail
    transporter shall must do the following:
     
    A) Obtain
    It must obtain the date of delivery and the handwritten

     
    275
    signature of the next non-rail transporter on the manifest; and
     
    B) Retain
    It must retain a copy of the manifest in accordance with
    Section 723.122.
     
    5) Before accepting hazardous waste from a rail transporter, a non-rail
    transporter shall must sign and date the manifest and provide a copy to the
    rail transporter.
     
    g) Transporters that transport hazardous waste out of the United States shall must do
    the following:
     
    1) Until September 5, 2006:
     
    1A) Indicate on the manifest the date the hazardous waste left the
    United States; and
     
    2B) Sign the manifest and retain one copy in accordance with Section
    723.122(c); and
     
    3C) Return a signed copy of the manifest to the generator; and
     
    4D) Give a copy of the manifest to a United States Customs official at
    the point of departure from the United States.
     
    2) Effective September 5, 2006:
     
    A) Sign and date the manifest in the International Shipments block to
    indicate the date that the hazardous waste left the United States;
     
    B) Retain one copy in accordance with Section 723.122(d);
     
    C) Return a signed copy of the manifest to the generator; and
     
    D) Give a copy of the manifest to a U.S. Customs official at the point
    of departure from the United States.
     
    BOARD NOTE: Subsection (g)(1)(A) theough (g)(1)(B) correspond with 40
    CFR 263.20(g) (2004). Subsection (g)(2)(A) theough (g)(2)(B) correspond with
    40 CFR 263.20(g) (2005). The Board added subsections (g)(1) and (g)(2),
    reciting the effective dates, based on 40 CFR 263.20(a)(3) (2005).
     
    h) A transporter transporting hazardous waste from a generator that generates greater
    than 100 kilograms but less than 1000 1,000 kilograms of hazardous waste in a
    calendar month need not comply with the requirements of this Section or those of
    Section 723.122 provided that:

     
    276
     
    1) The waste is being transported pursuant to a reclamation agreement
    provided for in 35 Ill. Adm. Code 722.120(e);
     
    2) The transporter records, on a log or shipping paper, the following
    information for each shipment:
     
    A) The name, address and USEPA Identification Number (35 Ill.
    Adm. Code 722.112) of the generator of the waste;
     
    B) The quantity of waste accepted;
     
    C) All shipping information required by the United States Department
    of Transportation;
     
    D) The date the waste is accepted; and
     
    3) The transporter carries this record when transporting waste to the
    reclamation facility; and
     
    4) The transporter retains these records for a period of at least three years
    after termination or expiration of the agreement.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 723.121 Compliance with the Manifest
     
    a) The transporter must deliver the entire quantity of hazardous waste which he has
    accepted from a generator or a transporter to:
     
    1) The designated facility listed on the manifest; or
     
    2) The alternate designated facility, if the hazardous waste cannot be
    delivered to the designated facility because an emergency prevents
    delivery; or
     
    3) The next designated transporter; or
     
    4) The place outside the United States designated by the generator.
     
    b) Non-delivery of the hazardous waste.
     
    b1) If
    Until September 5, 2006, if the hazardous waste cannot be delivered in
    accordance with paragraph subsection (a) of this section Section, the
    transporter must contact the generator for further directions and must
    revise the manifest according to the generator’s instructions.

     
    277
     
    2) Effective September 5, 2006.
     
    A) If the hazardous waste cannot be delivered in accordance with
    subsection (a) of this Section because of an emergency condition
    other than rejection of the waste by the designated facility, then the
    transporter must contact the generator for further directions and
    must revise the manifest according to the generator’s instructions.
     
    B) If hazardous waste is rejected by the designated facility while the
    transporter is on the premises of the designated facility, then the
    transporter must obtain the following, as appropriate:
     
    i) For a partial load rejection or for regulated quantities of
    container residues: a copy of the original manifest that
    includes the facility’s date and signature, the manifest
    tracking number of the new manifest that will accompany
    the shipment, and a description of the partial rejection or
    container residue in the discrepancy block of the original
    manifest. The transporter must retain a copy of this
    manifest in accordance with Section 723.122 and give the
    remaining copies of the original manifest to the rejecting
    designated facility. If the transporter is forwarding the
    rejected part of the shipment or a regulated container
    residue to an alternate facility or returning it to the
    generator, the transporter must obtain a new manifest to
    accompany the shipment, and the new manifest must
    include all of the information required in 35 Ill. Adm. Code
    724.172(b)(5)(A) through (b)(5)(F) or (b)(6)(A) through
    (b)(6)(F) or 35 Ill. Adm. Code 724.172(b)(5)(A) through
    (b)(5)(F) or (b)(6)(A) through (b)(6)(F).
     
    ii) For a full load rejection that will be taken back by the
    transporter: a copy of the original manifest that includes
    the rejecting facility’s signature and date attesting to the
    rejection, the description of the rejection in the discrepancy
    block of the manifest, and the name, address, phone
    number, and USEPA identification number for the alternate
    facility or generator to whom the shipment must be
    delivered. The transporter must retain a copy of the
    manifest in accordance with Section 723.122, and give a
    copy of the manifest containing this information to the
    rejecting designated facility. If the original manifest is not
    used, then the transporter must obtain a new manifest for
    the shipment and comply with 35 Ill. Adm. Code
    724.172(b)(5)(A) through (b)(5)(F) or (b)(6)(A) through

     
    278
    (b)(6)(F) or 35 Ill. Adm. Code 724.172(b)(5)(A) through
    (b)(5)(F) or (b)(6)(A) through (b)(6)(F).
     
    BOARD NOTE: Subsection (b)(1) is derived from 40 CFR 263.21(b) (2004),
    effective until September 5, 2006. Subsection (b)(2) is derived from 40 CFR
    263.21(b) (2005), effective September 5, 2006.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART C: HAZARDOUS WASTE DISCHARGES
     
    Section 723.130 Immediate Action
     
    a) In the event of a discharge of hazardous waste during transportation, the
    transporter must take appropriate immediate action to protect human health and
    the environment (e.g., notify local authorities, dike the discharge area).
     
    b) If a discharge of hazardous waste occurs during transportation and an official (of
    state or local government or of a federal agency) acting within the scope of his or
    her official responsibilities determines that immediate removal of the waste is
    necessary to protect human health or the environment, that official may authorize
    the removal of the waste by transporters that do not have U.S. EPA USEPA
    identification numbers and without the preparation of a manifest.
     
    c) An air, rail, highway, or water transporter that has discharged hazardous waste
    must:
     
    1) Give notice to the National Response Center (800-424-8802 or 202-426-
    2675), if required by 49 CFR 171.15 (Immediate Notice of Certain
    Hazardous Materials Incidents), incorporated by reference in 35 Ill. Adm.
    Code 720.111(b);
     
    2) Report in writing to the Director, Office of Hazardous Materials
    Regulations, Materials Transportation Bureau, Department of
    Transportation, Washington, D.C. 20590, as required by 49 CFR 171.16
    (Detailed Hazardous Materials Incident Reports), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b); and
     
    3) give
    Give notice to the following State agency:
     
    Illinois Emergency Management Agency
    110 East Adams
    Springfield, Illinois 62706
    217-782-7860
     
    d) A water (bulk shipment) transporter that has discharged hazardous waste must

     
    279
    give the same notice as required by 33 CFR 153.203 (Procedure for the NBotice
    of Discharge), incorporated by reference in 35 Ill. Adm. Code 720.111(b), for oil
    and hazardous substances.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 723.131 Discharge Clean Up Cleanup
     
    A transporter must clean up any hazardous waste discharge that occurs during transportation or
    take such action as may be required or approved by Federal federal, State, or local officials so
    that the hazardous waste discharge no longer presents a hazard to human health or the
    environment.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
     
    PART 724
    STANDARDS FOR OWNERS AND OPERATORS OF HAZARDOUS WASTE
    TREATMENT, STORAGE, AND DISPOSAL FACILITIES
     
    SUBPART A: GENERAL PROVISIONS
    Section
    724.101 Purpose, Scope, and Applicability
    724.103 Relationship to Interim Status Standards
     
    SUBPART B: GENERAL FACILITY STANDARDS
    Section
    724.110 Applicability
    724.111 USEPA Identification Number
    724.112 Required Notices
    724.113 General Waste Analysis
    724.114 Security
    724.115 General Inspection Requirements
    724.116 Personnel Training
    724.117 General Requirements for Ignitable, Reactive, or Incompatible Wastes
    724.118 Location Standards
    724.119 Construction Quality Assurance Program
     
    SUBPART C: PREPAREDNESS AND PREVENTION
    Section
    724.130 Applicability
    724.131 Design and Operation of Facility

     
    280
    724.132 Required Equipment
    724.133 Testing and Maintenance of Equipment
    724.134 Access to Communications or Alarm System
    724.135 Required Aisle Space
    724.137 Arrangements with Local Authorities
     
    SUBPART D: CONTINGENCY PLAN AND EMERGENCY PROCEDURES
    Section
    724.150 Applicability
    724.151 Purpose and Implementation of Contingency Plan
    724.152 Content of Contingency Plan
    724.153 Copies of Contingency Plan
    724.154 Amendment of Contingency Plan
    724.155 Emergency Coordinator
    724.156 Emergency Procedures
     
    SUBPART E: MANIFEST SYSTEM, RECORDKEEPING AND REPORTING
    Section
    724.170 Applicability
    724.171 Use of Manifest System
    724.172 Manifest Discrepancies
    724.173 Operating Record
    724.174 Availability, Retention, and Disposition of Records
    724.175 Annual Report
    724.176 Unmanifested Waste Report
    724.177 Additional Reports
     
    SUBPART F: RELEASES FROM SOLID WASTE MANAGEMENT UNITS
    Section
    724.190 Applicability
    724.191 Required Programs
    724.192 Groundwater Protection Standard
    724.193 Hazardous Constituents
    724.194 Concentration Limits
    724.195 Point of Compliance
    724.196 Compliance Period
    724.197 General Groundwater Monitoring Requirements
    724.198 Detection Monitoring Program
    724.199 Compliance Monitoring Program
    724.200 Corrective Action Program
    724.201 Corrective Action for Solid Waste Management Units
     
    SUBPART G: CLOSURE AND POST-CLOSURE CARE
    Section
    724.210 Applicability
    724.211 Closure Performance Standard

     
    281
    724.212 Closure Plan; Amendment of Plan
    724.213 Closure; Time Allowed For Closure
    724.214 Disposal or Decontamination of Equipment, Structures, and Soils
    724.215 Certification of Closure
    724.216 Survey Plat
    724.217 Post-Closure Care and Use of Property
    724.218 Post-Closure Care Plan; Amendment of Plan
    724.219 Post-Closure Notices
    724.220 Certification of Completion of Post-Closure Care
     
    SUBPART H: FINANCIAL REQUIREMENTS
    Section
    724.240 Applicability
    724.241 Definitions of Terms as Used in This Subpart
    724.242 Cost Estimate for Closure
    724.243 Financial Assurance for Closure
    724.244 Cost Estimate for Post-Closure Care
    724.245 Financial Assurance for Post-Closure Care
    724.246 Use of a Mechanism for Financial Assurance of Both Closure and Post-Closure
    Care
    724.247 Liability Requirements
    724.248 Incapacity of Owners or Operators, Guarantors, or Financial Institutions
    724.251 Wording of the Instruments
     
    SUBPART I: USE AND MANAGEMENT OF CONTAINERS
    Section
    724.270 Applicability
    724.271 Condition of Containers
    724.272 Compatibility of Waste with Container
    724.273 Management of Containers
    724.274 Inspections
    724.275 Containment
    724.276 Special Requirements for Ignitable or Reactive Waste
    724.277 Special Requirements for Incompatible Wastes
    724.278 Closure
    724.279 Air Emission Standards
     
    SUBPART J: TANK SYSTEMS
    Section
    724.290 Applicability
    724.291 Assessment of Existing Tank System Integrity
    724.292 Design and Installation of New Tank Systems or Components
    724.293 Containment and Detection of Releases
    724.294 General Operating Requirements
    724.295 Inspections
    724.296 Response to Leaks or Spills and Disposition of Leaking or Unfit-for-Use Tank

     
    282
    Systems
    724.297 Closure and Post-Closure Care
    724.298 Special Requirements for Ignitable or Reactive Waste
    724.299 Special Requirements for Incompatible Wastes
    724.300 Air Emission Standards
     
    SUBPART K: SURFACE IMPOUNDMENTS
    Section
    724.320 Applicability
    724.321 Design and Operating Requirements
    724.322 Action Leakage Rate
    724.323 Response Actions
    724.326 Monitoring and Inspection
    724.327 Emergency Repairs; Contingency Plans
    724.328 Closure and Post-Closure Care
    724.329 Special Requirements for Ignitable or Reactive Waste
    724.330 Special Requirements for Incompatible Wastes
    724.331 Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026, and
    F027
    724.332 Air Emission Standards
     
    SUBPART L: WASTE PILES
    Section
    724.350 Applicability
    724.351 Design and Operating Requirements
    724.352 Action Leakage Rate
    724.353 Response Action Plan
    724.354 Monitoring and Inspection
    724.356 Special Requirements for Ignitable or Reactive Waste
    724.357 Special Requirements for Incompatible Wastes
    724.358 Closure and Post-Closure Care
    724.359 Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026, and
    F027
     
    SUBPART M: LAND TREATMENT
    Section
    724.370 Applicability
    724.371 Treatment Program
    724.372 Treatment Demonstration
    724.373 Design and Operating Requirements
    724.376 Food-Chain Crops
    724.378 Unsaturated Zone Monitoring
    724.379 Recordkeeping
    724.380 Closure and Post-Closure Care
    724.381 Special Requirements for Ignitable or Reactive Waste
    724.382 Special Requirements for Incompatible Wastes

     
    283
    724.383 Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026, and
    F027
     
    SUBPART N: LANDFILLS
    Section
    724.400 Applicability
    724.401 Design and Operating Requirements
    724.402 Action Leakage Rate
    724.403 Monitoring and Inspection
    724.404 Response Actions
    724.409 Surveying and Recordkeeping
    724.410 Closure and Post-Closure Care
    724.412 Special Requirements for Ignitable or Reactive Waste
    724.413 Special Requirements for Incompatible Wastes
    724.414 Special Requirements for Bulk and Containerized Liquids
    724.415 Special Requirements for Containers
    724.416 Disposal of Small Containers of Hazardous Waste in Overpacked Drums (Lab
    Packs)
    724.417 Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026, and
    F027
     
    SUBPART O: INCINERATORS
    Section
    724.440 Applicability
    724.441 Waste Analysis
    724.442 Principal Organic Hazardous Constituents (POHCs)
    724.443 Performance Standards
    724.444 Hazardous Waste Incinerator Permits
    724.445 Operating Requirements
    724.447 Monitoring and Inspections
    724.451 Closure
     
    SUBPART S: SPECIAL PROVISIONS FOR CLEANUP
    Section
    724.650 Applicability of Corrective Action Management Unit Regulations
    724.651 Grandfathered Corrective Action Management Units
    724.652 Corrective Action Management Units
    724.653 Temporary Units
    724.654 Staging Piles
    724.655 Disposal of CAMU-Eligible Wastes in Permitted Hazardous Waste Landfills
     
    SUBPART W: DRIP PADS
    Section
    724.670 Applicability
    724.671 Assessment of Existing Drip Pad Integrity
    724.672 Design and Installation of New Drip Pads

     
    284
    724.673 Design and Operating Requirements
    724.674 Inspections
    724.675 Closure
     
    SUBPART X: MISCELLANEOUS UNITS
    Section
    724.700 Applicability
    724.701 Environmental Performance Standards
    724.702 Monitoring, Analysis, Inspection, Response, Reporting, and Corrective Action
    724.703 Post-Closure Care
     
    SUBPART AA: AIR EMISSION STANDARDS FOR PROCESS VENTS
    Section
    724.930 Applicability
    724.931 Definitions
    724.932 Standards: Process Vents
    724.933 Standards: Closed-Vent Systems and Control Devices
    724.934 Test Methods and Procedures
    724.935 Recordkeeping Requirements
    724.936 Reporting Requirements
     
    SUBPART BB: AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS
    Section
    724.950 Applicability
    724.951 Definitions
    724.952 Standards: Pumps in Light Liquid Service
    724.953 Standards: Compressors
    724.954 Standards: Pressure Relief Devices in Gas/Vapor Service
    724.955 Standards: Sampling Connecting Systems
    724.956 Standards: Open-ended Valves or Lines
    724.957 Standards: Valves in Gas/Vapor or Light Liquid Service
    724.958 Standards: Pumps, Valves, Pressure Relief Devices, and Other Connectors
    724.959 Standards: Delay of Repair
    724.960 Standards: Closed-Vent Systems and Control Devices
    724.961 Alternative Percentage Standard for Valves
    724.962 Skip Period Alternative for Valves
    724.963 Test Methods and Procedures
    724.964 Recordkeeping Requirements
    724.965 Reporting Requirements
     
    SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE
    IMPOUNDMENTS, AND CONTAINERS
    Section
    724.980 Applicability
    724.981 Definitions
    724.982 Standards: General

     
    285
    724.983 Waste Determination Procedures
    724.984 Standards: Tanks
    724.985 Standards: Surface Impoundments
    724.986 Standards: Containers
    724.987 Standards: Closed-Vent Systems and Control Devices
    724.988 Inspection and Monitoring Requirements
    724.989 Recordkeeping Requirements
    724.990 Reporting Requirements
    724.991 Alternative Control Requirements for Tanks (Repealed)
     
    SUBPART DD: CONTAINMENT BUILDINGS
    Section
    724.1100 Applicability
    724.1101 Design and Operating Standards
    724.1102 Closure and Post-Closure Care
     
    SUBPART EE: HAZARDOUS WASTE MUNITIONS AND EXPLOSIVES
    STORAGE
    Section
    724.1200 Applicability
    724.1201 Design and Operating Standards
    724.1202 Closure and Post-Closure Care
     
    724.Appendix A Recordkeeping Instructions
    724.Appendix B EPA Report Form and Instructions (Repealed)
    724.Appendix D Cochran’s Approximation to the Behrens-Fisher Student’s T-Test
    724.Appendix E Examples of Potentially Incompatible Waste
    724.Appendix I Groundwater Monitoring List
     
    AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the
    Environmental Protection Act [415 ILCS 5/7.2, 22.4, and 27].
     
    SOURCE: Adopted in R82-19 at 7 Ill. Reg. 14059, effective October 12, 1983; amended in
    R84-9 at 9 Ill. Reg. 11964, effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 1136,
    effective January 2, 1986; amended in R86-1 at 10 Ill. Reg. 14119, effective August 12, 1986;
    amended in R86-28 at 11 Ill. Reg. 6138, effective March 24, 1987; amended in R86-28 at 11 Ill.
    Reg. 8684, effective April 21, 1987; amended in R86-46 at 11 Ill. Reg. 13577, effective August
    4, 1987; amended in R87-5 at 11 Ill. Reg. 19397, effective November 12, 1987; amended in
    R87-39 at 12 Ill. Reg. 13135, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 458,
    effective December 28, 1988; amended in R89-1 at 13 Ill. Reg. 18527, effective November 13,
    1989; amended in R90-2 at 14 Ill. Reg. 14511, effective August 22, 1990; amended in R90-10 at
    14 Ill. Reg. 16658, effective September 25, 1990; amended in R90-11 at 15 Ill. Reg. 9654,
    effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14572, effective October 1, 1991;
    amended in R91-13 at 16 Ill. Reg. 9833, effective June 9, 1992; amended in R92-1 at 16 Ill. Reg.
    17702, effective November 6, 1992; amended in R92-10 at 17 Ill. Reg. 5806, effective March 26,
    1993; amended in R93-4 at 17 Ill. Reg. 20830, effective November 22, 1993; amended in R93-

     
    286
    16 at 18 Ill. Reg. 6973, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12487,
    effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17601, effective November 23, 1994;
    amended in R95-6 at 19 Ill. Reg. 9951, effective June 27, 1995; amended in R95-20 at 20 Ill.
    Reg. 11244, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 636,
    effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7638, effective April 15, 1998;
    amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17972, effective September 28, 1998; amended
    in R98-21/R99-2/R99-7 at 23 Ill. Reg. 2186, effective January 19, 1999; amended in R99-15 at
    23 Ill. Reg. 9437, effective July 26, 1999; amended in R00-5 at 24 Ill. Reg. 1146, effective
    January 6, 2000; amended in R00-13 at 24 Ill. Reg. 9833, effective June 20, 2000; expedited
    correction at 25 Ill. Reg. 5115, effective June 20, 2000; amended in R02-1/R02-12/R02-17 at 26
    Ill. Reg. 6635, effective April 22, 2002; amended in R03-7 at 27 Ill. Reg. 3725, effective
    February 14, 2003; amended in R05-8 at 29 Ill. Reg. 6009, effective April 13, 2005; amended in
    R05-2 at 29 Ill. Reg. 6365, effective April 22, 2005; amended in R06-5/R06-6/R06-7 at 30 Ill.
    Reg. ________, effective ______________________.
     
    SUBPART B: GENERAL FACILITY STANDARDS
     
    Section 724.118 Location Standards
     
    a) Seismic considerations.
     
    1) Portions of new facilities where treatment, storage or disposal of
    hazardous waste will be conducted must not be located within 61 meters
    (200 feet) of a fault that has had displacement in Holocene time.
     
    2) As used in subsection (a)(1) of this Section:
     
    A) “Fault” means a fracture along with rocks on one side have been
    displaced with respect to those on the other side.
     
    B) “Displacement” means the relative movement of any two sides of a
    fault measured in any direction.
     
    C) “Holocene” means the most recent epoch of the Quarternary
    period, extending from the end of the Pleistocene to the present.
     
    BOARD NOTE: Procedures for demonstrating compliance with this standard in
    Part B of the permit application are specified in 35 Ill. Adm. Code 703.182.
    Facilities that are located in political jurisdictions other than those listed in
    appendix VI to 40 CFR 264.Appendix VI (Political Jurisdictions in Which
    Compliance with§ 264.18(a) Must Be Demonstrated), incorporated by reference
    in 35 Ill. Adm. Code 720.111 720.111(b), are assumed to be in compliance with
    this requirement.
     
    b) Floodplains.
     

     
    287
    1) A facility located in a 100 year floodplain must be designed, constructed,
    operated and maintained to prevent washout of any hazardous waste by a
    100-year flood, unless the owner or operator can demonstrate the
    following to the Agency’s satisfaction:
     
    A) That procedures are in effect that will cause the waste to be
    removed safely, before flood waters can reach the facility, to a
    location where the wastes will not be vulnerable to flood waters; or
     
    B) For existing surface impoundments, waste piles, land treatment
    units, landfills and miscellaneous units, that no adverse effect on
    human health or the environment will result if washout occurs,
    considering the following:
     
    i) The volume and physical and chemical characteristics of
    the waste in the facility;
     
    ii) The concentration of hazardous constituents that would
    potentially affect surface waters as a result of washout;
     
    iii) The impact of such concentrations on the current or
    potential uses of and water quality standards established for
    the affected surface waters; and
     
    iv) The impact of hazardous constituents on the sediments of
    affected surface waters or the soils of the 100-year
    floodplain that could result from washout;
     
    2) As used in subsection (b)(1) of this Section:
     
    A) “100-year floodplain” means any land area that is subject to a one
    percent or greater chance of flooding in any given year from any
    source.
     
    B) “Washout” means the movement of hazardous waste from the
    active portion of the facility as a result of flooding.
     
    C) “100-year flood” means a flood that has a one percent chance of
    being equalled or exceeded in any given year.
     
    BOARD NOTE: Requirements pertaining to other Federal federal laws that
    affect the location and permitting of facilities are found in 40 CFR 270.3. For
    details relative to these laws, see EPA’s manual for SEA (special environmental
    area) requirements for hazardous waste facility permits. Though EPA is
    responsible for complying with these requirements, applicants are advised to
    consider them in planning the location of a facility to help prevent subsequent

     
    288
    project delays. Facilities may be required to obtain from the Illinois Department
    of Transportation on a permit or certification that a facility is flood-proofed.
     
    c) Salt dome formations, salt bed formations, underground mines and caves. The
    placement of any non-containerized or bulk liquid hazardous waste in any salt
    dome formation, salt bed formation, underground cave or mine is prohibited.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART D: CONTINGENCY PLAN AND EMERGENCY PROCEDURES
     
    Section 724.150 Applicability
     
    The regulations in this Subpart D apply to owners and operators of a11 all hazardous waste
    management facilities, except as Section 724.101 provides otherwise.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.152 Content of Contingency Plan
     
    a) The contingency plan must describe the actions facility personnel must take to
    comply with Sections 724.151 and 724.156 in response to fires, explosions, or
    any unplanned sudden or non-sudden release of hazardous waste or hazardous
    waste constituents to air, soil, or surface water at the facility.
     
    b) If the owner or operator has already prepared a Spill Prevention Control and
    Countermeasures (SPCC) Plan in accordance with federal 40 CFR Part 112 or
    300, or some other emergency or contingency plan, the owner or operator need
    only amend that plan to incorporate hazardous waste management provisions that
    are sufficient to comply with the requirements of this Part.
     
    c) The plan must describe arrangements agreed to by local police departments, fire
    departments, hospitals, contractors, and state and local emergency response teams
    to coordinate emergency services pursuant to Section 724.137.
     
    d) The plan must list names, addresses, and phone numbers (office and home) of all
    persons qualified to act as emergency coordinator (see Section 724.155), and this
    list must be kept up to date. Where more than one person is listed, one must be
    named as primary emergency coordinator and others must be listed in the order in
    which they will assume responsibility as alternates. For new facilities, this
    information must be supplied to the Agency at the time of certification, rather
    than at the time of permit application.
     
    e) The plan must include a list of all emergency equipment at the facility (such as
    fire extinguishing systems, spill control equipment, communications and alarm
    systems (internal and external), and decontamination equipment), where this

     
    289
    equipment is required. This list must be kept up to date. In addition, the plan
    must include the location and a physical description of each item on the list and a
    brief outline of its capabilities.
     
    f) The plan must include an evacuation plan for facility personnel where there is a
    possibility that evacuation could be necessary. This plan must describe signals to
    be used to begin evacuation, evacuation routes and alternative evacuation routes
    (in cases where the primary routes could be blocked by releases of hazardous
    waste or fires).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.153 Copies of Contingency Plan
     
    A copy of the contingency plan and all revisions to the plan must be:
     
    a) Maintained at the facility; and
     
    b) Submitted to all local police departments, fire departments, hospitals, and state
    and local emergency response teams that may be called upon to provide
    emergency services.
     
    BOARD NOTE: The contingency plan must be submitted to the Agency with Part B of the
    permit application under 35 Ill. Adm. Code 702 and 703, and, after modification or approval, the
    plan will become a condition of any permit issued.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.156 Emergency Procedures
     
    a) Whenever there is an imminent or actual emergency situation, the emergency
    coordinator (or the designee when the emergency coordinator is on call) must
    immediately do the following:
     
    1) Activate
    He or she must activate internal facility alarms or communication
    systems, where applicable, to notify all facility personnel; and
     
    2) Notify He or she must notify appropriate state or local agencies with
    designated response roles if their help is needed.
     
    b) Whenever there is a release, fire, or explosion, the emergency coordinator must
    immediately identify the character, exact source, amount, and areal extent of any
    released materials. The emergency coordinator may do this by observation or
    review of facility records or manifests and, if necessary, by chemical analysis.
     
    c) Concurrently, the emergency coordinator must assess possible hazards to human

     
    290
    health or the environment that may result from the release, fire, or explosion.
    This assessment must consider both direct and indirect effects of the release, fire,
    or explosion (e.g., the effects of any toxic, irritating, or asphyxiating gases that
    are generated, or the effects of any hazardous surface water run-off from water or
    chemical agents used to control fire and heat-induced explosions).
     
    d) If the emergency coordinator determines that the facility has had a release, fire, or
    explosion that could threaten human health or the environment outside the
    facility, the emergency coordinator must report the findings as follows:
     
    1) If the assessment indicates that evacuation of local areas may be
    advisable, the emergency coordinator must immediately notify appropriate
    local authorities. The emergency coordinator must be available to help
    appropriate officials decide whether local areas should be evacuated; and
     
    2) The emergency coordinator must immediately notify either the
    government official designated as the on-scene coordinator for that
    geographical area (in the applicable regional contingency plan under
    federal 40 CFR 300) or the National Response Center (using their 24-hour
    toll free number 800-424-8802). The report must include the following:
     
    A) Name and telephone number of reporter;
     
    B) Name and address of facility;
     
    C) Time and type of incident (e.g., release, fire);
     
    D) Name and quantity of materials involved, to the extent known;
     
    E) The extent of injuries, if any; and
     
    F) The possible hazards to human health or the environment outside
    the facility.
     
    e) During an emergency, the emergency coordinator must take all reasonable
    measures necessary to ensure that fires, explosions, and releases do not occur,
    recur, or spread to other hazardous waste at the facility. These measures must
    include, where applicable, stopping processes and operations, collecting and
    containing release waste, and removing or isolating containers.
     
    f) If the facility stops operations in response to a fire, explosion, or release, the
    emergency coordinator must monitor for leaks, pressure buildup, gas generation,
    or ruptures in valves, pipes, or other equipment, wherever this is appropriate.
     
    g) Immediately after an emergency, the emergency coordinator must provide for
    treating, storing, or disposing of recovered waste, contaminated soil or surface

     
    291
    water, or any other material that results from a release, fire, or explosion at the
    facility.
     
    BOARD NOTE: Unless the owner or operator can demonstrate, in accordance
    with 35 Ill. Adm. Code 721.103(d) or (e), that the recovered material is not a
    hazardous waste, the owner or operator becomes a generator of hazardous waste
    and must manage it in accordance with all applicable requirements of 35 Ill. Adm.
    Code 722, 723, and 724.
     
    h) The emergency coordinator must ensure that the following is true in the affected
    areas of the facility:
     
    1) No waste that may be incompatible with the released material is treated,
    stored, or disposed of until cleanup procedures are completed; and
     
    2) All emergency equipment listed in the contingency plan is cleaned and fit
    for its intended use before operations are resumed.
     
    i) The owner or operator must notify the Agency and appropriate state and local
    authorities that the facility is in compliance with subsection (h) of this Section
    before operations are resumed in the affected areas of the facility.
     
    j) The owner or operator must note in the operating record the time, date, and details
    of any incident that requires implementing the contingency plan. Within 15 days
    after the incident, the owner or operator must submit a written report on the
    incident to the Agency. The report must include the following:
     
    1) Name,
    The name, address, and telephone number of the owner or operator;
     
    2) Name,
    The name, address, and telephone number of the facility;
     
    3) Date,
    The date, time, and type of incident (e.g., fire, explosion);
     
    4) Name
    The name and quantity of materials involved;
     
    5) The extent of injuries, if any;
     
    6) An assessment of actual or potential hazards to human health or the
    environment, where this is applicable; and
     
    7) Estimated
    The estimated quantity and disposition of recovered material
    that resulted from the incident.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    292
    SUBPART E: MANIFEST SYSTEM, RECORDKEEPING AND
    REPORTING
     
    Section 724.170 Applicability
     
    The regulations in this Subpart E apply to owners and operators of both on-site and off-site
    facilities, except as Section 724.101 provides otherwise. Sections 724.171, 724.172, and
    724.176 do not apply to owners and operators of on-site facilities that do not receive any
    hazardous waste from off-site sources, nor do they apply to owners and operators of off-site
    facilities with respect to waste military munitions exempted from manifest requirements under
    35 Ill. Adm. Code 726.303(a). Section 724.173(b) only applies to permittees that treat, store, or
    dispose of hazardous wastes on-site where such wastes were generated.
     
    BOARD NOTE: This Section corresponds with 40 CFR 264.70(a) (2005), effective September
    5, 2006. The Board omitted 40 CFR 264.70(b) (2005), since that provision merely stated the
    September 5, 2006 effective date for the newer manifest requirements.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.171 Use of Manifest System
     
    a) Receipt of manifested hazardous waste.
     
    a1) The following requirements apply until September 5, 2006: If a facility
    receives hazardous waste accompanied by a manifest, the owner or
    operator, or the owner or operator’s agent, must do the following:
     
    1A) Sign
    It must sign and date each copy of the manifest to certify that
    the hazardous waste covered by the manifest was received;
     
    2B) Note
    It must note any significant discrepancies in the manifest (as
    defined in Section 724.172(a)) on each copy of the manifest;
     
    BOARD NOTE: The Board does not intend that the owner or
    operator of a facility whose procedures under Section 724.113(c)
    include waste analysis must perform that analysis before signing
    the manifest and giving it to the transporter. Section 724.172(b),
    however, requires reporting an unreconciled discrepancy
    discovered during later analysis.
     
    3C) Immediately
    It must immediately give the transporter at least one
    copy of the signed manifest;
     
    4D) Within 30 days after the delivery, It must send a copy of the
    manifest to the generator and to the Agency within 30 days after
    delivery; and

     
    293
     
    5E) Retain
    It must retain at the facility a copy of each manifest for at
    least three years from after the date of delivery.
     
    2) The following requirements apply effective September 5, 2006:
     
    A) If a facility receives hazardous waste accompanied by a manifest,
    the owner, operator, or its agent must sign and date the manifest, as
    indicated in subsection (a)(2)(B) of this Section to certify that the
    hazardous waste covered by the manifest was received, that the
    hazardous waste was received except as noted in the discrepancy
    space of the manifest, or that the hazardous waste was rejected as
    noted in the manifest discrepancy space.
     
    B) If a facility receives a hazardous waste shipment accompanied by a
    manifest, the owner, operator, or its agent must do the following:
     
    i) It must sign and date, by hand, each copy of the manifest;
     
    ii) It must note any discrepancies (as defined in Section
    724.172(b)) on each copy of the manifest;
     
    iii) It must immediately give the transporter at least one copy
    of the manifest;
     
    iv) It must send a copy of the manifest to the generator within
    30 days after delivery; and
     
    v) It must retain at the facility a copy of each manifest for at
    least three years after the date of delivery.
     
    C) If a facility receives hazardous waste imported from a foreign
    source, the receiving facility must mail a copy of the manifest to
    the following address within 30 days after delivery: International
    Compliance Assurance Division, OFA/OECA (2254A), U.S.
    Environmental Protection Agency, Ariel Rios Building, 1200
    Pennsylvania Avenue, NW., Washington, DC 20460.
     
    BOARD NOTE: Subsection (a)(1) of this Section corresponds with 40 CFR
    264.71(a) (2004), effective until September 5, 2006. Subsection (a)(2) of this
    Section corresponds with 40 CFR 264.71(a) (2005), effective September 5, 2006.
     
    b) If a facility receives, from a rail or water (bulk shipment) transporter, hazardous
    waste that is accompanied by a shipping paper containing all the information
    required on the manifest (excluding the USEPA identification numbers,
    generator’s certification, and signatures), the owner or operator, or the owner or

     
    294
    operator’s agent, must do the following:
     
    1) Sign
    It must sign and date each copy of the manifest or shipping paper (if
    the manifest has not been received) to certify that the hazardous waste
    covered by the manifest or shipping paper was received;
     
    2) Note
    It must note any significant discrepancies (as defined in Section
    724.172(a)) in the manifest or shipping paper (if the manifest has not been
    received) on each copy of the manifest or shipping paper;
     
    BOARD NOTE: The Board does not intend that the owner or operator of
    a facility whose procedures under Section 724.113(c) include waste
    analysis must perform that analysis before signing the shipping paper and
    giving it to the transporter. Section 724.172(b), however, requires
    reporting an unreconciled discrepancy discovered during later analysis.
     
    3) Immediately
    It must immediately give the rail or water (bulk shipment)
    transporter at least one copy of the manifest or shipping paper (if the
    manifest has not been received);
     
    4) Forwarding copies of the manifest.
     
    4A) Within
    30 days after the delivery, Until September 5, 2006: The
    owner or operator must send a copy of the signed and dated
    manifest to the generator and to the Agency within 30 days after
    the delivery; however, if the manifest has not been received within
    30 days after delivery, the owner or operator, or the owner or
    operator’s agent, must send a copy of the shipping paper signed
    and dated to the generator; and or
     
    B) Effective September 5, 2006: The owner or operator must send a
    copy of the signed and dated manifest or a signed and dated copy
    of the shipping paper (if the manifest has not been received within
    30 days after delivery) to the generator within 30 days after the
    delivery; and
     
    BOARD NOTE: Section 722.123(c) requires the generator to send three
    copies of the manifest to the facility when hazardous waste is sent by rail
    or water (bulk shipment). Subsection (b)(4)(A) is derived from 40 CFR
    264.74(b)(4) (2004), effective until September 5, 2006. Subsection
    (b)(4)(B) is derived from 40 CFR 264.74(b)(4) (2005), effective
    September 5, 2006.
     
    5) Retain at the facility a copy of the manifest and shipping paper (if signed
    in lieu of the manifest at the time of delivery) for at least three years from
    the date of delivery.

     
    295
     
    c) Whenever a shipment of hazardous waste is initiated from a facility, the owner or
    operator of that facility must comply with the requirements of 35 Ill. Adm. Code
    722.
     
    BOARD NOTE: The provisions of 35 Ill. Adm. Code 722.134 are
    applicable to the on-site accumulation of hazardous wastes by generators.
    Therefore, the provisions of Section 722.134 only apply to owners or
    operators that are shipping hazardous waste that they generated at that
    facility.
     
    d) Within three working days of the receipt of a shipment subject to Subpart H of 35
    Ill. Adm. Code 722, the owner or operator of the facility must provide a copy of
    the tracking document bearing all required signatures to the notifier; to the Office
    of Enforcement and Compliance Assurance, Office of Compliance, Enforcement
    Planning, Targeting and Data Division (2222A), Environmental Protection
    Agency, 401 M St., SW, Washington, DC 20460; to the Bureau of Land, Division
    of Land Pollution Control, Illinois Environmental Protection Agency, P.O. Box
    19276, Springfield, IL 62794-9276; and to competent authorities of all other
    concerned countries. The original copy of the tracking document must be
    maintained at the facility for at least three years from the date of signature.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.172 Manifest Discrepancies
     
    a) The following requirements apply until September 5, 2005:
     
    a1) Definition of a “manifest discrepancy.”
     
    1A) A manifest discrepancy is a difference between the quantity or
    type of hazardous waste designated on the manifest or shipping
    paper, and the quantity or type of hazardous waste a facility
    actually receives;
     
    2B) A significant discrepancy in quantity is as follows:
     
    Ai) For bulk waste, variations greater than 10 percent in
    weight; and
     
    Bii) For batch waste, any variation in piece count, such as a
    discrepancy of one drum in a truckload;
     
    3C) Significant discrepancies in type are obvious differences that can
    be discovered by inspection or waste analysis, such as waste
    solvent substituted for waste acid, or toxic constituents not

     
    296
    reported on the manifest or shipping paper.
     
    b2) Upon discovering a significant discrepancy, the owner or operator must
    attempt to reconcile the discrepancy with the waste generator or
    transporter (e.g., with telephone conversations). If the discrepancy is not
    resolved within 15 days after receiving the waste, the owner or operator
    must immediately submit to the Agency a letter describing the
    discrepancy and attempts to reconcile it, and a copy of the manifest or
    shipping paper at issue.
     
    b) The following requirements apply effective September 5, 2005:
     
    1) “Manifest discrepancies” are defined as any one of the following:
     
    A) Significant differences (as defined by subsection (b)(2) of this
    Section) between the quantity or type of hazardous waste
    designated on the manifest or shipping paper, and the quantity and
    type of hazardous waste a facility actually receives;
     
    B) Rejected wastes, which may be a full or partial shipment of
    hazardous waste that the treatment, storage, or disposal facility
    cannot accept; or
     
    C) Container residues, which are residues that exceed the quantity
    limits for empty containers set forth in 35 Ill. Adm. Code
    721.107(b).
     
    2) “Significant differences in quantity” are defined as the appropriate of the
    following: for bulk waste, variations greater than 10 percent in weight; or,
    for batch waste, any variation in piece count, such as a discrepancy of one
    drum in a truckload. “Significant differences in type” are defined as
    obvious differences that can be discovered by inspection or waste
    analysis, such as waste solvent substituted for waste acid, or as toxic
    constituents not reported on the manifest or shipping paper.
     
    3) Upon discovering a significant difference in quantity or type, the owner or
    operator must attempt to reconcile the discrepancy with the waste
    generator or transporter (
    e.g.,
    with telephone conversations). If the
    discrepancy is not resolved within 15 days after receiving the waste, the
    owner or operator must immediately submit to the Agency a letter
    describing the discrepancy and attempts to reconcile it, and a copy of the
    manifest or shipping paper at issue.
     
    4) Rejection of hazardous waste.
     
    A) Upon rejecting waste or identifying a container residue that

     
    297
    exceeds the quantity limits for empty containers set forth in 35 Ill.
    Adm. Code 721.107(b), the facility must consult with the generator
    prior to forwarding the waste to another facility that can manage
    the waste. If it is impossible to locate an alternative facility that
    can receive the waste, the facility may return the rejected waste or
    residue to the generator. The facility must send the waste to the
    alternative facility or to the generator within 60 days of the
    rejection or the container residue identification.
     
    B) While the facility is making arrangements for forwarding rejected
    wastes or residues to another facility under this Section, it must
    ensure that either the delivering transporter retains custody of the
    waste, or the facility must provide for secure, temporary custody of
    the waste, pending delivery of the waste to the first transporter
    designated on the manifest prepared under subsection (b)(5) or
    (b)(6) of this Section.
     
    5) Except as provided in subsection (b)(5)(G) of this Section, for full or
    partial load rejections and residues that are to be sent off-site to an
    alternate facility, the facility is required to prepare a new manifest in
    accordance with 35 Ill. Adm. Code 722.120(a) and the following
    instructions:
     
    A) Write the generator’s USEPA identification number in Item 1 of
    the new manifest. Write the generator’s name and mailing address
    in Item 5 of the new manifest. If the mailing address is different
    from the generator’s site address, then write the generator’s site
    address in the designated space in Item 5.
     
    B) Write the name of the alternate designated facility and the
    facility’s USEPA identification number in the designated facility
    block (Item 8) of the new manifest.
     
    C) Copy the manifest tracking number found in Item 4 of the old
    manifest to the Special Handling and Additional Information
    Block of the new manifest, and indicate that the shipment is a
    residue or rejected waste from the previous shipment.
     
    D) Copy the manifest tracking number found in Item 4 of the new
    manifest to the manifest reference number line in the Discrepancy
    Block of the old manifest (Item 18a).
     
    E) Write the USDOT description for the rejected load or the residue
    in Item 9 (U.S. DOT Description) of the new manifest and write
    the container types, quantity, and volumes of waste.
     

     
    298
    F) Sign the Generator’s/Offeror’s Certification to certify, as the
    offeror of the shipment, that the waste has been properly packaged,
    marked and labeled and is in proper condition for transportation.
     
    G) For full load rejections that are made while the transporter remains
    present at the facility, the facility may forward the rejected
    shipment to the alternate facility by completing Item 18b of the
    original manifest and supplying the information on the next
    destination facility in the Alternate Facility space. The facility
    must retain a copy of this manifest for its records, and then give
    the remaining copies of the manifest to the transporter to
    accompany the shipment. If the original manifest is not used, then
    the facility must use a new manifest and comply with subsections
    (b)(5)(A) through (b)(5)(F) of this Section.
     
    6) Except as provided in subsection (b)(6)(G) of this Section, for rejected
    wastes and residues that must be sent back to the generator, the facility is
    required to prepare a new manifest in accordance with 35 Ill. Adm. Code
    722.120(a) and the following instructions:
     
    A) Write the facility’s USEPA identification number in Item 1 of the
    new manifest. Write the generator’s name and mailing address in
    Item 5 of the new manifest. If the mailing address is different from
    the generator’s site address, then write the generator’s site address
    in the designated space for Item 5.
     
    B) Write the name of the initial generator and the generator’s USEPA
    identification number in the designated facility block (Item 8) of
    the new manifest.
     
    C) Copy the manifest tracking number found in Item 4 of the old
    manifest to the Special Handling and Additional Information
    Block of the new manifest, and indicate that the shipment is a
    residue or rejected waste from the previous shipment.
     
    D) Copy the manifest tracking number found in Item 4 of the new
    manifest to the manifest reference number line in the Discrepancy
    Block of the old manifest (Item 18a).
     
    E) Write the USDOT description for the rejected load or the residue
    in Item 9 (U.S. DOT Description) of the new manifest and write
    the container types, quantity, and volumes of waste.
     
    F) Sign the Generator’s/Offeror’s Certification to certify, as offeror of
    the shipment, that the waste has been properly packaged, marked
    and labeled and is in proper condition for transportation.

     
    299
     
    G) For full load rejections that are made while the transporter remains
    at the facility, the facility may return the shipment to the generator
    with the original manifest by completing Item 18b of the manifest
    and supplying the generator’s information in the Alternate Facility
    space. The facility must retain a copy for its records and then give
    the remaining copies of the manifest to the transporter to
    accompany the shipment. If the original manifest is not used, then
    the facility must use a new manifest and comply with subsections
    (b)(6)(A) through (b)(6)(F) of this Section.
     
    7) If a facility rejects a waste or identifies a container residue that exceeds
    the quantity limits for empty containers set forth in 35 Ill. Adm. Code
    721.107(b) after it has signed, dated, and returned a copy of the manifest
    to the delivering transporter or to the generator, the facility must amend its
    copy of the manifest to indicate the rejected wastes or residues in the
    discrepancy space of the amended manifest. The facility must also copy
    the manifest tracking number from Item 4 of the new manifest to the
    Discrepancy space of the amended manifest, and must re-sign and date the
    manifest to certify to the information as amended. The facility must retain
    the amended manifest for at least three years from the date of amendment,
    and must within 30 days, send a copy of the amended manifest to the
    transporter and generator that received copies prior to their being
    amended.
     
    BOARD NOTE: Subsection (a) is derived from 40 CFR 264.72 (2004), effective until
    September 5, 2006. Subsection (b) is derived from 40 CFR 264.72 (2005), effective September
    5, 2006.
     
    Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.176 Unmanifested Waste Report
     
    a) The following requirements apply until September 5, 2005: If a facility accepts
    for treatment, storage, or disposal any hazardous waste from an off-site source
    without an accompanying manifest, or without an accompanying shipping paper
    as described in 35 Ill. Adm. Code 723.120(e)(2), and if the waste is not excluded
    from the manifest requirement by 35 Ill. Adm. Code 721.105, then the owner or
    operator must prepare and submit a single copy of a report to the Agency within
    15 days after receiving the waste. The unmanifested waste report must be
    submitted on EPA form 8700-13B. Such report must be designated
    “Unmanifested Waste Report” and include the following information:
     
    a1) The USEPA identification number, name, and address of the facility;
     
    b2) The date the facility received the waste;

     
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    c3) The USEPA identification number, name, and address of the generator
    and the transporter, if available;
     
    d4) A description and the quantity of each unmanifested hazardous waste and
    facility received;
     
    e5) The method of treatment, storage, or disposal for each hazardous waste;
     
    f6) The certification signed by the owner or operator of the facility or the
    owner or operator’s authorized representative; and
     
    g7) A brief explanation of why the waste was unmanifested, if known.
     
    b) The following requirements apply effective September 5, 2005: If a facility
    accepts for treatment, storage, or disposal any hazardous waste from an off-site
    source without an accompanying manifest, or without an accompanying shipping
    paper, as described by 35 Ill. Adm. Code 723.120(e), and if the waste is not
    excluded from the manifest requirement by 35 Ill. Adm. Code 260 through 265,
    then the owner or operator must prepare and submit a letter to the Agency within
    fifteen days after receiving the waste. The unmanifested waste report must
    contain the following information:
     
    1) The USEPA identification number, name, and address of the facility;
     
    2) The date the facility received the waste;
     
    3) The USEPA identification number, name, and address of the generator
    and the transporter, if available;
     
    4) A description and the quantity of each unmanifested hazardous waste the
    facility received;
     
    5) The method of treatment, storage, or disposal for each hazardous waste;
     
    6) The certification signed by the owner or operator of the facility or its
    authorized representative; and
     
    7) A brief explanation of why the waste was unmanifested, if known.
     
    BOARD NOTE: Small quantities of hazardous waste are excluded from regulation under this
    Part and do not require a manifest. Where a facility receives unmanifested hazardous wastes, the
    Board suggests USEPA has suggested that the owner or operator obtain from each generator a
    certification that the waste qualifies for exclusion. Otherwise, the Board the Board suggests
    USEPA has suggested that the owner or operator file an unmanifested waste report for the
    hazardous waste movement. Subsection (a) is derived from 40 CFR 264.76 (2004), effective

     
    301
    until September 5, 2006. Subsection (b) is derived from 40 CFR 264.76 (2005), effective
    September 5, 2006.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART F: RELEASES FROM SOLID WASTE MANAGEMENT UNITS
     
    Section 724.193 Hazardous Constituents
     
    a) The Agency must specify in the facility permit the hazardous constituents to
    which the groundwater protection standard of Section 724.192 applies. Hazardous
    constituents are constituents identified in Appendix H of 35 Ill. Adm. Code 721
    that have been detected in groundwater in the uppermost aquifer underlying a
    regulated unit and that are reasonably expected to be in or derived from waste
    contained in a regulated unit, unless the Agency has excluded them under
    subsection (b) of this Section.
     
    b) The Agency must exclude a 35 Ill. Adm. Code 721, Appendix H constituent in
    Appendix H of 35 Ill. Adm. Code 721 from the list of hazardous constituents
    specified in the facility permit if it finds that the constituent is not capable of
    posing a substantial present or potential hazard to human health or the
    environment. In deciding whether to grant an exemption, the Agency must
    consider the following:
     
    1) Potential adverse effects on groundwater quality, considering the
    following:
     
    A) The physical and chemical characteristics of the waste in the
    regulated unit, including its potential for migration;
     
    B) The hydrogeological characteristics of the facility and surrounding
    land;
     
    C) The quantity of groundwater and the direction of groundwater
    flow;
     
    D) The proximity and withdrawal rates of groundwater users;
     
    E) The current and future uses of groundwater in the area;
     
    F) The existing quality of groundwater, including other sources of
    contamination, and their cumulative impact on the groundwater
    quality;
     
    G) The potential for health risks caused by human exposure to waste
    constituents;

     
    302
     
    H) The potential damage to wildlife, crops, vegetation, and physical
    structures caused by exposure to waste constituents;
     
    I) The persistence and permanence of the potential adverse effects;
    and
     
    2) Potential adverse effects on hydraulically-connected surface water quality,
    considering the following:
     
    A) The volume and physical and chemical characteristics of the waste
    in the regulated unit;
     
    B) The hydrogeological characteristics of the facility and surrounding
    land;
     
    C) The quantity and quality of groundwater and the direction of
    groundwater flow;
     
    D) The patterns of rainfall in the region;
     
    E) The proximity of the regulated unit to surface waters;
     
    F) The current and future uses of surface waters in the area and any
    water quality standards established for those surface waters;
     
    G) The existing quality of surface water, including other sources of
    contamination, and the cumulative impact on surface water quality;
     
    H) The potential for health risks caused by human exposure to waste
    constituents;
     
    I) The potential damage to wildlife, crops, vegetation, and physical
    structures caused by exposure to waste constituents; and
     
    J) The persistence and permanence of the potential adverse effects.
     
    c) In making any determination under subsection (b) of this Section about the use of
    groundwater in the area around the facility, the Agency must consider any
    identification of underground sources of drinking water and exempted aquifers
    made under 35 Ill. Adm. Code 704.123.
     
    d) The Agency must make specific written findings in granting any exemptions
    under subsection (b) of this Section.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)

     
    303
     
    Section 724.194 Concentration Limits
     
    a) The Agency must specify in the facility permit concentration limits in the
    groundwater for hazardous constituents established under Section 724.193. The
    following must be true of the concentration of a hazardous constituent:
     
    1) It must not exceed the background level of that constituent in the
    groundwater at the time that limit is specified in the permit; or
     
    2) For any of the constituents listed in Table 1, it must not exceed the
    respective value given in that Table if the background level of the
    constituent is below the value given in Table 1; or
     
    3) It must not exceed an alternative limit established by the Agency under
    subsection (b) of this Section.
     
    TABLE 1 -- MAXIMUM CONCENTRATION OF CONSTITUENTS
    FOR GROUNDWATER PROTECTION
     
     
     
    Constituent
    Maximum
    Concentration
    (mg/lmg/
    )
     
    Arsenic 0.05
    Barium 1.0
    Cadmium 0.01
    Chromium 0.05
    Lead 0.05
    Mercury 0.002
    Selenium 0.01
    Silver 0.05
    Endrin (1,2,3,4,10,10-hexachloro-6,7-
    epoxy-1,4,4a,5,6,7,8,8a-octahydro-
    endo,endo-1,4:5,8-dimethanonaphthalene)
    0.0002
    Lindane (1,2,3,4,5,6-hexachlorocyclo-
    hexane, gamma isomer)
    0.004
    Methoxychlor (1,1,1-Trichloro-2,2'-bis-(p-
    methoxyphenyl)ethane)
    0.1
    Toxaphene (Technical chlorinated
    camphene, 67-69 percent chlorine)
    0.005
    2,4-D (2,4-Dichlorophenoxyacetic acid) 0.1
    2,4,5-TP (Silvex) (2,4,5-Trichlorophenoxy-
    propionic acid)
    0.01
     
    b) The Agency must establish an alternative concentration limit for a hazardous

     
    304
    constituent if it finds that the constituent will not pose a substantial present or
    potential hazard to human health or the environment as long as the alternative
    concentration limit is not exceeded. In establishing alternate concentration limits,
    the Agency must consider the following factors:
     
    1) Potential adverse effects on groundwater quality, considering the
    following:
     
    A) The physical and chemical characteristics of the waste in the
    regulated unit, including its potential for migration;
     
    B) The hydrogeological characteristics of the facility and surrounding
    land;
     
    C) The quantity of groundwater and the direction of groundwater
    flow;
     
    D) The proximity and withdrawal rates of groundwater users;
     
    E) The current and future uses of groundwater in the area;
     
    F) The existing quality of groundwater, including other sources of
    contamination and their cumulative impact on the groundwater
    quality;
     
    G) The potential for health risks caused by human exposure to waste
    constituents;
     
    H) The potential damage to wildlife, crops, vegetation, and physical
    structures caused by exposure to waste constituents;
     
    I) The persistence and permanence of the potential adverse effects;
    and
     
    2) Potential adverse effects on hydraulically-connected surface-water quality,
    considering the following:
     
    A) The volume and physical and chemical characteristics of the waste
    in the regulated unit;
     
    B) The hydrogeological characteristics of the facility and surrounding
    land;
     
    C) The quantity and quality of groundwater and the direction of
    groundwater flow;
     

     
    305
    D) The patterns of rainfall in the region;
     
    E) The proximity of the regulated unit to surface waters;
     
    F) The current and future uses of surface waters in the area and any
    water quality standards established for those surface waters;
     
    G) The existing quality of surface water, including other sources of
    contamination and the cumulative impact on surface-water quality;
     
    H) The potential for health risks caused by human exposure to waste
    constituents;
     
    I) The potential damage to wildlife, crops, vegetation, and physical
    structures caused by exposure to waste constituents; and
     
    J) The persistence and permanence of the potential adverse effects.
     
    c) In making any determination under subsection (b) of this Section about the use of
    groundwater in the area around the facility, the Agency must consider any
    identification of underground sources of drinking water and exempted aquifers
    made under 35 Ill. Adm. Code 704.123.
     
    d) The Agency must make specific written findings in setting any alternate
    concentration limits under subsection (b) of this Section.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART H: FINANCIAL REQUIREMENTS
     
    Section 724.243 Financial Assurance for Closure
     
    An owner or operator of each facility must establish financial assurance for closure of the
    facility. The owner or operator must choose from the options that are specified in subsections
    (a) through (f) of this Section.
     
    a) Closure trust fund.
     
    1) An owner or operator may satisfy the requirements of this Section by
    establishing a closure trust fund that conforms to the requirements of this
    subsection (a) and submitting an original signed duplicate of the trust
    agreement to the Agency. An owner or operator of a new facility must
    submit the original signed duplicate of the trust agreement to the Agency
    at least 60 days before the date on which hazardous waste is first received
    for treatment, storage or disposal. The trustee must be an entity that has
    the authority to act as a trustee and whose trust operations are regulated

     
    306
    and examined by a federal or State agency.
     
    2) The wording of the trust agreement must be that specified in Section
    724.251 and the trust agreement must be accompanied by a formal
    certification of acknowledgment (as specified in Section 724.251).
    Schedule A of the trust agreement must be updated within 60 days after a
    change in the amount of the current closure cost estimate covered by the
    agreement.
     
    3) Payments into the trust fund must be made annually by the owner or
    operator over the term of the initial RCRA permit or over the remaining
    operating life of the facility as estimated in the closure plan, whichever
    period is shorter; this period is hereafter referred to as the “pay-in period.”
    The payments into the closure trust fund must be made as follows:
     
    A) For a new facility, the first payment must be made before the
    initial receipt of hazardous waste for treatment, storage, or
    disposal. A receipt from the trustee for this payment must be
    submitted by the owner or operator to the Agency before this
    initial receipt of hazardous waste. The first payment must be at
    least equal to the current closure cost estimate, except as provided
    in subsection (g) of this Section, divided by the number of years in
    the pay-in period. Subsequent payments must be made no later
    than 30 days after each anniversary date of the first payment. The
    amount of each subsequent payment must be determined by the
    following formula:
     
    Next payment = (CE - CV) / Y
     
    where CE is the current closure cost estimate, CV is the
    current value of the trust fund and Y is the number of years
    remaining in the pay-in period.
     
    B) If an owner or operator establishes a trust fund as specified in 35
    Ill. Adm. Code 725.243(a) and the value of that trust fund is less
    than the current closure cost estimate when a permit is awarded for
    the facility, the amount of the current closure cost estimate still to
    be paid into the trust fund must be paid in over the pay-in period as
    defined in subsection (a)(3) of this Section. Payments must
    continue to be made no later than 30 days after each anniversary
    date of the first payment made pursuant to 35 Ill. Adm. Code 725.
    The amount of each payment must be determined by the following
    formula:
     
    Next payment = (CE - CV) / Y
     

     
    307
    where CE is the current closure cost estimate, CV is the
    current value of the trust fund, and Y is the number of years
    remaining in the pay-in period.
     
    4) The owner or operator may accelerate payments into the trust fund or may
    deposit the full amount of the current closure cost estimate at the time the
    fund is established. However, the owner or operator must maintain the
    value of the fund at no less than the value that the fund would have if
    annual payments were made as specified in subsection (a)(3) of this
    Section.
     
    5) If the owner or operator establishes a closure trust fund after having used
    one or more alternate mechanisms specified in this Section or in 35 Ill.
    Adm. Code 725.243, its first payment must be in at least the amount that
    the fund would contain if the trust fund were established initially and
    annual payments made according to specifications of this subsection (a)
    and 35 Ill. Adm. Code 725.243, as applicable.
     
    6) After the pay-in period is completed, whenever the current closure cost
    estimate changes, the owner or operator must compare the new estimate
    with the trustee’s most recent annual valuation of the trust fund. If the
    value of the fund is less than the amount of the new estimate, the owner or
    operator, within 60 days after the change in the cost estimate, must either
    deposit an amount into the fund so that its value after this deposit at least
    equals the amount of the current closure cost estimate or obtain other
    financial assurance as specified in this Section to cover the difference.
     
    7) If the value of the trust fund is greater than the total amount of the current
    closure cost estimate, the owner or operator may submit a written request
    to the Agency for release of the amount in excess of the current closure
    cost estimate.
     
    8) If an owner or operator substitutes other financial assurance, as specified
    in this Section for all or part of the trust fund, it may submit a written
    request to the Agency for release of the amount in excess of the current
    closure cost estimate covered by the trust fund.
     
    9) Within 60 days after receiving a request from the owner or operator for
    release of funds as specified in subsection (a)(7) or (a)(8) of this Section,
    the Agency must instruct the trustee to release to the owner or operator
    such funds as the Agency specifies in writing.
     
    10) After beginning partial or final closure, an owner or operator or another
    person authorized to conduct partial or final closure may request
    reimbursement for closure expenditures by submitting itemized bills to the
    Agency. The owner or operator may request reimbursement for partial

     
    308
    closure only if sufficient funds are remaining in the trust fund to cover the
    maximum costs of closing the facility over its remaining operating life.
    Within 60 days after receiving bills for partial or final closure activities,
    the Agency must instruct the trustee to make reimbursement in those
    amounts as the Agency specifies in writing if the Agency determines that
    the partial or final closure expenditures are in accordance with the
    approved closure plan, or otherwise justified. If the Agency determines
    that the maximum cost of closure over the remaining life of the facility
    will be significantly greater than the value of the trust fund, it must
    withhold reimbursement of such amounts as it deems prudent until it
    determines, in accordance with subsection (i) of this Section, that the
    owner or operator is no longer required to maintain financial assurance for
    final closure of the facility. If the Agency does not instruct the trustee to
    make such reimbursements, the Agency must provide the owner or
    operator with a detailed written statement of reasons.
     
    11) The Agency must agree to termination of the trust when either of the
    following occurs:
     
    A) An owner or operator substitutes alternate financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (i).
     
    b) Surety bond guaranteeing payment into a closure trust fund.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining a surety bond that conforms to the requirements of this
    subsection (b) and submitting the bond to the Agency. An owner or
    operator of a new facility must submit the bond to the Agency at least 60
    days before the date on which hazardous waste is first received for
    treatment, storage or disposal. The bond must be effective before this
    initial receipt of hazardous waste. The surety company issuing the bond
    must, at a minimum, be among those listed as acceptable sureties on
    Federal federal bonds in Circular 570 of the U.S. Department of the
    Treasury.
     
    2) The wording of the surety bond must be that specified in Section 724.251.
     
    3) The owner or operator who uses a surety bond to satisfy the requirements
    of this Section must also establish a standby trust fund. Under the terms
    of the bond, all payments made thereunder will be deposited by the surety
    directly into the standby trust fund in accordance with instructions from
    the Agency. This standby trust fund must meet the requirements specified
    in subsection (a) of this Section except as follows:

     
    309
     
    A) An original, signed duplicate of the trust agreement must be
    submitted to the Agency with the surety bond; and
     
    B) Until the standby trust fund is funded pursuant to the requirements
    of this Section, the following are not required by these regulations:
     
    i) Payments into the trust fund as specified in subsection (a)
    of this Section;
     
    ii) Updating of Schedule A of the trust agreement (see 40 CFR
    264.151(a) 35 Ill. Adm. Code 724.251) to show current
    closure cost estimates;
     
    iii) Annual valuations, as required by the trust agreement; and
     
    iv) Notices of nonpayment as required by the trust agreement.
     
    4) The bond must guarantee that the owner or operator will do one of the
    following:
     
    A) Fund the standby trust fund in an amount equal to the penal sum of
    the bond before the beginning of final closure of the facility;
     
    B) Fund the standby trust fund in an amount equal to the penal sum
    within 15 days after an order to begin final closure is issued by the
    Board or a U.S. district court or other court of competent
    jurisdiction; or
     
    C) Provide alternate financial assurance as specified in this Section,
    and obtain the Agency’s written approval of the assurance
    provided, within 90 days after receipt by both the owner or
    operator and the Agency of a notice of cancellation of the bond
    from the surety.
     
    5) Under the terms of the bond, the surety will become liable on the bond
    obligation when the owner or operator fails to perform as guaranteed by
    the bond.
     
    6) The penal sum of the bond must be in an amount at least equal to the
    current closure cost estimate, except as provided in subsection (g) of this
    Section.
     
    7) Whenever the current closure cost estimate increases to an amount greater
    than the penal sum, the owner or operator, within 60 days after the
    increase, must either cause the penal sum to be increased to an amount at

     
    310
    least equal to the current closure cost estimate and submit evidence of
    such increase to the Agency or obtain other financial assurance, as
    specified in this Section, to cover the increase. Whenever the current
    closure cost estimate decreases, the penal sum may be reduced to the
    amount of the current closure cost estimate following written approval by
    the Agency.
     
    8) Under the terms of the bond, the surety may cancel the bond by sending
    notice of cancellation by certified mail to the owner or operator and to the
    Agency. Cancellation may not occur, however, during the 120 days
    beginning on the date of receipt of the notice of cancellation by both the
    owner or operator and the Agency, as evidence by the return receipts.
     
    9) The owner or operator may cancel the bond if the Agency has given prior
    written consent based on its receipt of evidence of alternate financial
    assurance as specified in this Section.
     
    c) Surety bond guaranteeing performance of closure.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining a surety bond that conforms to the requirements of this
    subsection (c) and submitting the bond to the Agency. An owner or
    operator of a new facility must submit the bond to the Agency at least 60
    days before the date on which hazardous waste is first received for
    treatment, storage, or disposal. The bond must be effective before this
    initial receipt of hazardous waste. The surety company issuing the bond
    must, at a minimum, be among those listed as acceptable sureties on
    Federal federal bonds in Circular 570 of the U.S. Department of the
    Treasury.
     
    2) The wording of the surety bond must be that specified in Section 724.251.
     
    3) The owner or operator who uses a surety bond to satisfy the requirements
    of this Section must also establish a standby trust fund. Under the terms
    of the bond, all payments made thereunder will be deposited by the surety
    directly into the standby trust fund in accordance with instructions from
    the Agency. This standby trust must meet the requirements specified in
    subsection (a) of this Section, except as follows:
     
    A) An original, signed duplicate of the trust agreement must be
    submitted to the Agency with the surety bond; and
     
    B) Unless the standby trust fund is funded pursuant to the
    requirements of this Section, the following are not required by
    these regulations:
     

     
    311
    i) Payments into the trust fund, as specified in subsection (a)
    of this Section;
     
    ii) Updating of Schedule A of the trust agreement (as specified
    in Section 724.251) to show current closure cost estimates;
     
    iii) Annual valuations, as required by the trust agreement; and
     
    iv) Notices of nonpayment, as required by the trust agreement.
     
    4) The bond must guarantee that the owner or operator will do the following:
     
    A) Perform final closure in accordance with the closure plan and other
    requirements of the permit for the facility whenever required to do
    so; or
     
    B) Provide alternative financial assurance, as specified in this Section,
    and obtain the Agency’s written approval of the assurance
    provided, within 90 days after receipt by both the owner or
    operator and the Agency of a notice of cancellation of the bond
    from the surety.
     
    5) Under the terms of the bond, the surety will become liable on the bond
    obligation when the owner or operator fails to perform as guaranteed by
    the bond. Following a final judicial determination or Board order finding
    that the owner or operator has failed to perform final closure in
    accordance with the approved closure plan and other permit requirements
    when required to do so, under the terms of the bond the surety will
    perform final closure, as guaranteed by the bond, or will deposit the
    amount of the penal sum into the standby trust fund.
     
    6) The penal sum of the bond must be in an amount at least equal to the
    current closure cost estimate.
     
    7) Whenever the current closure cost estimate increases to an amount greater
    than the penal sum, the owner or operator, within 60 days after the
    increase, must either cause the penal sum to be increased to an amount at
    least equal to the current closure cost estimate and submit evidence of
    such increase to the Agency or obtain other financial assurance as
    specified in this Section. Whenever the current closure cost estimate
    decreases, the penal sum may be reduced to the amount of the current
    closure cost estimate following written approval by the Agency.
     
    8) Under the terms of the bond, the surety may cancel the bond by sending
    notice of cancellation by certified mail to the owner or operator and to the
    Agency. Cancellation may not occur, however, during the 120 days

     
    312
    beginning on the date of receipt of the notice of cancellation by both the
    owner or operator and the Agency, as evidenced by the return receipts.
     
    9) The owner or operator may cancel the bond if the Agency has given prior
    written consent. The Agency must provide such written consent when
    either of the following occurs:
     
    A) An owner or operator substitutes alternative financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (i) of this Section.
     
    10) The surety must not be liable for deficiencies in the performance of
    closure by the owner or operator after the Agency releases the owner or
    operator from the requirements of this Section in accordance with
    subsection (i) of this Section.
     
    d) Closure letter of credit.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining an irrevocable standby letter of credit that conforms to the
    requirements of this subsection (d) and submitting the letter to the
    Agency. An owner or operator of a new facility must submit the letter of
    credit to the Agency at least 60 days before the date on which hazardous
    waste is first received for treatment, storage, or disposal. The letter of
    credit must be effective before this initial receipt of hazardous waste. The
    issuing institution must be an entity that has the authority to issue letters
    of credit and whose letter-of-credit operations are regulated and examined
    by a federal or state agency.
     
    2) The wording of the letter of credit must be that specified in Section
    724.251.
     
    3) An owner or operator who uses a letter of credit to satisfy the
    requirements of this Section must also establish a standby trust fund.
    Under the terms of the letter of credit, all amounts paid pursuant to a draft
    by the Agency must be deposited by the issuing institution directly into
    the standby trust fund in accordance with instructions from the Agency.
    This standby trust fund must meet the requirements of the trust fund
    specified in subsection (a) of this Section, except as follows:
     
    A) An original, signed duplicate of the trust agreement must be
    submitted to the Agency with the letter of credit; and
     
    B) Unless the standby trust fund is funded pursuant to the

     
    313
    requirements of this Section, the following are not required by
    these regulations.
     
    i) Payments into the trust fund, as specified in subsection (a)
    of this Section;
     
    ii) Updating of Schedule A of the trust agreement (as specified
    in Section 724.251) to show current closure cost estimates;
     
    iii) Annual valuations, as required by the trust agreement; and
     
    iv) Notices of nonpayment, as required by the trust agreement.
     
    4) The letter or credit must be accompanied by a letter from the owner or
    operator referring to the letter of credit by number, issuing institution, and
    date and providing the following information: the USEPA identification
    number, name and address of the facility, and the amount of funds assured
    for closure of the facility by the letter of credit.
     
    5) The letter of credit must be irrevocable and issued for a period of at least
    one year. The letter of credit must provide that the expiration date will be
    automatically extended for a period of at least one year unless, at least 120
    days before the current expiration date, the issuing institution notifies both
    the owner or operator and the Agency by certified mail of a decision not to
    extend the expiration date. Under the terms of the letter of credit, the 120
    days will begin on the date when both the owner or operator and the
    Agency have received the notice, as evidenced by the return receipts.
     
    6) The letter of credit must be issued in an amount at least equal to the
    current closure cost estimate, except as provided in subsection (g) of this
    Section.
     
    7) Whenever the current closure cost estimate increases to an amount greater
    than the amount of the credit, the owner or operator, within 60 days after
    the increase, must either cause the amount of the credit to be increased so
    that it at least equals the current closure cost estimate and submit evidence
    of such increase to the Agency, or obtain other financial assurance, as
    specified in this Section, to cover the increase. Whenever the current
    closure cost estimate decreases, the amount of the credit may be reduced
    to the amount of the current closure cost estimate following written
    approval by the Agency.
     
    8) Following a final judicial determination or Board order finding that the
    owner or operator has failed to perform final closure in accordance with
    the closure plan and other permit requirements when required to do so, the
    Agency may draw on the letter of credit.

     
    314
     
    9) If the owner or operator does not establish alternative financial assurance,
    as specified in this Section, and obtain written approval of such alternative
    assurance from the Agency within 90 days after receipt by both the owner
    or operator and the Agency of a notice from issuing institution that it has
    decided not to extend the letter of credit beyond the current expiration
    date, the Agency must draw on the letter of credit. The Agency may delay
    the drawing if the issuing institution grants an extension of the term of the
    credit. During the last 30 days of any such extension the Agency must
    draw on the letter of credit if the owner or operator has failed to provide
    alternative financial assurance, as specified in this Section, and obtain
    written approval of such assurance from the Agency.
     
    10) The Agency must return the letter of credit to the issuing institution for
    termination when either of the following occurs:
     
    A) An owner or operator substitutes alternative financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (i) of this Section.
     
    e) Closure insurance.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining closure insurance that conforms to the requirements of this
    subsection (e) and submitting a certificate of such insurance to the
    Agency. An owner or operator of a new facility must submit the
    certificate of insurance to the Agency at least 60 days before the date on
    which hazardous waste is first received for treatment, storage, or disposal.
    The insurance must be effective before this initial receipt of hazardous
    waste. At a minimum, the insurer must be licensed to transact the
    business of insurance or be eligible to provide insurance as an excess or
    surplus lines insurer in one or more States.
     
    2) The wording of the certificate of insurance must be that specified in
    Section 724.251.
     
    3) The closure insurance policy must be issued for a face amount at least
    equal to the current closure cost estimate, except as provided in subsection
    (g) of this Section. The term “face amount” means the total amount the
    insurer is obligated to pay under the policy. Actual payments by the
    insurer will not change the face amount, although the insurer’s future
    liability will be lowered by the amount of the payments.
     
    4) The closure insurance policy must guarantee that funds will be available

     
    315
    to close the facility whenever final closure occurs. The policy must also
    guarantee that, once final closure begins, the insurer will be responsible
    for paying out funds, up to an amount equal to the face amount of the
    policy, upon the direction of the Agency to such party or parties, as the
    Agency specifies.
     
    5) After beginning partial or final closure, an owner or operator or any other
    person authorized to conduct closure may request reimbursement for
    closure expenditures by submitting itemized bills to the Agency. The
    owner or operator may request reimbursements for partial closure only if
    the remaining value of the policy is sufficient to cover the maximum costs
    of closing the facility over its remaining operating life. Within 60 days
    after receiving bills for closure activities, the Agency must instruct the
    insurer to make reimbursement in such amounts, as the Agency specifies
    in writing, if the Agency determines that the partial or final closure
    expenditures are in accordance with the approved closure plan or
    otherwise justified. If the Agency determines that the maximum cost of
    closure over the remaining life of the facility will be significantly greater
    than the face amount of the policy, it must withhold reimbursement of
    such amounts that it deems prudent, until it determines, in accordance with
    subsection (i) of this Section, that the owner or operator is no longer
    required to maintain financial assurance for closure of the facility. If the
    Agency does not instruct the insurer to make such reimbursements, the
    Agency must provide the owner or operator with a detailed written
    statement of reasons.
     
    6) The owner or operator must maintain the policy in full force and effect
    until the Agency consents to termination of the policy by the owner or
    operator, as specified in subsection (e)(10) of this Section. Failure to pay
    the premium, without substitution of alternative financial assurance, as
    specified in this Section, will constitute a significant violation of these
    regulations, warranting such remedy as the Board may impose pursuant to
    the Environmental Protection Act. Such violation will be deemed to begin
    upon receipt by the Agency of a notice of future cancellation, termination
    or failure to renew due to nonpayment of the premium, rather than upon
    the date of expiration.
     
    7) Each policy must contain a provision allowing assignment of the policy to
    a successor owner or operator. Such assignment may be conditional upon
    consent of the insurer, provided such consent is not unreasonably refused.
     
    8) The policy must provide that the insurer may not cancel, terminate, or fail
    to renew the policy except for failure to pay the premium. The automatic
    renewal of the policy must, at a minimum, provide the insured with the
    option of renewal at the face amount of the expiring policy. If there is a
    failure to pay the premium, the insurer may elect to cancel, terminate, or

     
    316
    fail to renew the policy by sending notice by certified mail to the owner or
    operator and the Agency. Cancellation, termination, or failure to renew
    may not occur, however, during the 120 days beginning with the date of
    receipt of the notice by both the Agency and the owner or operator, as
    evidenced by the return receipts. Cancellation, termination, or failure to
    renew may not occur, and the policy will remain in full force and effect, in
    the event that on or before the date of expiration one of the following
    occurs:
     
    A) The Agency deems the facility abandoned;
     
    B) The permit is terminated or revoked or a new permit is denied;
     
    C) Closure is ordered by the Board or a U.S. district court or other
    court of competent jurisdiction;
     
    D) The owner or operator is named as debtor in a voluntary or
    involuntary proceeding under Title 11 of the United States Code
    (Bankruptcy); or
     
    E) The premium due is paid.
     
    9) Whenever the current closure cost estimate increases to an amount greater
    than the face amount of the policy, the owner or operator, within 60 days
    after the increase, must either cause the face amount to be increased to an
    amount at least equal to the current closure cost estimate and submit
    evidence of such increase to the Agency, or obtain other financial
    assurance, as specified in this Section to cover the increase. Whenever the
    current closure cost estimate decreases, the face amount may be reduced
    to the amount of the current closure cost estimate following written
    approval by the Agency.
     
    10) The Agency must give written consent to the owner or operator that it may
    terminate the insurance policy when either of the following occurs:
     
    A) An owner or operator substitutes alternative financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (i) of this Section.
     
    f) Financial test and corporate guarantee for closure.
     
    1) An owner or operator may satisfy the requirements of this Section by
    demonstrating that it passes a financial test, as specified in this subsection
    (f). To pass this test the owner or operator must meet the criteria of either

     
    317
    subsection (f)(1)(A) or (f)(1)(B) of this Section:
     
    A) The owner or operator must have the following:
     
    i) Two of the following three ratios: a ratio of total liabilities
    to net worth less than 2.0; a ratio of the sum of net income
    plus depreciation, depletion and amortization to total
    liabilities greater than 0.1; and a ratio of current assets to
    current liabilities greater than 1.5;
     
    ii) Net working capital and tangible net worth each at least six
    times the sum of the current closure and post-closure cost
    estimates; and the current plugging and abandonment cost
    estimates;
     
    iii) Tangible net worth of at least $10 million; and
     
    iv) Assets located in the United States amounting to at least 90
    percent of total assets or at least six times the sum of the
    current closure and post-closure cost estimates and the
    current plugging and abandonment cost estimates.
     
    B) The owner or operator must have the following:
     
    i) A current rating for its most recent bond issuance of AAA,
    AA, A, or BBB as issued by Standard and Poor’s or Aaa,
    Aa, A, or Baa as issued by Moody’s;
     
    ii) Tangible net worth at least six times the sum of the current
    closure and post-closure cost estimates and the current
    plugging and abandonment cost estimates;
     
    iii) Tangible net worth of at least $10 million; and
     
    iv) Assets located in the United States amounting to at least 90
    percent of total assets or at least six times the sum of the
    current closure and post-closure estimates and the current
    plugging and abandonment cost estimates.
     
    2) The phrase “current closure and post-closure cost estimates,” as used in
    subsection (f)(1) of this Section, refers to the cost estimates required to be
    shown in subsections 1-4 of the letter from the owner’s or operator’s chief
    financial officer (40 CFR 264.151(f)) (incorporated by reference in see
    Section 724.251). The phrase “current plugging and abandonment cost
    estimates,” as used in subsection (f)(1) of this Section, refers to the cost
    estimates required to be shown in subsections 1-4 of the letter from the

     
    318
    owner’s or operator’s chief financial officer (40 CFR 144.70(f)),
    incorporated by reference in see 35 Ill. Adm. Code 704.240).
     
    3) To demonstrate that it meets this test, the owner or operator must submit
    the following items to the Agency:
     
    A) A letter signed by the owner’s or operator’s chief financial officer
    and worded as specified in Section 724.251; and
     
    B) A copy of the independent certified public accountant’s report on
    examination of the owner’s or operator’s financial statements for
    the latest completed fiscal year; and
     
    C) A special report from the owner’s or operator’s independent
    certified public accountant to the owner or operator stating the
    following:
     
    i) That the accountant has compared the data that the letter
    from the chief financial officer specifies as having been
    derived from the independently audited, year-end financial
    statements for the latest fiscal year with the amounts in
    such financial statements; and
     
    ii) In connection with that procedure, that no matters came to
    the accountant’s attention which caused the accountant to
    believe that the specified data should be adjusted.
     
    4) An owner or operator of a new facility must submit the items specified in
    subsection (f)(3) of this Section to the Agency at least 60 days before the
    date on which hazardous waste is first received for treatment, storage, or
    disposal.
     
    5) After the initial submission of items specified in subsection (f)(3) of this
    Section, the owner or operator must send updated information to the
    Agency within 90 days after the close of each succeeding fiscal year. This
    information must consist of all three items specified in subsection (f)(3) of
    this Section.
     
    6) If the owner or operator no longer meets the requirements of subsection
    (f)(1) of this Section the owner or operator must send notice to the Agency
    of intent to establish alternative financial assurance, as specified in this
    Section. The notice must be sent by certified mail within 90 days after the
    end of the fiscal year for which the year-end financial data show that the
    owner or operator no longer meets the requirements. The owner or
    operator must provide the alternative financial assurance within 120 days
    after the end of such fiscal year.

     
    319
     
    7) The Agency may, based on a reasonable belief that the owner or operator
    may no longer meet the requirements of subsection (f)(1) of this Section,
    require reports of financial condition at any time from the owner or
    operator in addition to those specified in subsection (f)(3) of this Section.
    If the Agency finds, on the basis of such reports or other information, that
    the owner or operator no longer meets the requirements of subsection
    (f)(1) of this Section, the owner or operator must provide alternative
    financial assurance, as specified in this Section, within 30 days after
    notification of such a finding.
     
    8) The Agency may disallow use of this test on the basis of qualifications in
    the opinion expressed by the independent certified public accountant in
    the accountant’s report on examination of the owner’s or operator’s
    financial statements (see subsection (f)(3)(B) of this Section). An adverse
    opinion or a disclaimer of opinion will be cause for disallowance. The
    Agency must evaluate other qualifications on an individual basis. The
    owner or operator must provide alternative financial assurance, as
    specified in this Section, within 30 days after notification of the
    disallowance.
     
    9) The owner or operator is no longer required to submit the items specified
    in subsection (f)(3) of this Section when either of the following occurs:
     
    A) An owner or operator substitutes alternative financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (i) of this Section.
     
    10) An owner or operator may meet the requirements of this Section by
    obtaining a written guarantee, hereafter referred to as “corporate
    guarantee.” The guarantor must be the direct or higher-tier parent
    corporation of the owner or operator, a firm whose parent corporation is
    also the parent corporation of the owner or operator, or a firm with a
    “substantial business relationship” with the owner or operator. The
    guarantor must meet the requirements for owners or operators in
    subsections (f)(1) through (f)(8) of this Section, must comply with the
    terms of the corporate guarantee, and the wording of the corporate
    guarantee must be that specified in Section 724.251. The certified copy of
    the corporate guarantee must accompany the items sent to the Agency, as
    specified in subsection (f)(3) of this Section. One of these items must be
    the letter from the guarantor’s chief financial officer. If the guarantor’s
    parent corporation is also the parent corporation of the owner or operator,
    the letter must describe the value received in consideration of the
    guarantee. If the guarantor is a firm with a “substantial business

     
    320
    relationship” with the owner or operator, this letter must describe this
    “substantial business relationship” and the value received in consideration
    of the guarantee. The terms of the corporate guarantee must provide as
    follows:
     
    A) If the owner or operator fails to perform final closure of a facility
    covered by the corporate guarantee in accordance with the closure
    plan and other permit requirements whenever required to do so, the
    guarantor will do so or establish a trust fund, as specified in
    subsection (a) of this Section, in the name of the owner or
    operator.
     
    B) The corporate guarantee will remain in force unless the guarantor
    sends notice of cancellation by certified mail to the owner or
    operator and to the Agency. Cancellation may not occur, however,
    during the 120 days beginning on the date of receipt of the notice
    of cancellation by both the owner or operator and the Agency, as
    evidenced by the return receipts.
     
    C) If the owner or operator fails to provide alternative financial
    assurance as specified in this Section and obtain the written
    approval of such alternative assurance from the Agency within 90
    days after receipt by both the owner or operator and the Agency of
    a notice of cancellation of the corporate guarantee from the
    guarantor, the guarantor will provide such alternative financial
    assurance in the name of the owner or operator.
     
    g) Use of multiple financial mechanisms. An owner or operator may satisfy the
    requirements of this Section by establishing more than one financial mechanism
    per facility. These mechanisms are limited to trust funds, surety bonds
    guaranteeing payment into a trust fund, letters of credit, and insurance. The
    mechanisms must be as specified in subsections (a), (b), (d), and (e) of this
    Section, respectively, except that it is the combination of mechanisms, rather than
    the single mechanism, that must provide financial assurance for an amount at least
    equal to the current closure cost estimate. If an owner or operator uses a trust
    fund in combination with a surety bond or a letter of credit, it may use the trust
    fund as the standby trust fund for the other mechanisms. A single standby trust
    fund may be established for two or more mechanisms. The Agency may use any
    or all of the mechanisms to provide for closure of the facility.
     
    h) Use of a financial mechanism for multiple facilities. An owner or operator may
    use a financial assurance mechanism specified in this Section to meet the
    requirements of this Section for more than one facility. Evidence of financial
    assurance submitted to the Agency must include a list showing, for each facility,
    the USEPA identification number, name, address, and the amount of funds for
    closure assured by the mechanism. The amount of funds available through the

     
    321
    mechanism must be no less than the sum of funds that would be available if a
    separate mechanism had been established and maintained for each facility. The
    amount of funds available to the Agency must be sufficient to close all of the
    owner or operator’s facilities. In directing funds available through the mechanism
    for closure of any of the facilities covered by the mechanism, the Agency may
    direct only the amount of funds designated for that facility, unless the owner or
    operator agrees to the use of additional funds available under the mechanism.
     
    i) Release of the owner or operator from the requirements of this Section. Within
    60 days after receiving certifications from the owner or operator and an
    independent registered professional engineer that final approved closure has been
    accomplished in accordance with the closure plan, the Agency must notify the
    owner or operator in writing that it is no longer required by this Section to
    maintain financial assurance for closure of the facility, unless the Agency
    determines that closure has not been in accordance with the approved closure
    plan. The Agency must provide the owner or operator a detailed written
    statement of any such determination that closure has not been in accordance with
    the approved closure plan.
     
    j) Appeal. The following Agency actions are deemed to be permit modifications or
    refusals to modify for purposes of appeal to the Board (35 Ill. Adm. Code
    702.184(e)(3)):
     
    1) An increase in, or a refusal to decrease the amount of, a bond, letter of
    credit, or insurance;
     
    2) Requiring alternative assurance upon a finding that an owner or operator
    or parent corporation no longer meets a financial test.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.245 Financial Assurance for Post-Closure Care
     
    An owner or operator of a hazardous waste management unit subject to the requirements of
    Section 724.244 must establish financial assurance for post-closure care in accordance with the
    approved post-closure plan for the facility 60 days prior to the initial receipt of hazardous waste
    or the effective date of the regulation, whichever is later. The owner or operator must choose
    from among the following options:
     
    a) Post-closure trust fund.
     
    1) An owner or operator may satisfy the requirements of this Section by
    establishing a post-closure trust fund that conforms to the requirements of
    this subsection (a) and submitting an original, signed duplicate of the trust
    agreement to the Agency. An owner or operator of a new facility must
    submit the original, signed duplicate of the trust agreement to the Agency

     
    322
    at least 60 days before the date on which hazardous waste is first received
    for disposal. The trustee must be an entity that has the authority to act as a
    trustee and whose trust operations are regulated and examined by a federal
    or State agency.
     
    2) The wording of the trust agreement must be that specified in Section
    724.251 and the trust agreement accompanied by a formal certification of
    acknowledgment (as specified in Section 724.251). Schedule A of the
    trust agreement must be updated within 60 days after a change in the
    amount of the current post-closure cost estimate covered by the
    agreement.
     
    3) Payments into the trust fund must be made annually by the owner or
    operator over the term of the initial RCRA permit or over the remaining
    operating life of the facility as estimated in the closure plan, whichever
    period is shorter; this period is hereafter referred to as the “pay-in period.”
    The payments into the post-closure trust fund must be made as follows:
     
    A) For a new facility, the first payment must be made before the
    initial receipt of hazardous waste for disposal. A receipt from the
    trustee for this payment must be submitted by the owner or
    operator to the Agency before this initial receipt of hazardous
    waste. The first payment must be at least equal to the current post-
    closure cost estimate, except as provided in subsection (g) of this
    Section, divided by the number of years in the pay-in period.
    Subsequent payments must be made no later than 30 days after
    each anniversary date of the first payment. The amount of each
    subsequent payment must be determined by the following formula:
     
    Next payment = (CE - CV) / Y
     
    where CE is the current post-closure cost estimate, CV is
    the current value of the trust fund, and Y is the number of
    years remaining in the pay-in period.
     
    B) If an owner or operator establishes a trust fund, as specified in 35
    Ill. Adm. Code 725.245(a), and the value of that trust fund is less
    than the current post-closure cost estimate when a permit is
    awarded for the facility, the amount of the current post-closure cost
    estimate still to be paid into the trust fund must be paid in over the
    pay-in period as defined in subsection (a)(3) of this Section.
    Payments must continue to be made no later than 30 days after
    each anniversary date of the first payment made pursuant to 35 Ill.
    Adm. Code 725. The amount of each payment must be determined
    by the following formula:
     

     
    323
    Next payment = (CE - CV) / Y
     
    where CE is the current post-closure cost estimate, CV is
    the current value of the trust fund, and Y is the number of
    years remaining in the pay-in period.
     
    4) The owner or operator may accelerate payments into the trust fund or
    owner or operator must maintain the value of the fund at no less than the
    value that the fund would have if annual payments were made as specified
    in subsection (a)(3) of this Section.
     
    5) If the owner or operator establishes a post-closure trust fund after having
    used one or more alternative mechanisms specified in this Section or in 35
    Ill. Adm. Code 725.245, its first payment must be in at least the amount
    that the fund would contain if the trust fund were established initially and
    annual payments made according to specifications of this subsection (a)
    and 35 Ill. Adm. Code 725.245, as applicable.
     
    6) After the pay-in period is completed, whenever the current post-closure
    cost estimate changes during the operating life of the facility, the owner or
    operator must compare the new estimate with the trustee’s most recent
    annual valuation of the trust fund. If the value of the fund is less than the
    amount of the new estimate, the owner or operator, within 60 days after
    the change in the cost estimate, must either deposit an amount into the
    fund so that its value after this deposit at least equals the amount of the
    current post-closure cost estimate, or obtain other financial assurance, as
    specified in this Section, to cover the difference.
     
    7) During the operating life of the facility, if the value of the trust fund is
    greater than the total amount of the current post-closure cost estimate, the
    owner or operator may submit a written request to the Agency for release
    of the amount in excess of the current post-closure cost estimate.
     
    8) If an owner or operator substitutes other financial assurance as specified in
    this Section for all or part of the trust fund, it may submit a written request
    to the Agency for release of the amount in excess of the current post-
    closure cost estimate covered by the trust fund.
     
    9) Within 60 days after receiving a request from the owner or operator for
    release of funds, as specified in subsection (a)(7) or (a)(8) of this Section,
    the Agency must instruct the trustee to release to the owner or operator
    such funds as the Agency specifies in writing.
     
    10) During the period of post-closure care, the Agency must approve a release
    of funds if the owner or operator demonstrates to the Agency that the
    value of the trust fund exceeds the remaining cost of post-closure care.

     
    324
     
    11) An owner or operator or any other person authorized to perform post-
    closure care may request reimbursement for post-closure care
    expenditures by submitting itemized bills to the Agency. Within 60 days
    after receiving bills for post-closure activities, the Agency must instruct
    the trustee to make requirements in those amounts that the Agency
    specifies in writing if the Agency determines that the post-closure care
    expenditures are in accordance with the approved post-closure plan or
    otherwise justified. If the Agency does not instruct the trustee to make
    such reimbursements, the Agency must provide the owner or operator with
    a detailed written statement of reasons.
     
    12) The Agency must agree to termination of the trust when either of the
    following occurs:
     
    A) An owner or operator substitutes alternative financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (i) of this Section.
     
    b) Surety bond guaranteeing payment into a post-closure trust fund.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining a surety bond that conforms to the requirements of this
    subsection (b) and submitting the bond to the Agency. An owner or
    operator of a new facility must submit the bond to the Agency at least 60
    days before the date on which hazardous waste is first received for
    disposal. The bond must be effective before this initial receipt of
    hazardous waste. The surety company issuing the bond must, at a
    minimum, be among those listed as acceptable sureties on Federal federal
    bonds in Circular 570 of the U.S. Department of the Treasury.
     
    2) The wording of the surety bond must be that specified in Section 724.251.
     
    3) The owner or operator who uses a surety bond to satisfy the requirements
    of this Section must also establish a standby trust fund. Under the terms
    of the bond, all payments made thereunder will be deposited by the surety
    directly into the standby trust fund in accordance with instructions from
    the Agency. This standby trust fund must meet the requirements specified
    in subsection (a) of this Section, except as follows:
     
    A) An original, signed duplicate of the trust agreement must be
    submitted to the Agency with the surety bond; and
     
    B) Until the standby trust fund is funded pursuant to the requirements

     
    325
    of this Section, the following are not required by these regulations:
     
    i) Payments into the trust fund, as specified in subsection (a)
    of this Section;
     
    ii) Updating of Schedule A of the trust agreement (as specified
    in Section 724.251) to show current post-closure cost
    estimates;
     
    iii) Annual valuations, as required by the trust agreement; and
     
    iv) Notices of nonpayment, as required by the trust agreement.
     
    4) The bond must guarantee that the owner or operator will do one of the
    following:
     
    A) Fund the standby trust fund in an amount equal to the penal sum of
    the bond before the beginning of final closure of the facility;
     
    B) Fund the standby trust fund in an amount equal to the penal sum
    within 15 days after an order to begin closure is issued by the
    Board or a U.S. district court or other court of competent
    jurisdiction; or
     
    C) Provide alternative financial assurance as specified in this Section,
    and obtain the Agency’s written approval of the assurance
    provided, within 90 days after receipt by both the owner or
    operator and the Agency of a notice of cancellation of the bond
    from the surety.
     
    5) Under the terms of the bond, the surety will become liable on the bond
    obligation when the owner or operator fails to perform as guaranteed by
    the bond.
     
    6) The penal sum of the bond must be in an amount at least equal to the
    current post-closure cost estimate, except as provided in subsection (g) of
    this Section.
     
    7) Whenever the current post-closure cost estimate increases to an amount
    greater than the penal sum, the owner or operator, within 60 days after the
    increase, must either cause the penal sum to be increased to an amount at
    least equal to the current post-closure cost estimate and submit evidence
    of such increase to the Agency or obtain other financial assurance, as
    specified in this Section, to cover the increase. Whenever the current
    post-closure cost estimate decreases, the penal sum may be reduced to the
    amount of the current post-closure cost estimate following written

     
    326
    approval by the Agency.
     
    8) Under the terms of the bond, the surety may cancel the bond by sending
    notice of cancellation by certified mail to the owner or operator and to the
    Agency. Cancellation may not occur, however, during the 120 days
    beginning on the date of receipt of the notice of cancellation by both the
    owner or operator and the Agency, as evidence by the return receipts.
     
    9) The owner or operator may cancel the bond if the Agency has given prior
    written consent based on its receipt of evidence of alternative financial
    assurance, as specified in this Section.
     
    c) Surety bond guaranteeing performance of post-closure care.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining a surety bond that conforms to the requirements of this
    subsection (c) and submitting the bond to the Agency. An owner or
    operator of a new facility must submit the bond to the Agency at least 60
    days before the date on which hazardous waste is first received for
    disposal. The bond must be effective before this initial receipt of
    hazardous waste. The surety company issuing the bond must, at a
    minimum, be among those listed as acceptable sureties on Federal federal
    bonds in Circular 570 of the U.S. Department of the Treasury.
     
    2) The wording of the surety bond must be that specified in Section 724.251.
     
    3) The owner or operator who uses a surety bond to satisfy the requirements
    of this Section must also establish a standby trust fund. Under the terms
    of the bond, all payments made thereunder will be deposited by the surety
    directly into the standby trust fund in accordance with instructions from
    the Agency. This standby trust must meet the requirements specified in
    subsection (a) of this Section, except as follows:
     
    A) An original, signed duplicate of the trust agreement must be
    submitted to the Agency with the surety bond; and
     
    B) Unless the standby trust fund is funded pursuant to the
    requirements of this Section, the following are not required:
     
    i) Payments into the trust fund, as specified in subsection (a)
    of this Section;
     
    ii) Updating of Schedule A of the trust agreement (as specified
    in Section 724.251) to show current post-closure cost
    estimates;
     

     
    327
    iii) Annual valuations, as required by the trust agreement; and
     
    iv) Notices of nonpayment, as required by the trust agreement.
     
    4) The bond must guarantee that the owner or operator will do either of the
    following:
     
    A) Perform final post-closure care in accordance with the post-closure
    plan and other requirements of the permit for the facility; or
     
    B) Provide alternative financial assurance, as specified in this Section,
    and obtain the Agency’s written approval of the assurance
    provided, within 90 days after receipt by both the owner or
    operator and the Agency of a notice of cancellation of the bond
    from the surety.
     
    5) Under the terms of the bond, the surety will become liable on the bond
    obligation when the owner or operator fails to perform as guaranteed by
    the bond. Following a final judicial determination or Board order finding
    that the owner or operator has failed to perform post-closure care in
    accordance with the approved post-closure plan and other permit
    requirements, under the terms of the bond the surety will perform post-
    closure care in accordance with post-closure plan and other permit
    requirements or will deposit the amount of the penal sum into the standby
    trust fund.
     
    6) The penal sum of the bond must be in an amount at least equal to the
    current post-closure cost estimate.
     
    7) Whenever the current post-closure cost estimate increases to an amount
    greater than the penal sum during the operating life of the facility, the
    owner or operator, within 60 days after the increase, must either cause the
    penal sum to be increased to an amount at least equal to the current post-
    closure cost estimate and submit evidence of such increase to the Agency,
    or obtain other financial assurance, as specified in this Section. Whenever
    the current closure cost estimate decreases during the operating life of the
    facility, the penal sum may be reduced to the amount of the current post-
    closure cost estimate following written approval by the Agency.
     
    8) During the period of post-closure care, the Agency must approve a
    decrease in the penal sum if the owner or operator demonstrates to the
    Agency that the amount exceeds the remaining cost of post-closure care.
     
    9) Under the terms of the bond, the surety may cancel the bond by sending
    notice of cancellation by certified mail to the owner or operator and to the
    Agency. Cancellation may not occur, however, during the 120 days

     
    328
    beginning on the date of receipt of the notice of cancellation by both the
    owner or operator and the Agency, as evidenced by the return receipts.
     
    10) The owner or operator may cancel the bond if the Agency has given prior
    written consent. The Agency must provide such written consent when
    either of the following occurs:
     
    A) An owner or operator substitutes alternative financial assurance as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (i) of this Section.
     
    11) The surety will not be liable for deficiencies in the performance of post-
    closure care by the owner or operator after the Agency releases the owner
    or operator from the requirements of this Section in accordance with
    subsection (i) of this Section.
     
    d) Post-closure letter of credit.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining an irrevocable standby letter of credit that conforms to the
    requirements of this subsection (d) and submitting the letter to the
    Agency. An owner or operator of a new facility must submit the letter of
    credit to the Agency at least 60 days before the date on which hazardous
    waste is first received for disposal. The letter of credit must be effective
    before this initial receipt of hazardous waste. The issuing institution must
    be an entity that has the authority to issue letters of credit and whose
    letter-of-credit operations are regulated and examined by a federal or State
    agency.
     
    2) The wording of the letter of credit must be that specified in Section
    724.251.
     
    3) An owner or operator who uses a letter of credit to satisfy the
    requirements of this Section must also establish a standby trust fund.
    Under the terms of the letter of credit, all amounts paid pursuant to a draft
    by the Agency must be deposited by the issuing institution directly into
    the standby trust fund in accordance with instructions from the Agency.
    This standby trust fund must meet the requirements of the trust fund
    specified in subsection (a) of this Section, except as follows:
     
    A) An original, signed duplicate of the trust agreement must be
    submitted to the Agency with the letter of credit; and
     
    B) Unless the standby trust fund is funded pursuant to the

     
    329
    requirements of this Section, the following are not required by
    these regulations:
     
    i) Payments into the trust fund, as specified in subsection (a)
    of this Section;
     
    ii) Updating of Schedule A of the trust agreement (as specified
    in Section 724.251) to show current post-closure cost
    estimates;
     
    iii) Annual valuations, as required by the trust agreement; and
     
    iv) Notices of nonpayment, as required by the trust agreement.
     
    4) The letter or credit must be accompanied by a letter from the owner or
    operator referring to the letter of credit by number, issuing institution, and
    date and providing the following information: the USEPA identification
    number, name and address of the facility, and the amount of funds assured
    for post-closure care of the facility by the letter of credit.
     
    5) The letter of credit must be irrevocable and issued for a period of at least
    one year. The letter of credit must provide that the expiration date will be
    automatically extended for a period of at least one year unless, at least 120
    days before the current expiration date, the issuing institution notifies both
    the owner or operator and the Agency by certified mail of a decision not to
    extend the expiration date. Under the terms of the letter of credit, the 120
    days will begin on the date when both the owner or operator and the
    Agency have received the notice, as evidenced by the return receipts.
     
    6) The letter of credit must be issued in an amount at least equal to the
    current post-closure cost estimate, except as provided in subsection (g) of
    this Section.
     
    7) Whenever the current post-closure cost estimate increases to an amount
    greater than the amount of the credit during the operating life of the
    facility, the owner or operator, within 60 days after the increase, must
    either cause the amount of the credit to be increased so that it at least
    equals the current post-closure cost estimate and submit evidence of such
    increase to the Agency, or obtain other financial assurance as specified in
    this Section to cover the increase. Whenever the current post-closure cost
    estimate decreases during the operating life of the facility, the amount of
    the credit may be reduced to the amount of the current post-closure cost
    estimate following written approval by the Agency.
     
    8) During the period of post-closure care, the Agency must approve a
    decrease in the amount of the letter of credit if the owner or operator

     
    330
    demonstrates to the Agency that the amount exceeds the remaining cost of
    post-closure care.
     
    9) Following a final judicial determination or Board order finding that the
    owner or operator has failed to perform post-closure care in accordance
    with the approved post-closure plan and other permit requirements, the
    Agency may draw on the letter of credit.
     
    10) If the owner or operator does not establish alternative financial assurance,
    as specified in this Section, and obtain written approval of such alternative
    assurance from the Agency within 90 days after receipt by both the owner
    or operator and the Agency of a notice from the issuing institution that it
    has decided not to extend the letter of credit beyond the current expiration
    date, the Agency must draw on the letter of credit. The Agency may delay
    the drawing if the issuing institution grants an extension of the term of the
    credit. During the last 30 days of any such extension the Agency must
    draw on the letter of credit if the owner or operator has failed to provide
    alternative financial assurance, as specified in this Section, and obtain
    written approval of such assurance from the Agency.
     
    11) The Agency must return the letter of credit to the issuing institution for
    termination when either of the following occurs:
     
    A) An owner or operator substitutes alternative financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (i) of this Section.
     
    e) Post-closure insurance.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining post-closure insurance that conforms to the requirements of this
    subsection (e) and submitting a certificate of such insurance to the
    Agency. An owner or operator of a new facility must submit the
    certificate of insurance to the Agency at least 60 days before the date on
    which hazardous waste is first received for disposal. The insurance must
    be effective before this initial receipt of hazardous waste. At a minimum,
    the insurer must be licensed to transact the business of insurance or be
    eligible to provide insurance as an excess or surplus lines insurer in one or
    more states.
     
    2) The wording of the certificate of insurance must be that specified in
    Section 724.251.
     
    3) The post-closure insurance policy must be issued for a face amount at

     
    331
    least equal to the current post-closure cost estimate, except as provided in
    subsection (g) of this Section. The term “face amount” means the total
    amount the insurer is obligated to pay under the policy. Actual payments
    by the insurer will not change the face amount, although the insurer’s
    future liability will be lowered by the amount of the payments.
     
    4) The post-closure insurance policy must guarantee that funds will be
    available to provide post-closure care of facility whenever the post-closure
    period begins. The policy must also guarantee that, once post-closure care
    begins, the insurer will be responsible for paying out funds, up to an
    amount equal to the face amount of the policy, upon the direction of the
    Agency to such party or parties as the Agency specifies.
     
    5) An owner or operator or any other person authorized to perform post-
    closure care may request reimbursement for post-closure care
    expenditures by submitting itemized bills to the Agency. Within 60 days
    after receiving bills for post-closure activities, the Agency must instruct
    the insurer to make reimbursement in such amounts as the Agency
    specifies in writing if the Agency determines that the post-closure care
    expenditures are in accordance with the approved post-closure plan or
    otherwise justified. If the Agency does not instruct the insurer to make
    such reimbursements, the Agency must provide the owner or operator with
    a detailed written statement of reasons.
     
    6) The owner or operator must maintain the policy in full force and effect
    until the Agency consents to termination of the policy by the owner or
    operator as specified in subsection (e)(11) of this Section. Failure to pay
    the premium, without substitution of alternative financial assurance as
    specified in this Section, will constitute a significant violation of these
    regulations, warranting such remedy as the Board may impose pursuant to
    the Environmental Protection Act [415 ILCS 5]. Such violation will be
    deemed to begin upon receipt by the Agency of a notice of future
    cancellation, termination, or failure to renew due to nonpayment of the
    premium, rather than upon the date of expiration.
     
    7) Each policy must contain a provision allowing assignment of the policy to
    a successor owner or operator. Such assignment may be conditional upon
    consent of the insurer, provided such consent is not unreasonably refused.
     
    8) The policy must provide that the insurer may not cancel, terminate, or fail
    to renew the policy except for failure to pay the premium. The automatic
    renewal of the policy must, at a minimum, provide the insured with the
    option of renewal at the face amount of the expiring policy. If there is a
    failure to pay the premium, the insurer may elect to cancel, terminate, or
    fail to renew the policy by sending notice by certified mail to the owner or
    operator and the Agency. Cancellation, termination, or failure to renew

     
    332
    may not occur, however, during the 120 days beginning with the date of
    receipt of the notice by both the Agency and the owner or operator, as
    evidenced by the return receipts. Cancellation, termination, or failure to
    renew may not occur, and the policy will remain in full force and effect, in
    the event that on or before the date of expiration one of the following
    occurs:
     
    A) The Agency deems the facility abandoned;
     
    B) The permit is terminated or revoked or a new permit is denied;
     
    C) Closure is ordered by the Board or a U.S. district court or other
    court of competent jurisdiction;
     
    D) The owner or operator is named as debtor in a voluntary or
    involuntary proceeding under Title 11 of the United States Code
    (Bankruptcy); or
     
    E) The premium due is paid.
     
    9) Whenever the current post-closure cost estimate increases to an amount
    greater than the face amount of the policy during the life of the facility, the
    owner or operator, within 60 days after the increase, must either cause the
    face amount to be increased to an amount at least equal to the current post-
    closure cost estimate and submit evidence of such increase to the Agency
    or obtain other financial assurance, as specified in this Section, to cover
    the increase. Whenever the current post-closure cost estimate decreases
    during the operating life of the facility, the face amount may be reduced to
    the amount of the current post-closure cost estimate following written
    approval by the Agency.
     
    10) Commencing on the date that liability to make payments pursuant to the
    policy accrues, the insurer must thereafter annually increase the face
    amount of the policy. Such increase must be equivalent to the face
    amount of the policy, less any payments made, multiplied by an amount
    equivalent to 85 percent of the most recent investment rate or of the
    equivalent coupon-issue yield announced by the U.S. Treasury for 26-
    week Treasury securities.
     
    11) The Agency must give written consent to the owner or operator that the
    owner or operator may terminate the insurance policy when either of the
    following occurs:
     
    A) An owner or operator substitutes alternative financial assurance, as
    specified in this Section; or
     

     
    333
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (i) of this Section.
     
    f) Financial test and corporate guarantee for post-closure care.
     
    1) An owner or operator may satisfy the requirements of this Section by
    demonstrating that it passes a financial test as specified in this subsection
    (f). To pass this test the owner or operator must meet the criteria of either
    subsection (f)(1)(A) or (f)(1)(B) of this Section:
     
    A) The owner or operator must have the following:
     
    i) Two of the following three ratios: a ratio of total liabilities
    to net worth less than 2.0; a ratio of the sum of net income
    plus depreciation, depletion and amortization to total
    liabilities greater than 0.1; and a ratio of current assets to
    current liabilities greater than 1.5;
     
    ii) Net working capital and tangible net worth each at least six
    times the sum of the current closure and post-closure cost
    estimates and the current plugging and abandonment cost
    estimates;
     
    iii) Tangible net worth of at least $10 million; and
     
    iv) Assets in the United States amounting to at least 90 percent
    of its total assets or at least six times the sum of the current
    closure and post-closure cost estimates and the current
    plugging and abandonment cost estimates.
     
    B) The owner or operator must have the following:
     
    i) A current rating for its most recent bond issuance of AAA,
    AA, A, or BBB as issued by Standard and Poor’s or Aaa,
    Aa, A, or Baa as issued by Moody’s;
     
    ii) Tangible net worth at least six times the sum of the current
    closure and post-closure cost estimates and current
    plugging and abandonment cost estimates;
     
    iii) Tangible net worth of at least $10 million; and
     
    iv) Assets located in the United States amounting to at least 90
    percent of its total assets or at least six times the sum of the
    current closure and post-closure cost estimates and the
    current plugging and abandonment cost estimates.

     
    334
     
    2) The phrase “current closure and post-closure cost estimates,” as used in
    subsection (f)(1) of this Section, refers to the cost estimates required to be
    shown in subsections 1 through 4 of the letter from the owner’s or
    operator’s chief financial officer (40 CFR 264.151(f), incorporated by
    reference in see Section 724.251). The phrase “current plugging and
    abandonment cost estimates,” as used in subsection (f)(1) of this Section,
    refers to the cost estimates required to be shown in subsections 1 through
    4 of the letter from the owner’s or operator’s chief financial officer (40
    CFR 144.70(f), incorporated by reference in see 35 Ill. Adm. Code
    704.240).
     
    3) To demonstrate that it meets this test, the owner or operator must submit
    the following items to the Agency:
     
    A) A letter signed by the owner’s or operator’s chief financial officer
    and worded, as specified in Section 724.251; and
     
    B) A copy of the independent certified public accountant’s report on
    examination of the owner’s or operator’s financial statements for
    the latest completed fiscal year; and
     
    C) A special report from the owner’s or operator’s independent
    certified public accountant to the owner or operator stating the
    following:
     
    i) The accountant has compared the data that the letter from
    the chief financial officer specifies as having been derived
    from the independently audited, year-end financial
    statements for the latest fiscal year with the amounts in
    such financial statements; and
     
    ii) In connection with that procedure, no matters came to the
    accountant’s attention that caused the accountant to believe
    that the specified data should be adjusted.
     
    4) An owner or operator of a new facility must submit the items specified in
    subsection (f)(3) of this Section to the Agency at least 60 days before the
    date on which hazardous waste is first received for disposal.
     
    5) After the initial submission of items specified in subsection (f)(3) of this
    Section, the owner or operator must send updated information to the
    Agency within 90 days after the close of each succeeding fiscal year. This
    information must consist of all three items specified in subsection (f)(3) of
    this Section.
     

     
    335
    6) If the owner or operator no longer meets the requirements of subsection
    (f)(1) of this Section, the owner or operator must send notice to the
    Agency of intent to establish alternative financial assurance, as specified
    in this Section. The notice must be sent by certified mail within 90 days
    after the end of the fiscal year for which the year-end financial data show
    that the owner or operator no longer meets the requirements the owner or
    operator must provide the alternative financial assurance within 120 days
    after the end of such fiscal year.
     
    7) Based on a reasonable belief that the owner or operator may no longer
    meet the requirements of subsection (f)(1) of this Section, the Agency may
    require reports of financial condition at any time from the owner or
    operator in addition to those specified in subsection (f)(3) of this Section.
    If the Agency finds, on the basis of such reports or other information, that
    the owner or operator no longer meets the requirements of subsection
    (f)(1) of this Section, the owner or operator must provide alternative
    financial assurance, as specified in this Section, within 30 days after
    notification of such a finding.
     
    8) The Agency may disallow use of this test on the basis of qualifications in
    the opinion expressed by the independent certified public accountant in
    the accountant’s report on examination of the owner’s or operator’s
    financial statements (see subsection (f)(3)(B) of this Section). An adverse
    opinion or a disclaimer of opinion will be cause for disallowance. The
    Agency must evaluate other qualifications on an individual basis. The
    owner or operator must provide alternative financial assurance, as
    specified in this Section, within 30 days after notification of the
    disallowance.
     
    9) During the period of post-closure care, the Agency must approve a
    decrease in the current post-closure cost estimate for which this test
    demonstrates financial assurance if the owner or operator demonstrates to
    the Agency that the amount of the cost estimate exceeds the remaining
    cost of post-closure care.
     
    10) The owner or operator is no longer required to submit the items specified
    in subsection (f)(3) of this Section when either of the following occurs:
     
    A) An owner or operator substitutes alternative financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (i) of this Section.
     
    11) An owner or operator may meet the requirements of this Section by
    obtaining a written guarantee, hereafter referred to as “corporate

     
    336
    guarantee.” The guarantor must be the direct or higher-tier parent
    corporation of the owner or operator, a firm whose parent corporation is
    also the parent corporation of the owner or operator, or a firm with a
    “substantial business relationship” with the owner or operator. The
    guarantor must meet the requirements for owners or operators in
    subsections (f)(1) through (f)(9), and must comply with the terms of the
    corporate guarantee. The wording of the corporate guarantee must be that
    specified in Section 724.251. A certified copy of the corporate guarantee
    must accompany the items sent to the Agency, as specified in subsection
    (f)(3) of this Section. One of these items must be the letter from the
    guarantor’s chief financial officer. If the guarantor’s parent corporation is
    also the parent corporation of the owner or operator, the letter must
    describe the value received in consideration of the guarantee. If the
    guarantor is a firm with a “substantial business relationship” with the
    owner or operator, this letter must describe this “substantial business
    relationship” and the value received in consideration of the guarantee.
    The terms of the corporate guarantee must provide as follows:
     
    A) That if the owner or operator fails to perform post-closure care of a
    facility covered by the corporate guarantee in accordance with the
    post-closure plan and other permit requirements whenever required
    to do so, the guarantor will do so or establish a trust fund as
    specified in subsection (a) of this Section in the name of the owner
    or operator.
     
    B) That the corporate guarantee will remain in force unless the
    guarantor sends notice of cancellation by certified mail to the
    owner or operator and to the Agency. Cancellation may not occur,
    however, during the 120 days beginning on the date of receipt of
    the notice of cancellation by both the owner or operator and the
    Agency, as evidenced by the return receipts.
     
    C) That if the owner or operator fails to provide alternative financial
    assurance as specified in this Section and obtain the written
    approval of such alternative assurance from the Agency within 90
    days after receipt by both the owner or operator and the Agency of
    a notice of cancellation of the corporate guarantee from the
    guarantor, the guarantor will provide such alternative financial
    assurance in the name of the owner or operator.
     
    g) Use of multiple financial mechanisms. An owner or operator may satisfy the
    requirements of this Section by establishing more than one financial mechanism
    per facility. These mechanisms are limited to trust funds, surety bonds
    guaranteeing payment into a trust fund, letters of credit and insurance. The
    mechanisms must be as specified in subsections (a), (b), (d), and (e) of this
    Section, respectively, except that it is the combination of mechanisms, rather than

     
    337
    the single mechanism, that must provide financial assurance for an amount at least
    equal to the current post-closure cost estimate. If an owner or operator uses a
    trust fund in combination with a surety bond or a letter of credit, it may use the
    trust fund as the standby trust fund for the other mechanisms. A single standby
    trust fund may be established for two or more mechanisms. The Agency may use
    any or all of the mechanisms to provide for post-closure care of the facility.
     
    h) Use of a financial mechanism for multiple facilities. An owner or operator may
    use a financial assurance mechanism specified in this Section to meet the
    requirements of this Section for more than one facility. Evidence of financial
    assurance submitted to the Agency must include a list showing, for each facility,
    the USEPA identification number, name, address, and the amount of funds for
    post-closure care assured by the mechanism. The amount of funds available
    through the mechanism must be no less than the sum of funds that would be
    available if a separate mechanism had been established and maintained for each
    facility. The amount of funds available to the Agency must be sufficient to close
    all of the owner or operator’s facilities. In directing funds available through the
    mechanism for post-closure care of any of the facilities covered by the
    mechanism, the Agency may direct only the amount of funds designated for that
    facility, unless the owner or operator agrees to the use of additional funds
    available under the mechanism.
     
    i) Release of the owner or operator from the requirements of this Section. Within
    60 days after receiving certifications from the owner or operator and an
    independent registered professional engineer that the post-closure care period has
    been completed for a hazardous waste disposal unit in accordance with the
    approved plan, the Agency must notify the owner or operator that it is no longer
    required to maintain financial assurance for post-closure care of that unit, unless
    the Agency determines that post-closure care has not been in accordance with the
    approved post-closure plan. The Agency must provide the owner or operator with
    a detailed written statement of any such determination that post-closure care has
    not been in accordance with the approved post-closure plan.
     
    j) Appeal. The following Agency actions are deemed to be permit modifications or
    refusals to modify for purposes of appeal to the Board (35 Ill. Adm. Code
    702.184(e)(3)):
     
    1) An increase in or a refusal to decrease the amount of a bond, letter of
    credit, or insurance;
     
    2) Requiring alternative assurance upon a finding that an owner or operator
    or parent corporation no longer meets a financial test.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    338
    Section 724.248 Incapacity of Owners or Operators, Guarantors, or Financial Institutions
     
    a) An owner or operator must notify the Agency by certified mail of the
    commencement of a voluntary or involuntary proceeding under Title 11 of the
    United States Code (Bankruptcy) naming the owners or operators as debtor, within
    10 days after commencement of the proceeding. A guarantor of a corporate
    guarantee, as specified in Sections 724.243(f) and 724.245(f), must make such a
    notification if he is named as a debtor, as required under the terms of the
    corporate guarantee (40 CFR 264.151(h), incorporated by reference in see Section
    724.251).
     
    b) An owner or operator who fulfills the requirements of Sections 724.243, 724.245,
    or 724.247 by obtaining a trust fund, surety bond, letter of credit, or insurance
    policy will be deemed to be without the required financial assurance or liability
    coverage in the event of bankruptcy of the trustee or issuing institution, or a
    suspension or revocation of the authority of the trustee institution to act as trustee
    or of the institution issuing the surety bond, letter of credit, or insurance policy to
    issue such instruments. The owner or operator must establish other financial
    assurance or liability coverage within 60 days after such an event.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.251 Wording of the Instruments
     
    The Agency must promulgate standardized forms based on 40 CFR 264.151 (Wording of the
    Instruments), incorporated by reference in 35 Ill. Adm. Code 720.111(b), with such changes in
    wording as are necessary under Illinois law. Any owner or operator required to establish
    financial assurance under this Subpart H must do so only upon the standardized forms
    promulgated by the Agency. The Agency must reject any financial assurance document that is
    not submitted on such standardized forms.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART I: USE AND MANAGEMENT OF CONTAINERS
     
    Section 724.273 Management of Containers
     
    a) A container holding hazardous waste must always be closed during storage,
    except when it is necessary to add or remove waste.
     
    b) A container holding hazardous waste must not be opened, handled, or stored in a
    manner that may rupture the container or cause it to leak.
     
    BOARD NOTE: Reuse of containers in transportation is governed by U.S. Department of
    Transportation USDOT regulations including those set forth in 49 CFR 173.28 (Reuse,
    Reconditioning, and Remanufacture of Packagings), incorporated by reference in 35 Ill. Adm.

     
    339
    Code 720.111(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.277 Special Requirements for Incompatible Wastes
     
    a) Incompatible wastes or incompatible wastes and materials (see Appendix E
    appendix V of this Part 40 CFR 265 (Examples of Potentially Incompatible
    Waste), incorporated by reference in 35 Ill. Adm. Code 720.111(b), for examples)
    must not be placed in the same container, unless Section 724.117(b) is complied
    with.
     
    b) Hazardous waste must not be placed in an unwashed container that previously
    held an incompatible waste or material.
     
    c) A storage container holding a hazardous waste that is incompatible with any
    waste or other materials stored nearby in other containers, piles, open tanks, or
    surface impoundments must be separated from the other materials or protected
    from them by means of a dike, berm, wall, or other device.
     
    BOARD NOTE: The purpose of this Section is to prevent fires, explosions, gaseous emission,
    leaching, or other discharge of hazardous waste or hazardous waste constituents that could result
    from the mixing of incompatible wastes or materials if containers break or leak. As required by
    Section 724.113, the waste analysis plan must include analyses needed to comply with Section
    724.277. Also Section 724.117(c) requires waste analyses, trial tests, or other documentation to
    assure compliance with Section 724.117(b). As required by Section 724.173, the owner or
    operator must place the results of each waste analysis and trial test, and any documented
    information, in the operating record of the facility.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART J: TANK SYSTEMS
     
    Section 724.290 Applicability
     
    The requirements of this Subpart J apply to owners and operators of facilities that use tank
    systems for storing or treating hazardous waste, except as otherwise provided in subsection (a),
    (b), or (c) of this Section or in Section 724.101.
     
    a) Tank systems that are used to store or treat hazardous waste that contains no free
    liquids and are situated inside a building with an impermeable floor are exempted
    from the requirements in Section 724.293. To demonstrate the absence or
    presence of free liquids in the stored or treated waste, the following test must be
    used: USEPA Method 9095 9095B (Paint Filter Liquids Test), as described in
    “Test Methods for Evaluating Solid Wastes Physical/Chemical Methods” USEPA
    Publication No. publication number EPA-530/SW-846), incorporated by

     
    340
    reference in 35 Ill. Adm. Code 720.111 720.111(a).
     
    b) Tank systems, including sumps, are defined in 35 Ill. Adm. Code 720.110, that
    serve as part of a secondary containment system to collect or contain releases of
    hazardous wastes are exempted from the requirements in Section 724.293(a).
     
    c) Tanks, sumps, and other such collection devices or systems used in conjunction
    with drip pads, as defined in 35 Ill. Adm. Code 720.110 and regulated under
    Subpart W of this Part, must meet the requirements of this Subpart J.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.291 Assessment of Existing Tank System Integrity
     
    a) For each existing tank system that does not have secondary containment meeting
    the requirements of Section 724.293, the owner or operator must determine either
    that the tank system is not leaking or that it is unfit for use. Except as provided in
    subsection (c) of this Section, the owner or operator must, by January 12, 1988,
    obtain and keep on file at the facility a written assessment reviewed and certified
    by an independent, qualified registered professional engineer, in accordance with
    35 Ill. Adm. Code 702.126(d), that attests to the tank system’s integrity.
     
    b) This assessment must determine whether the tank system is adequately designed
    and has sufficient structural strength and compatibility with the wastes to be
    stored or treated, to ensure that it will not collapse, rupture, or fail. At a
    minimum, this assessment must consider the following:
     
    1) Design standards, if available, according to which the tank and ancillary
    equipment were constructed;
     
    2) Hazardous characteristics of the wastes that have been and will be
    handled;
     
    3) Existing corrosion protection measures;
     
    4) Documented age of the tank system, if available (otherwise an estimate of
    the age); and
     
    5) Results of a leak test, internal inspection, or other tank integrity
    examination so that the following is true:
     
    A) For non-enterable underground tanks, the assessment must include
    a leak test that is capable of taking into account the effects of
    temperature variations, tank end deflection, vapor pockets, and
    high water table effects, and
     

     
    341
    B) For other than non-enterable underground tanks and for ancillary
    equipment, this assessment must include either a leak test, as
    described above, or other integrity examination that is certified by
    an independent, qualified registered professional engineer in
    accordance with 35 Ill. Adm. Code 702.126(d), that address
    cracks, leaks, corrosion, and erosion.
     
    BOARD NOTE: The practices described in the American Petroleum
    Institute (API) Publication, “Guide for Inspection of Refinery
    Equipment,” Chapter XIII, “Atmospheric and Low-Pressure Storage
    Tanks,” incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(a), may be used, where applicable, as guidelines in conducting
    other than a leak test.
     
    c) Tank systems that store or treat materials that become hazardous wastes
    subsequent to July 14, 1986, must conduct this assessment within 12 months after
    the date that the waste becomes a hazardous waste.
     
    d) If, as a result of the assessment conducted in accordance with subsection (a) of
    this Section, a tank system is found to be leaking or unfit for use, the owner or
    operator must comply with the requirements of Section 724.296.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.292 Design and Installation of New Tank Systems or Components
     
    a) Owners or operators of new tank systems or components must obtain and submit
    to the Agency, at time of submittal of Part B information, a written assessment,
    reviewed and certified by an independent, qualified registered professional
    engineer in accordance with 35 Ill. Adm. Code 702.126(d), attesting that the tank
    system has sufficient structural integrity and is acceptable for the storing and
    treating of hazardous waste. The assessment must show that the foundation,
    structural support, seams, connections, and pressure controls (if applicable) are
    adequately designed and that the tank system has sufficient structural strength,
    compatibility with the wastes to be stored or treated and corrosion protection to
    ensure that it will not collapse, rupture, or fail. This assessment, which will be
    used by the Agency to review and approve or disapprove the acceptability of the
    tank system design, must include, at a minimum, the following information:
     
    1) Design standards according to which tanks or the ancillary equipment are
    constructed;
     
    2) Hazardous characteristics of the wastes to be handled;
     
    3) For new tank systems or components in which the external shell of a metal
    tank or any external metal component of the tank system will be in contact

     
    342
    with the soil or with water, a determination by a corrosion expert of the
    following:
     
    A) Factors affecting the potential for corrosion, including but not
    limited to the following:
     
    i) Soil moisture content;
     
    ii) Soil pH;
     
    iii) Soil sulfide level;
     
    iv) Soil resistivity;
     
    v) Structure to soil potential;
     
    vi) Influence of nearby underground metal structures (e.g.,
    piping);
     
    vii) Existence of stray electric current;
     
    viii) Existing corrosion-protection measures (e.g., coating,
    cathodic protection, etc.); and
     
    B) The type and degree of external corrosion protection that are
    needed to ensure the integrity of the tank system during the use of
    the tank system or component, consisting of one or more of the
    following:
     
    i) Corrosion-resistant materials of construction, such as
    special alloys, fiberglass reinforced plastic, etc.;
     
    ii) Corrosion-resistant coating, such as epoxy, fiberglass, etc.,
    with cathodic protection (e.g., impressed current or
    sacrificial anodes); and
     
    iii) Electrical isolation devices, such as insulating joints,
    flanges, etc.
     
    BOARD NOTE: The practices described in the National
    Association of Corrosion Engineers (NACE) standard,
    “Recommended Practice (RP-02-85) “Control of External
    Corrosion on Metallic Buried, Partially Buried, or Submerged
    Liquid Storage Systems,” NACE Recommended Practice RP0285,
    and API Publication 1632, “Cathodic Protection of Underground
    Petroleum Storage Tanks and Piping Systems,” API

     
    343
    Recommended Practice 1632, each incorporated by reference in 35
    Ill. Adm. Code 720.111 720.111(a), may be used, where
    applicable, as guidelines in providing corrosion protection for tank
    systems.
     
    4) For underground tank system components that are likely to be adversely
    affected by vehicular traffic, a determination of design or operational
    measures that will protect the tank system against potential damage; and
     
    5) Design considerations to ensure the following:
     
    A) That tank foundations will maintain the load of a full tank;
     
    B) That tank systems will be anchored to prevent flotation or
    dislodgment where the tank system is placed in a saturated zone, or
    is located within a seismic fault zone subject to the standards of
    Section 724.118(a); and
     
    C) That tank systems will withstand the effects of frost heave.
     
    b) The owner or operator of a new tank system must ensure that proper handling
    procedures are adhered to in order to prevent damage to the system during
    installation. Prior to covering, enclosing or placing a new tank system or
    component in use, an independent qualified installation inspector or an
    independent, qualified registered professional engineer, either of whom is trained
    and experienced in the proper installation of tank systems or components, must
    inspect the system for the presence of any of the following items:
     
    1) Weld breaks;
     
    2) Punctures;
     
    3) Scrapes of protective coatings;
     
    4) Cracks;
     
    5) Corrosion;
     
    6) Other structural damage or inadequate construction or installation. All
    discrepancies must be remedied before the tank system is covered,
    enclosed, or placed in use.
     
    c) New tank systems or components that are placed underground and which are
    backfilled must be provided with a backfill material that is a noncorrosive,
    porous, and homogeneous substance which is installed so that the backfill is
    placed completely around the tank and compacted to ensure that the tank and

     
    344
    piping are fully and uniformly supported.
     
    d) All new tanks and ancillary equipment must be tested for tightness prior to being
    covered, enclosed or placed in use. If a tank system is found not to be tight, all
    repairs necessary to remedy the leaks in the system must be performed prior to the
    tank system being covered, enclosed, or placed into use.
     
    e) Ancillary equipment must be supported and protected against physical damage
    and excessive stress due to settlement, vibration, expansion, or contraction.
     
    BOARD NOTE: The piping system installation procedures described in API
    Publication 1615, “Installation of Underground Petroleum Storage Systems,” API
    Recommended Practice 1615;, or American National Standards Institute (ANSI)
    Standard B31.3, “Chemical Plant and Petroleum Refinery Piping”; ASME/ANSI
    Standard B31.3-1987, as supplemented by B31.3a-1988 and B31.3b-1988, and
    ANSI Standard B31.4 “Liquid Petroleum Transportation Piping Systems for
    Hydrocarbons, Liquid Petroleum Gas, Anhydrous Ammonia, and Alcohols,”
    ASME/ANSI Standard B31.4-1986, as supplemented by B31.4a-1987, each
    incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(a), may be used
    where applicable, as guidelines for proper installation of piping systems.
     
    f) The owner or operator must provide the type and degree of corrosion protection
    recommended by an independent corrosion expert, based on the information
    provided under subsection (a)(3) of this Section, or other corrosion protection if
    the Agency determines that other corrosion protection is necessary to ensure the
    integrity of the tank system during use of the tank system. The installation of a
    corrosion protection system that is field fabricated must be supervised by an
    independent corrosion expert to ensure proper installation.
     
    g) The owner or operator must obtain and keep on file at the facility written
    statements by those persons required to certify the design of the tank system and
    supervise the installation of the tank system in accordance with the requirements
    of subsections (b) through (f) of this Section, that attest that the tank system was
    properly designed and installed and that repairs, pursuant to subsections (b) and
    (d) of this Section, were performed. These written statements must also include
    the certification statement, as required in 35 Ill. Adm. Code 702.126(d).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.293 Containment and Detection of Releases
     
    a) In order to prevent the release of hazardous waste or hazardous constituents to the
    environment, secondary containment that meets the requirements of this Section
    must be provided (except as provided in subsections (f) and (g) of this Section).
     
    1) For a new tank system or component, prior to their being put into service;

     
    345
     
    2) For all existing tank systems used to store or treat Hazardous Waste
    Numbers F020, F021, F022, F023, F026, or F027, as defined in 35 Ill.
    Adm. Code 721.131, within two years after January 12, 1987;
     
    3) For those existing tank systems of known and documented age, within two
    years after January 12, 1987, or when the tank system has reached 15
    years of age, whichever comes later;
     
    4) For those existing tank systems for which the age cannot be documented,
    within eight years of January 12, 1987; but if the age of the facility is
    greater than seven years, secondary containment must be provided by the
    time the facility reaches 15 years of age, or within two years of January
    12, 1987, whichever comes later; and
     
    5) For tank systems that store or treat materials that become hazardous
    wastes subsequent to January 12, 1987, within the time intervals required
    in subsections (a)(1) through (a)(4) of this Section, except that the date
    that a material becomes a hazardous waste must be used in place of
    January 12, 1987.
     
    b) Secondary containment systems must fulfill the following:
     
    1) It must be designed, installed, and operated to prevent any migration of
    wastes or accumulated liquid out of the system to the soil, groundwater, or
    surface water at any time during the use of the tank system; and
     
    2) It must be capable of detecting and collecting releases and accumulated
    liquids until the collected material is removed.
     
    c) To meet the requirements of subsection (b) of this Section, secondary
    containment systems must, at a minimum, fulfill the following:
     
    1) It must be constructed of or lined with materials that are compatible with
    the wastes to be placed in the tank system and must have sufficient
    strength and thickness to prevent failure owing to pressure gradients
    (including static head and external hydrological forces), physical contact
    with the waste to which it is exposed, climatic conditions, and the stress of
    daily operation (including stresses from nearby vehicular traffic);
     
    2) It must be placed on a foundation or base capable of providing support to
    the secondary containment system, resistance to pressure gradients above
    and below the system, and capable of preventing failure due to settlement,
    compression or uplift;
     
    3) It must be provided with a leak-detection system that is designed and

     
    346
    operated so that it will detect the failure of either the primary or secondary
    containment structure or the presence of any release of hazardous waste or
    accumulated liquid in the secondary containment system within 24 hours,
    or at the earliest practicable time if the owner or operator demonstrates, by
    way of permit application, to the Agency that existing detection
    technologies or site conditions will not allow detection of a release within
    24 hours; and
     
    4) It must be sloped or otherwise designed or operated to drain and remove
    liquids resulting from leaks, spills, or precipitation. Spilled or leaked
    waste and accumulated precipitation must be removed from the secondary
    containment system within 24 hours, or in as timely a manner as is
    possible to prevent harm to human health and the environment, if the
    owner or operator demonstrates to the Agency, by way of permit
    application, that removal of the released waste or accumulated
    precipitation cannot be accomplished within 24 hours.
     
    BOARD NOTE: If the collected material is a hazardous waste under 35
    Ill. Adm. Code 721, it is subject to management as a hazardous waste in
    accordance with all applicable requirements of 35 Ill. Adm. Code 722
    through 725. If the collected material is discharged through a point source
    to waters of the State, it is subject to the NPDES permit requirement of
    Section 12(f) of the Environmental Protection Act and 35 Ill. Adm. Code
    309. If discharged to a Publicly Owned Treatment Work (POTW), it is
    subject to the requirements of 35 Ill. Adm. Code 307 and 310. If the
    collected material is released to the environment, it may be subject to the
    reporting requirements of 35 Ill. Adm. Code 750.410 and federal 40 CFR
    302.6.
     
    d) Secondary containment for tanks must include one or more of the following
    devices:
     
    1) A liner (external to the tank);
     
    2) A vault;
     
    3) A double-walled tank; or
     
    4) An equivalent device, as approved by the Board in an adjusted standards
    proceeding.
     
    e) In addition to the requirements of subsections (b), (c), and (d) of this Section,
    secondary containment systems must satisfy the following requirements:
     
    1) An external liner system must fulfill the following:
     

     
    347
    A) It must be designed or operated to contain 100 percent of the
    capacity of the largest tank within its boundary.
     
    B) It must be designed or operated to prevent run-on or infiltration of
    precipitation into the secondary containment system, unless the
    collection system has sufficient excess capacity to contain run-on
    or infiltration. Such additional capacity must be sufficient to
    contain precipitation from a 25-year, 24-hour rainfall event.
     
    C) It must be free of cracks or gaps; and
     
    D) It must be designed and installed to surround the tank completely
    and to cover all surrounding earth likely to come into contact with
    the waste if the waste is released from the tanks (i.e., it is capable
    of preventing lateral as well as vertical migration of the waste).
     
    2) A vault system must fulfill the following:
     
    A) It must be designed or operated to contain 100 percent of the
    capacity of the largest tank within the vault system’s boundary;
     
    B) It must be designed or operated to prevent run-on or infiltration of
    precipitation into the secondary containment system unless the
    collection system has sufficient excess capacity to contain run-on
    or infiltration. Such additional capacity must be sufficient to
    contain precipitation from a 25-year, 24-hour rainfall event;
     
    C) It must be constructed with chemical-resistant water stops in place
    at all joints (if any);
     
    D) It must be provided with an impermeable interior coating or lining
    that is compatible with the stored waste and that will prevent
    migration of waste into the concrete;
     
    E) It must be provided with a means to protect against the formation
    of and ignition of vapors within the vault, if the waste being stored
    or treated fulfills the following:
     
    i) It meets the definition of ignitable waste under 35 Ill. Adm.
    Code 721.121; or
     
    ii) It meets the definition of reactive waste under 35 Ill. Adm.
    Code 721.123, and may form an ignitable or explosive
    vapor;
     
    F) It must be provided with an exterior moisture barrier or be

     
    348
    otherwise designed or operated to prevent migration of moisture
    into the vault if the vault is subject to hydraulic pressure.
     
    3) A double-walled tank must fulfill the following:
     
    A) It must be designed as an integral structure (i.e., an inner tank
    completely enveloped within an outer shell) so that any release
    from the inner tank is contained by the outer shell;
     
    B) It must be protected, if constructed of metal, from both corrosion
    of the primary tank interior and of the external surface of the outer
    shell; and
     
    C) It must be provided with a built-in continuous leak detection
    system capable of detecting a release within 24 hours, or at the
    earliest practicable time, if the owner or operator demonstrates, by
    way of permit application, to the Agency that the existing
    detection technology or site conditions would not allow detection
    of a release within 24 hours.
     
    BOARD NOTE: The provisions outlined in the Steel Tank
    Institute’s Institute document (STI) “Standard for Dual Wall
    Underground Steel Storage Tanks,” incorporated by reference in
    35 Ill. Adm. Code 720.111 720.111(a), may be used as a guideline
    for aspects of the design of underground steel double-walled tanks.
     
    f) Ancillary equipment must be provided with secondary containment (e.g., trench,
    jacketing, double-walled piping, etc.) that meets the requirements of subsections
    (b) and (c) of this Section, except as follows:
     
    1) Aboveground piping (exclusive of flanges, joints, valves, and other
    connections) that are visually inspected for leaks on a daily basis;
     
    2) Welded flanges, welded joints, and welded connections that are visually
    inspected for leaks on a daily basis;
     
    3) Sealless or magnetic coupling pumps and sealless valves that are visually
    inspected for leaks on a daily basis; and
     
    4) Pressurized aboveground piping systems with automatic shut-off devices
    (e.g., excess flow check valves, flow metering shutdown devices, loss of
    pressure actuated shut-off devices, etc.) that are visually inspected for
    leaks on a daily basis.
     
    g) Pursuant to Section 28.1 of the Environmental Protection Act [415 ILCS 5/28.1],
    and in accordance with 35 Ill. Adm. Code 101 and 104, an adjusted standard will

     
    349
    be granted by the Board regarding alternative design and operating practices only
    if the Board finds either that the alternative design and operating practices,
    together with location characteristics, will prevent the migration of any hazardous
    waste or hazardous constituents into the groundwater or surface water at least as
    effectively as secondary containment during the active life of the tank system, or
    that in the event of a release that does migrate to groundwater or surface water, no
    substantial present or potential hazard will be posed to human health or the
    environment. New underground tank systems may not receive an adjusted
    standard from the secondary containment requirements of this Section through a
    justification in accordance with subsection (g)(2) of this Section.
     
    1) When determining whether to grant alternative design and operating
    practices based on a demonstration of equivalent protection of
    groundwater and surface water, the Board will consider whether the
    petitioner has justified an adjusted standard based on the following
    factors:
     
    A) The nature and quantity of the wastes;
     
    B) The proposed alternative design and operation;
     
    C) The hydrogeologic setting of the facility, including the thickness of
    soils present between the tank system and groundwater; and
     
    D) All other factors that would influence the quality and mobility of
    the hazardous constituents and the potential for them to migrate to
    groundwater or surface water.
     
    2) When determining whether to grant alternative design and operating
    practices based on a demonstration of no substantial present or potential
    hazard, the Board will consider whether the petitioner has justified an
    adjusted standard based on the following factors:
     
    A) The potential adverse effects on groundwater, surface water and
    land quality taking into account, considering the following:
     
    i) The physical and chemical characteristics of the waste in
    the tank system, including its potential for migration;
     
    ii) The hydrogeological characteristics of the facility and
    surrounding land;
     
    iii) The potential for health risk caused by human exposure to
    waste constituents;
     
    iv) The potential for damage to wildlife, crops, vegetation, and

     
    350
    physical structures caused by exposure to waste
    constituents; and
     
    v) The persistence and permanence of the potential adverse
    effects.
     
    B) The potential adverse effects of a release on groundwater quality,
    taking into account;
     
    i) The quantity and quality of groundwater and the direction
    of groundwater flow;
     
    ii) The proximity and withdrawal rates of groundwater users;
     
    iii) The current and future uses of groundwater in the area; and
     
    iv) The existing quality of groundwater, including other
    sources of contamination and their cumulative impact on
    the groundwater quality.
     
    C) The potential adverse effects of a release on surface water quality,
    taking the following into account:
     
    i) The quantity and quality of groundwater and the direction
    of groundwater flow;
     
    ii) The patterns of rainfall in the region;
     
    iii) The proximity of the tank system to surface waters;
     
    iv) The current and future uses of surface waters in the area
    and water quality standards established for those surface
    waters; and
     
    v) The existing quality of surface water, including other
    sources of contamination and the cumulative impact on
    surface water quality.
     
    D) The potential adverse effect of a release on the land surrounding
    the tank system, taking the following into account:
     
    i) The patterns of rainfall in the region; and
     
    ii) The current and future uses of the surrounding land.
     
    3) The owner or operator of a tank system, for which alternative design and

     
    351
    operating practices had been granted in accordance with the requirements
    of subsection (g)(1) of this Section, at which a release of hazardous waste
    has occurred from the primary tank system but which has not migrated
    beyond the zone of engineering control (as established in the alternative
    design and operating practices), must do the following:
     
    A) It must comply with the requirements of Section 724.296, except
    Section 724.296(d); and
     
    B) It must decontaminate or remove contaminated soil to the extent
    necessary to do the following:
     
    i) Enable the tank system for which the alternative design and
    operating practices were granted to resume operation with
    the capability for the detection of releases at least
    equivalent to the capability it had prior to the release; and
     
    ii) Prevent the migration of hazardous waste or hazardous
    constituents to groundwater or surface water; and
     
    C) If contaminated soil cannot be removed or decontaminated in
    accordance with subsection (g)(3)(B) of this Section, the owner or
    operator must comply with the requirement of Section 724.297(b).
     
    4) The owner or operator of a tank system, for which alternative design and
    operating practices had been granted in accordance with the requirements
    of subsection (g)(1) of this Section, at which a release of hazardous waste
    has occurred from the primary tank system and which has migrated
    beyond the zone of engineering control (as established in the alternative
    design and operating practices), must do the following:
     
    A) Comply with the requirements of Section 724.296(a), (b), (c), and
    (d); and
     
    B) Prevent the migration of hazardous waste or hazardous
    constituents to groundwater or surface water, if possible, and
    decontaminate or remove contaminated soil. If contaminated soil
    cannot be decontaminated or removed, or if groundwater has been
    contaminated, the owner or operator must comply with the
    requirements of Section 724.297(b); and
     
    C) If repairing, replacing or reinstalling the tank system, provide
    secondary containment in accordance with the requirements of
    subsections (a) through (f) of this Section, or make the alternative
    design and operating practices demonstration to the Board again,
    and meet the requirements for new tank systems in Section

     
    352
    724.292 if the tank system is replaced. The owner or operator
    must comply with these requirements even if contaminated soil is
    decontaminated or removed and groundwater or surface water has
    not been contaminated.
     
    h) In order to make an alternative design and operating practices, the owner or
    operator must follow the following procedures in addition to those specified in
    Section 28.1 of the Act [415 ILCS 5/28.1] and 35 Ill. Adm. Code 101 and 104:
     
    1) The owner or operator must file a petition for approval of alternative
    design and operating practices according to the following schedule:
     
    A) For existing tank systems, at least 24 months prior to the date that
    secondary containment must be provided in accordance with
    subsection (a) of this Section.
     
    B) For new tank systems, at least 30 days prior to entering into a
    contract for installation.
     
    2) As part of the petition, the owner or operator must also submit the
    following to the Board:
     
    A) A description of the steps necessary to conduct the demonstration
    and a timetable for completing each of the steps. The
    demonstration must address each of the factors listed in subsection
    (g)(1) or (g)(2) of this Section; and
     
    B) The portion of the Part B permit application specified in 35 Ill.
    Adm. Code 703.202.
     
    3) The owner or operator must complete its showing within 180 days after
    filing its petition for approval of alternative design and operating
    practices.
     
    4) The Agency must issue or modify the RCRA permit so as to require the
    permittee to construct and operate the tank system in the manner that was
    provided in any Board order approving alternative design and operating
    practices.
     
    i) All tank systems, until such time as secondary containment that meets the
    requirements of this Section is provided, must comply with the following:
     
    1) For non-enterable underground tanks, a leak test that meets the
    requirements of Section 724.291(b)(5) or other tank integrity methods, as
    approved or required by the Agency, must be conducted at least annually.
     

     
    353
    2) For other than non-enterable underground tanks, the owner or operator
    must do either of the following:
     
    A) Conduct a leak test, as in subsection (i)(1) of this Section, or
     
    B) Develop a schedule and procedure for an assessment of the overall
    condition of the tank system by an independent, qualified
    registered professional engineer. The schedule and procedure must
    be adequate to detect obvious cracks, leaks, and corrosion or
    erosion that may lead to cracks and leaks. The owner or operator
    must remove the stored waste from the tank, if necessary, to allow
    the condition of all internal tank surfaces to be assessed. The
    frequency of these assessments must be based on the material of
    construction of the tank and its ancillary equipment, the age of the
    system, the type of corrosion or erosion protection used, the rate of
    corrosion or erosion observed during the previous inspection and
    the characteristics of the waste being stored or treated.
     
    3) For ancillary equipment, a leak test or other integrity assessment, as
    approved by the Agency, must be conducted at least annually.
     
    BOARD NOTE: The practices described in the API Publication, “Guide
    for Inspection of Refinery Equipment,” Chapter XIII, “Atmospheric and
    Low-Pressure Storage Tanks,” incorporated by reference in 35 Ill. Adm.
    Code 720.111 720.111(a), may be used, where applicable, as a guideline
    for assessing the overall condition of the tank system.
     
    4) The owner or operator must maintain on file at the facility a record of the
    results of the assessments conducted in accordance with subsections (i)(1)
    through (i)(3) of this Section.
     
    5) If a tank system or component is found to be leaking or unfit for use as a
    result of the leak test or assessment in subsections (i)(1) through (1)(3) of
    this Section, the owner or operator must comply with the requirements of
    Section 724.296.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.295 Inspections
     
    a) The owner or operator must develop and follow a schedule and procedure for
    inspecting overfill controls.
     
    b) The owner or operator must inspect the following at least once each operating
    day:
     

     
    354
    1) Aboveground portions of the tank system, if any, to detect corrosion or
    releases of waste;
     
    2) Data gathered from monitoring and leak detection equipment (e.g.,
    pressure or temperature gauges, monitoring wells, etc.) to ensure that the
    tank system is being operated according to its design; and
     
    3) The construction materials and the area immediately surrounding the
    externally accessible portion of the tank system, including the secondary
    containment system (e.g., dikes) to detect erosion or signs of releases of
    hazardous waste (e.g., wet spots, dead vegetation, etc.).
     
    BOARD NOTE: Section 724.115(c) requires the owner or operator to remedy
    any deterioration or malfunction the owner or operator finds. Section 724.296
    requires the owner or operator to notify the Agency within 24 hours of confirming
    a leak. Also federal 40 CFR 302 302.6 may require the owner or operator to
    notify the National Response Center of a release.
     
    c) The owner or operator must inspect cathodic protection systems, if present,
    according to, at a minimum, the following schedule to ensure that they are
    functioning properly:
     
    1) The proper operation of the cathodic protection system must be confirmed
    within six months after initial installation and annually thereafter; and
     
    2) All sources of impressed current must be inspected or tested, as
    appropriate, at least bimonthly (i.e., every other month).
     
    BOARD NOTE: The practices described in the NACE Standard, RP-02-85,
    “Control of External Corrosion on Metallic Buried, Partially Buried, or
    Submerged Liquid Storage Systems,” NACE Recommended Practice, RP0285-
    85, and API Publication 1632, “Cathodic Protection of Underground Petroleum
    Storage Tanks and Piping Systems,” API Recommended Practice 1632, each
    incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(a), may be used,
    where applicable, as guidelines in maintaining and inspecting cathodic protection
    systems.
     
    d) The owner or operator must document in the operating record of the facility an
    inspection of those items in subsections (a) through (c) of this Section.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.296 Response to Leaks or Spills and Disposition of Leaking or Unfit-for-Use
    Tank Systems
     
    A tank system or secondary containment system from which there has been a leak or spill, or

     
    355
    which is unfit for use, must be removed from service immediately, and the owner or operator
    must satisfy the following requirements:
     
    a) Cease using; prevent flow or addition of wastes. The owner or operator must
    immediately stop the flow of hazardous waste into the tank system or secondary
    containment system and inspect the system to determine the cause of the release.
     
    b) Removal of waste from tank system or secondary containment system.
     
    1) If the release was from the tank system, the owner or operator must,
    within 24 hours after detection of the leak or as otherwise provided in the
    permit, remove as much of the waste as is necessary to prevent further
    release of hazardous waste to the environment and to allow inspection and
    repair of the tank system to be performed.
     
    2) If the material released was to a secondary containment system, all
    released materials must be removed within 24 hours or as otherwise
    provided in the permit to prevent harm to human health and the
    environment.
     
    c) Containment of visible releases to the environment. The owner or operator must
    immediately conduct a visual inspection of the release and, based upon that
    inspection, do the following:
     
    1) Prevent further migration of the leak or spill to soils or surface water; and
     
    2) Remove and properly dispose of any visible contamination of the soil or
    surface water.
     
    d) Notifications, reports.
     
    1) Any release to the environment, except as provided in subsection (d)(2) of
    this Section, must be reported to the Agency within 24 hours of its
    detection.
     
    2) A leak or spill of hazardous waste is exempted from the requirements of
    this subsection (d) if the following is true:
     
    A) The spill was less than or equal to a quantity of one pound; and
     
    B) It was immediately contained and cleaned up.
     
    3) Within 30 days of detection of a release to the environment, a report
    containing the following information must be submitted to the Agency:
     
    A) Likely route of migration of the release;

     
    356
     
    B) Characteristics of the surrounding soil (soil composition, geology,
    hydrogeology, climate, etc.);
     
    C) Results of any monitoring or sampling conducted in connection
    with the release (if available). If sampling or monitoring data
    relating to the release are not available within 30 days, these data
    must be submitted to the Agency as soon as they become available.
     
    D) Proximity the downgradient drinking water, surface water, and
    populated areas; and
     
    E) Description of response actions taken or planned.
     
    e) Provision of secondary containment, repair, or closure.
     
    1) Unless the owner or operator satisfies the requirements of subsections
    (e)(2) through (e)(4) of this Section, the tank system must be closed in
    accordance with Section 724.297.
     
    2) If the cause of the release was a spill that has not damaged the integrity of
    the system, the owner or operator may return the system to service as soon
    as the released waste is removed and repairs, if necessary, are made.
     
    3) If the cause of the release was a leak from the primary tank system into the
    secondary containment system, the system must be repaired prior to
    returning the tank system to service.
     
    4) If the source of the release was a leak to the environment from a
    component of a tank system without secondary containment, the owner or
    operator must provide the component of the system from which the leak
    occurred with secondary containment that satisfies the requirements of
    Section 724.293 before it can be returned to service, unless the source of
    the leak is an aboveground portion of a tank system that can be inspected
    visually. If the source is an aboveground component that can be inspected
    visually, the component must be repaired and may be returned to service
    without secondary containment, as long as the requirements of subsection
    (f) of this Section are satisfied. If a component is replaced to comply with
    the requirements of this subsection (e), that component must satisfy the
    requirements of new tank systems or components in Sections 724.292 and
    724.293. Additionally, if a leak has occurred in any portion of a tank
    system component that is not readily accessible for visual inspection (e.g.,
    the bottom of an in-ground or on-ground tank), the entire component must
    be provided with secondary containment in accordance with Section
    724.293 prior to being returned to use.
     

     
    357
    f) Certification of major repairs. If the owner or operator has repaired a tank system
    in accordance with subsection (e) of this Section, and the repair has been
    extensive (e.g., installation of an internal liner, repair, or a ruptured primary
    containment or secondary containment vessel), the tank system must not be
    returned to service unless the owner or operator has obtained a certification by an
    independent, qualified registered professional engineer, in accordance with 35 Ill.
    Adm. Code 702.126(d), that the repaired system is capable of handling hazardous
    wastes without release for the intended life of the system. This certification must
    be submitted to the Agency within seven days after returning the tank system to
    use.
     
    BOARD NOTE: See Section 724.115(c) for the requirements necessary to remedy a failure.
    Also, federal 40 CFR 302.6, incorporated by reference in 35 Ill. Adm. Code 720.111, may
    require the owner or operator to notify the National Response Center of certain releases. any
    “reportable quantity.”
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.298 Special Requirements for Ignitable or Reactive Waste
     
    a) Ignitable or reactive waste must not be placed in tank systems unless the
    following is true:
     
    1) The waste is treated, rendered, or mixed before or immediately after
    placement in the tank system so that the following is true:
     
    A) The resulting waste, mixture, or dissolved material no longer meets
    the definition of ignitable or reactive waste under 35 Ill. Adm.
    Code 721.121 or 721.123; and
     
    B) Section 724.117(b) is complied with; or
     
    2) The waste is stored or treated in such a way that it is protected from any
    material or conditions that may cause the waste to ignite or react; or
     
    3) The tank is used solely for emergencies.
     
    b) The owner or operator of a facility where ignitable or reactive waste is stored or
    treated in a tank must comply with the requirements for the maintenance of
    protective distances between the waste management area and any public ways,
    streets, alleys, or an adjoining property line that can be built upon, as required in
    tables 2-1 through 2-6 of the National Fire Protection Association’s “Flammable
    and Combustible Liquids Code,” NFPA 30, incorporated by reference in 35 Ill.
    Adm. Code 720.111 720.111(a)).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)

     
    358
     
    SUBPART N: LANDFILLS
     
    Section 724.414 Special Requirements for Bulk and Containerized Liquids
     
    a) This subsection (a) corresponds with 40 CFR 264.314(a), which pertains to pre
    May 8, 1985 actions, a date long since passed. This statement maintains
    structural consistency with USEPA rules.
     
    b) The placement of bulk or non-containerized liquid hazardous waste or hazardous
    waste containing free liquids (whether or not sorbents have been added) in any
    landfill is prohibited.
     
    c) To demonstrate the absence or presence of free liquids in either a containerized or
    a bulk waste, the following test must be used: Method 9095 9095B (Paint Filter
    Liquids Test), as described in “Test Methods for Evaluating Solid Wastes,
    Physical/Chemical Methods,” USEPA Publication No. publication number EPA-
    530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(a).
     
    d) Containers holding free liquids must not be placed in a landfill unless the
    following is true:
     
    1) All free-standing liquid fulfills one of the following:
     
    A) It has been removed by decanting or other methods;
     
    B) It has been mixed with sorbent or solidified so that free-standing
    liquid is no longer observed; or
     
    C) It has been otherwise eliminated; or
     
    2) The container is very small, such as an ampule; or
     
    3) The container is designed to hold free liquids for use other than storage,
    such as a battery or capacitor; or
     
    4) The container is a lab pack as defined in Section 724.416 and is disposed
    of in accordance with Section 724.416.
     
    e) Sorbents used to treat free liquids to be disposed of in landfills must be
    nonbiodegradable. Nonbiodegradable sorbents are the following: materials listed
    or described in subsection (e)(1) of this Section; materials that pass one of the
    tests in subsection (e)(2) of this Section; or materials that are determined by the
    Board to be nonbiodegradable through the adjusted standard procedure of 35 Ill.
    Adm. Code 104.
     

     
    359
    1) Nonbiodegradable sorbents are the following:
     
    A) Inorganic minerals, other inorganic materials, and elemental
    carbon (e.g., aluminosilicates (clays, smectites, Fuller’s earth,
    bentonite, calcium bentonite, montmorillonite, calcined
    montmorillonite, kaolinite, micas (illite), vermiculites, zeolites,
    etc.), calcium carbonate (organic free limestone),
    oxides/hydroxides (alumina, lime, silica (sand), diatomaceous
    earth, etc.), perlite (volcanic glass), expanded volcanic rock,
    volcanic ash, cement kiln dust, fly ash, rice hull ash, activated
    charcoal (activated carbon), etc.); or
     
    B) High molecular weight synthetic polymers (e.g., polyethylene,
    high density polyethylene (HDPE), polypropylene, polystrene,
    polyurethane, polyacrylate, polynorborene, polyisobutylene,
    ground synthetic rubber, cross-linked allylstrene and tertiary butyl
    copolymers, etc.). This does not include polymers derived from
    biological material or polymers specifically designed to be
    degradable; or
     
    C) Mixtures of these nonbiodegradable materials.
     
    2) Tests for nonbiodegradable sorbents are the following:
     
    A) The sorbent material is determined to be nonbiodegradable under
    ASTM Method G21-70 (1984a)--“ (Standard Practice for
    Determining Resistance of Synthetic Polymer Materials to
    Fungi),” incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(a);
     
    B) The sorbent material is determined to be nonbiodegradable under
    ASTM Method G22-76 (1984b)--“ (Standard Practice for
    Determining Resistance of Plastics to Bacteria),” incorporated by
    reference in 35 Ill. Adm. Code 720.111 720.111(a); or
     
    C) The sorbent material is determined to be non-biodegradable under
    OECD test Guideline for Testing of Chemicals, Method 301B
    (CO2 Evolution (Modified Sturm Test)), incorporated by reference
    in 35 Ill. Adm. Code 720.111 720.111(a).
     
    f) The placement of any liquid that is not a hazardous waste in a hazardous waste
    landfill is prohibited (35 Ill. Adm. Code 729.311), unless the Board finds that the
    owner or operator has demonstrated the following in a petition for an adjusted
    standard pursuant to Section 28.1 of the Act [415 ILCS 5/28.1] and 35 Ill. Adm.
    Code 101 and 104:
     

     
    360
    1) The only reasonably available alternative to the placement in a hazardous
    waste landfill is placement in a landfill or unlined surface impoundment,
    whether or not permitted or operating under interim status, that contains or
    which may reasonably be anticipated to contain hazardous waste; and
     
    2) Placement in the hazardous waste landfill will not present a risk of
    contamination of any underground source of drinking water (as that term
    is defined in 35 Ill. Adm. Code 702.110).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.416 Disposal of Small Containers of Hazardous Waste in Overpacked Drums
    (Lab Packs)
     
    Small containers of hazardous waste in overpacked drums (lab packs) may be placed in a landfill
    if the following requirements are met:
     
    a) Hazardous waste must be packaged in non-leaking inside containers. The inside
    containers must be of a design and constructed of a material that will not react
    dangerously with, be decomposed by, or be ignited by the contained waste. The
    inside containers must be tightly and securely sealed. The inside containers must
    be of the size and type specified in the Department of Transportation (DOT)
    USDOT hazardous materials regulations (49 CFR 173 (Shippers--General
    Requirements for Shipments and Packages), 178 (Specifications for Packagings),
    and 179 (Specifications for Tank Cars), each incorporated by reference in 35 Ill.
    Adm. Code 720.111(b)), if those regulations specify a particular inside container
    for the waste.
     
    b) The inside containers must be overpacked in an open head DOT-specification
    USDOT-specification metal shipping container (49 CFR 178 (Specifications for
    Packagings) and 179 (Specifications for Tank Cars)) of no more than 416 liter
    (110 gallon) capacity and surrounded by, at a minimum, a sufficient quantity of
    sorbent material, determined to be nonbiodegradable in accordance with Section
    724.414(e), to completely sorb all of the liquid contents of the inside containers.
    The metal outer container must be full after packing with inside containers and
    sorbent material.
     
    c) In accordance with Section 724.117(b), the sorbent material used must not be
    capable of reacting dangerously with, being decomposed by, or being ignited by
    the contents of the inside containers, in accordance with Section 724.117(b).
     
    d) Incompatible waste, as defined in 35 Ill. Adm. Code 720.110, must not be placed
    in the same outside container.
     
    e) Reactive wastes, other than cyanide- or sulfide-bearing waste as defined in 35 Ill.
    Adm. Code 721.123(a)(5), must be treated or rendered non-reactive prior to

     
    361
    packaging in accordance with subsections (a) through (d) of this Section.
    Cyanide- and sulfide-bearing reactive waste may be packed in accordance with
    subsections (a) through (d) of this Section without first being treated or rendered
    non-reactive.
     
    f) Such disposal is in compliance with 35 Ill. Adm. Code 728. Persons who
    incinerate lab packs according to 35 Ill. Adm. Code 728.142(c)(1) may use fiber
    drums in place of metal outer containers. Such fiber drums must meet the DOT
    USDOT specifications in 49 CFR 173.12 (Exceptions for Shipments of Waste
    Materials), incorporated by reference in 35 Ill. Adm. Code 720.111(b), and be
    overpacked according to the requirements of subsection (b) of this Section.
     
    g) Pursuant to 35 Ill. Adm. Code 729.312, the use of labpacks for disposal of liquid
    wastes or wastes containing free liquids allowed under this Section is restricted to
    labwaste and non-periodic waste, as those terms are defined in that Part.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART O: INCINERATORS
     
    Section 724.440 Applicability
     
    a) The regulations in this Subpart O apply to owners and operators of hazardous
    waste incinerators (as defined in 35 Ill. Adm. Code 720.110), except as Section
    724.101 provides otherwise.
     
    b) Integration of the MACT standards.
     
    1) Except as provided by subsections (b)(2), (b)(3), and (b)(4) of this
    Section, the standards of this Part no longer apply when an owner or
    operator demonstrates compliance with the maximum achievable control
    technology (MACT) requirements of subpart EEE of 40 CFR 63, Subpart
    EEE (National Emission Standards for Hazardous Air Pollutants from
    Hazardous Waste Combustors), incorporated by reference in 35 Ill. Adm.
    Code 720.111 720.111(b), by conducting a comprehensive performance
    test and submitting to the Agency a Notification of Compliance, under 40
    CFR 63.1207(j) and 63.1210(b), documenting compliance with the
    requirements of subpart EEE of 40 CFR 63, subpart EEE. Nevertheless,
    even after this demonstration of compliance with the MACT standards,
    RCRA permit conditions that were based on the standards of this Part will
    continue to be in effect until they are removed from the permit or the
    permit is terminated or revoked, unless the permit expressly provides
    otherwise.
     
    2) The MACT standards of subpart EEE of 40 CFR 63, subpart EEE do not
    replace the closure requirements of Section 724.451 or the applicable

     
    362
    requirements of Subparts A through H, BB, and CC of this Part.
     
    3) The particulate matter standard of Section 724.443(c) remains in effect for
    incinerators that elect to comply with the alternative to the particulate
    matter standard of 40 CFR 63.1206(b)(14) (When and How Must You
    Comply with the Standards and Operating Requirements?), incorporated
    by reference in 35 Ill. Adm. Code 720.111 720.111(b).
     
    4) The following requirements remain in effect for startup, shutdown, and
    malfunction events if the owner or operator elects to comply with 35 Ill.
    Adm. Code 703.320(a)(1)(A) to minimize emissions of toxic compounds
    from the following events:
     
    A) Section 724.445(a), requiring that an incinerator operate in
    accordance with operating requirements specified in the permit;
    and
     
    B) Section 724.445(c), requiring compliance with the emission
    standards and operating requirements during startup and shutdown
    if hazardous waste is in the combustion chamber, except for
    particular hazardous wastes.
     
    BOARD NOTE: Sections 9.1 and 39.5 of the Environmental Protection Act [415
    ILCS 5/9.1 and 39.5] make the federal MACT standards directly applicable to
    entities in Illinois and authorize the Agency to issue permits based on the federal
    standards. Operating conditions used to determine effective treatment of
    hazardous waste remain effective after the owner or operator demonstrates
    compliance with the standards of subpart EEE of 40 CFR 63, subpart EEE. In
    adopting this subsection (b), USEPA stated as follows (at 64 Fed Reg. 52828,
    52975 (September 30,1999)):
     
    Under this approach . . . , MACT air emissions and related
    operating requirements are to be included in Title V permits;
    RCRA permits will continue to be required for all other aspects of
    the combustion unit and the facility that are governed by RCRA
    (e.g., corrective action, general facility standards, other
    combustor-specific concerns such as materials handling, risk-based
    emissions limits and operating requirements, as appropriate, and
    other hazardous waste management units).
     
    c) After consideration of the waste analysis included with Part B of the permit
    application, the Agency, in establishing the permit conditions, must exempt the
    applicant from all requirements of this Subpart O, except Section 724.441 (Waste
    Analysis) and Section 724.451 (Closure):
     
    1) If the Agency finds that the waste to be burned is one of the following:

     
    363
     
    A) It is listed as a hazardous waste in Subpart D of 35 Ill. Adm. Code
    721 solely because it is ignitable (Hazard Code I), corrosive
    (Hazard Code C), or both;
     
    B) It is listed as a hazardous waste in Subpart D of 35 Ill. Adm. Code
    721 solely because it is reactive (Hazard Code R) for
    characteristics other than those listed in Section 721.123(a)(4) and
    (5), and will not be burned when other hazardous wastes are
    present in the combustion zone;
     
    C) It is a hazardous waste solely because it possesses the
    characteristic of ignitability, as determined by the test for
    characteristics of hazardous wastes under Subpart C of 35 Ill.
    Adm. Code 721; or
     
    D) It is a hazardous waste solely because it possesses any of the
    reactivity characteristics described by 35 Ill. Adm. Code
    721.123(a)(1), (a)(2), (a)(3), (a)(6), (a)(7), and (a)(8) and will not
    be burned when other hazardous wastes are present in the
    combustion zone; and
     
    2) If the waste analysis shows that the waste contains none of the hazardous
    constituents listed in Subpart H of 35 Ill. Adm. Code 721 that would
    reasonably be expected to be in the waste.
     
    d) If the waste to be burned is one that is described by subsection (b)(1)(A),
    (b)(1)(B), (b)(1)(C), or (b)(1)(D) of this Section and contains insignificant
    concentrations of the hazardous constituents listed in Subpart H of 35 Ill. Adm.
    Code 721, then the Agency may, in establishing permit conditions, exempt the
    applicant from all requirements of this Subpart O, except Section 724.441 (Waste
    Analysis) and Section 724.451 (Closure), after consideration of the waste analysis
    included with Part B of the permit application, unless the Agency finds that the
    waste will pose a threat to human health or the environment when burned in an
    incinerator.
     
    e) The owner or operator of an incinerator may conduct trial burns subject only to
    the requirements of 35 Ill. Adm. Code 703.222 through 703.225 (short-term and
    incinerator permits).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.442 Principal Organic Hazardous Constituents (POHCs)
     
    a) Principal organic hazardous constituents (POHCs) in the waste feed must be
    treated to the extent required by the performance standard of Section 724.443.

     
    364
     
    b) Designation of POHCs.
     
    1) One or more POHCs will be specified in the facility’s permit, from among
    those constituents listed in Appendix H to 35 Ill. Adm. Code 721,
    Appendix H, for each waste feed to be burned. This specification will be
    based on the degree of difficulty of incineration of the organic constituents
    in the waste and on their concentration or mass in the waste feed,
    considering the results of waste analyses and trial burns or alternative data
    submitted with Part B of the facility’s permit application. Organic
    constituents that represent the greatest degree of difficulty of incineration
    will be those most likely to be designated as POHCs. Constituents are
    more likely to be designated as POHCs if they are present in large
    quantities or concentrations in the waste.
     
    2) Trial POHCs will be designated for performance of trial burns in
    accordance with the procedure specified in 35 Ill. Adm. Code 703.222
    through 703.225 for obtaining trial burn permits.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.443 Performance Standards
     
    An incinerator burning hazardous waste must be designed, constructed, and maintained so that,
    when operated in accordance with operating requirements specified under Section 724.445, it
    will meet the following performance standards:
     
    a) Destruction and removal efficiency.
     
    1) Except as provided in subsection (a)(2) of this Section, an incinerator
    burning hazardous waste must achieve a destruction and removal
    efficiency (DRE) of 99.99% for each principal organic hazardous
    constituent (POHC) designated (under Section 724.442) in its permit for
    each waste feed. DRE is determined for each POHC from the following
    equation:
     
    (
    )
    N
    O
    N
    100
    DRE
    ×
    =
      
     
    Where:
     
    N = Mass feed rate of one principal organic hazardous
    constituent (POHC) in the waste stream feeding the
    incinerator, and
     
    O = Mass emission rate of the same POHC present in

     
    365
    exhaust emissions prior to release to the
    atmosphere.
     
    2) An incinerator burning hazardous wastes F020, F021, F022, F023, F026,
    or F027 must achieve a destruction and removal efficiency (DRE) of
    99.9999% for each principal organic hazardous constituent (POHC)
    designated (under Section 724.442) in its permit. This performance must
    be demonstrated on POHCs that are more difficult to incinerate than tetra-,
    penta-, and hexachlorodibenzo-p-dioxins and dibenzofurans. DRE is
    determined for each POHC from the equation in subsection (a)(1) of this
    Section. In addition, the owner or operator of the incinerator must notify
    the Agency of its intent to incinerate hazardous wastes F020, F021, F022,
    F023, F026, or F027.
     
    b) An incinerator burning hazardous waste and producing stack emissions of more
    than 1.8 kilograms per hour (4 pounds per hour) of hydrogen chloride (HCl) must
    control HCl emissions such that the rate of emission is no greater than the larger
    of either 1.8 kilograms per hour or one percent of the HCl in the stack gas prior to
    entering any pollution control equipment.
     
    c) An incinerator burning hazardous waste must not emit particulate matter in excess
    of 180 milligrams per dry standard cubic meter (0.08 grains per dry standard
    cubic foot) when corrected for the amount of oxygen in the stack gas according to
    the following formula:
     
    Y
    21
    M
    14
    C
    ×
    =
      
     
    1) Where:
     
    C = the corrected concentration of particulate matter,
     
    M = the measured concentration of particulate matter, and
     
    Y = the measured concentration of oxygen in the stack gas, using the
    Orsat method for oxygen analysis of dry flue gas, presented in
    Method 3 in appendix A to 40 CFR 60, Appendix A (Method 3)
    (Gas Analysis for the Determination of Dry Molecular Weight),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    2) This correction procedure is to be used by all hazardous waste incinerators
    except those operating under conditions of oxygen enrichment. For these
    facilities, The Agency must select an appropriate correction procedure, to
    be specified in the facility permit.
     
    d) For the purposes of permit enforcement, compliance with the operating

     
    366
    requirements specified in the permit (under Section 724.445) will be regarded as
    compliance with this Section. However, evidence that compliance with those
    permit conditions is insufficient to ensure compliance with the performance
    requirements of this Section may be “information” justifying modification,
    revocation or reissuance of a permit under 35 Ill. Adm. Code 702.184.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART S: SPECIAL PROVISIONS FOR CLEANUP
     
    Section 724.652 Corrective Action Management Units
     
    a) To implement remedies under Section 724.201 or RCRA section 3008(h), or to
    implement remedies at a permitted facility that is not subject to Section 724.201,
    the Agency may designate an area at the facility as a corrective action
    management unit under the requirements in this Section. “Corrective action
    management unit” or “CAMU” means an area within a facility that is used only
    for managing CAMU-eligible wastes for implementing corrective action or
    cleanup at that facility. A CAMU must be located within the contiguous property
    under the control of the owner or operator where the wastes to be managed in the
    CAMU originated. One or more CAMUs may be designated at a facility.
     
    1) “CAMU-eligible waste” means the following:
     
    A) All solid and hazardous wastes, and all media (including
    groundwater, surface water, soils, and sediments) and debris, that
    are managed for implementing cleanup. As-generated wastes
    (either hazardous or non-hazardous) from ongoing industrial
    operations at a site are not CAMU-eligible wastes.
     
    B) Wastes that would otherwise meet the description in subsection
    (a)(1)(A) of this Section are not CAMU-eligible waste where the
    following is true:
     
    i) The wastes are hazardous waste found during cleanup in
    intact or substantially intact containers, tanks, or other non-
    land-based units found above ground, unless the wastes are
    first placed in the tanks, containers, or non-land-based units
    as part of cleanup, or the containers or tanks are excavated
    during the course of cleanup; or
     
    ii) The Agency makes the determination in subsection (a)(2)
    of this Section to prohibit the wastes from management in a
    CAMU.
     
    C) Notwithstanding subsection (a)(1)(A) of this Section, where

     
    367
    appropriate, as-generated non-hazardous waste may be placed in a
    CAMU where such waste is being used to facilitate treatment or
    the performance of the CAMU.
     
    2) The Agency must prohibit the placement of waste in a CAMU where the
    Agency determines that the wastes have not been managed in compliance
    with applicable land disposal treatment standards of 35 Ill. Adm. Code
    728, applicable unit design requirements of this Part or 35 Ill. Adm. Code
    725, or other applicable requirements of this Subtitle G, and that the non-
    compliance likely contributed to the release of the waste.
     
    3) Prohibition against placing liquids in a CAMU.
     
    A) The placement of bulk or noncontainerized liquid hazardous waste
    or free liquids contained in hazardous waste (whether or not
    sorbents have been added) in any CAMU is prohibited except
    where placement of such wastes facilitates the remedy selected for
    the waste.
     
    B) The requirements in Section 724.414(d) for placement of
    containers holding free liquids in landfills apply to placement in a
    CAMU, except where placement facilitates the remedy selected for
    the waste.
     
    C) The placement of any liquid that is not a hazardous waste in a
    CAMU is prohibited unless such placement facilitates the remedy
    selected for the waste or a demonstration is made pursuant to
    Section 724.414(f).
     
    D) The absence or presence of free liquids in either a containerized or
    a bulk waste must be determined in accordance with Section
    724.414(c). Sorbents used to treat free liquids in a CAMU must
    meet the requirements of Section 724.414(e).
     
    4) Placement of CAMU-eligible wastes into or within a CAMU does not
    constitute land disposal of hazardous waste.
     
    5) Consolidation or placement of CAMU-eligible wastes into or within a
    CAMU does not constitute creation of a unit subject to minimum
    technology requirements.
     
    b) Establishing a CAMU.
     
    1) The Agency must designate a regulated unit (as defined in Section
    724.190(a)(2)) as a CAMU or must incorporate a regulated unit into a
    CAMU, if it determines that the following is true of a regulated unit:

     
    368
     
    A) The regulated unit is closed or closing, meaning it has begun the
    closure process under Section 724.213 or 35 Ill. Adm. Code
    725.213; and
     
    B) Inclusion of the regulated unit will enhance implementation of
    effective, protective, and reliable remedial actions for the facility.
     
    2) The Subpart F, G, and H requirements and the unit-specific requirements
    of this Part or 35 Ill. Adm. Code 265 that applied to the regulated unit will
    continue to apply to that portion of the CAMU after incorporation into the
    CAMU.
     
    c) The Agency must designate a CAMU that will be used for storage or treatment
    only in accordance with subsection (f) of this Section. The Agency must
    designate any other CAMU in accordance with the following requirements:
     
    1) The CAMU must facilitate the implementation of reliable, effective,
    protective, and cost-effective remedies;
     
    2) Waste management activities associated with the CAMU must not create
    unacceptable risks to humans or to the environment resulting from
    exposure to hazardous wastes or hazardous constituents;
     
    3) The CAMU must include uncontaminated areas of the facility, only if
    including such areas for the purpose of managing CAMU-eligible waste is
    more protective than management of such wastes at contaminated areas of
    the facility;
     
    4) Areas within the CAMU, where wastes remain in place after closure of the
    CAMU, must be managed and contained so as to minimize future releases,
    to the extent practicable;
     
    5) The CAMU must expedite the timing of remedial activity implementation,
    when appropriate and practicable;
     
    6) The CAMU must enable the use, when appropriate, of treatment
    technologies (including innovative technologies) to enhance the long-term
    effectiveness of remedial actions by reducing the toxicity, mobility, or
    volume of wastes that will remain in place after closure of the CAMU; and
     
    7) The CAMU must, to the extent practicable, minimize the land area of the
    facility upon which wastes will remain in place after closure of the
    CAMU.
     
    d) The owner or operator must provide sufficient information to enable the Agency

     
    369
    to designate a CAMU in accordance with the criteria in this Section. This must
    include, unless not reasonably available, information on the following:
     
    1) The origin of the waste and how it was subsequently managed (including a
    description of the timing and circumstances surrounding the disposal or
    release);
     
    2) Whether the waste was listed or identified as hazardous at the time of
    disposal or release; and
     
    3) Whether the disposal or release of the waste occurred before or after the
    land disposal requirements of 35 Ill. Adm. Code 728 were in effect for the
    waste listing or characteristic.
     
    e) The Agency must specify, in the permit or order, requirements for the CAMU to
    include the following:
     
    1) The areal configuration of the CAMU.
     
    2) Except as provided in subsection (g) of this Section, requirements for
    CAMU-eligible waste management to include the specification of
    applicable design, operation, treatment, and closure requirements.
     
    3) Minimum Design Requirements: a CAMU, except as provided in
    subsection (f) of this Section, into which wastes are placed must be
    designed in accordance with the following:
     
    A) Unless the Agency approves alternative requirements under
    subsection (e)(3)(B) of this Section, a CAMU that consists of new,
    replacement, or laterally expanded units must include a composite
    liner and a leachate collection system that is designed and
    constructed to maintain less than a 30-cm depth of leachate over
    the liner. For purposes of this Section, “composite liner”
     
    means a
    system consisting of two components; the upper component must
    consist of a minimum 30-mil flexible membrane liner (FML), and
    the lower component must consist of at least a two-foot layer of
    compacted soil with a hydraulic conductivity of no more than
    1x10
    -7
    cm/sec. FML components consisting of high density
    polyethylene (HDPE) must be at least 60 mil thick. The FML
    component must be installed in direct and uniform contact with the
    compacted soil component;
     
    B) Alternative Requirements. The Agency must approve alternative
    requirements if it determines that either of the following is true:
     
    i) The Agency determines that alternative design and

     
    370
    operating practices, together with location characteristics,
    will prevent the migration of any hazardous constituents
    into the groundwater or surface water at least as effectively
    as the liner and leachate collection systems in subsection
    (e)(3)(A) of this Section; or
     
    ii) The CAMU is to be established in an area with existing
    significant levels of contamination, and the Agency
    determines that an alternative design, including a design
    that does not include a liner, would prevent migration from
    the unit that would exceed long-term remedial goals.
     
    4) Minimum treatment requirements: Unless the wastes will be placed in a
    CAMU for storage or treatment only in accordance with subsection (f) of
    this Section, CAMU-eligible wastes that, absent this Section, would be
    subject to the treatment requirements of 35 Ill. Adm. Code 728, and that
    the Agency determines contain principal hazardous constituents must be
    treated to the standards specified in subsection (e)(4)(C) of this Section.
     
    A) Principal hazardous constituents are those constituents that the
    Agency determines pose a risk to human health and the
    environment substantially higher than the cleanup levels or goals
    at the site.
     
    i) In general, the Agency must designate as principal
    hazardous constituents those contaminants specified in
    subsection (e)(4)(H) of this Section.
     
    BOARD NOTE: The Board has codified 40 CFR
    264.552(e)(4)(i)(A)(
    1
    ) and (e)(4)(i)(A)(
    2
    ) as subsections
    (e)(4)(H)(i) and (e)(4)(H)(ii) of this Section in order to
    comply with Illinois Administrative Code codification
    requirements.
     
    ii) The Agency must also designate constituents as principal
    hazardous constituents, where appropriate, when risks to
    human health and the environment posed by the potential
    migration of constituents in wastes to groundwater are
    substantially higher than cleanup levels or goals at the site;
    when making such a designation, the Agency must consider
    such factors as constituent concentrations, and fate and
    transport characteristics under site conditions.
     
    iii) The Agency must also designate other constituents as
    principal hazardous constituents that the Agency
    determines pose a risk to human health and the

     
    371
    environment substantially higher than the cleanup levels or
    goals at the site.
     
    B) In determining which constituents are “principal hazardous
    constituents,” the Agency must consider all constituents that,
    absent this Section, would be subject to the treatment requirements
    in 35 Ill. Adm. Code 728.
     
    C) Waste that the Agency determines contains principal hazardous
    constituents must meet treatment standards determined in
    accordance with subsection (e)(4)(D) or (e)(4)(E) of this Section.
     
    D) Treatment standards for wastes placed in a CAMU.
     
    i) For non-metals, treatment must achieve 90 percent
    reduction in total principal hazardous constituent
    concentrations, except as provided by subsection
    (e)(4)(D)(iii) of this Section.
     
    ii) For metals, treatment must achieve 90 percent reduction in
    principal hazardous constituent concentrations as measured
    in leachate from the treated waste or media (tested
    according to the TCLP) or 90 percent reduction in total
    constituent concentrations (when a metal removal treatment
    technology is used), except as provided by subsection
    (e)(4)(D)(iii) of this Section.
     
    iii) When treatment of any principal hazardous constituent to a
    90 percent reduction standard would result in a
    concentration less than 10 times the Universal Treatment
    Standard for that constituent, treatment to achieve
    constituent concentrations less than 10 times the Universal
    Treatment Standard is not required. Universal Treatment
    Standards are identified in Table U to 35 Ill. Adm. Code
    728.
     
    iv) For waste exhibiting the hazardous characteristic of
    ignitability, corrosivity, or reactivity, the waste must also
    be treated to eliminate these characteristics.
     
    v) For debris, the debris must be treated in accordance with §
    268.45, or by methods or to levels established under
    subsections (e)(4)(D)(i) through (e)(4)(D)(iv) or subsection
    (e)(4)(E) of this Section, whichever the Agency determines
    is appropriate.
     

     
    372
    vi) Alternatives to TCLP. For metal bearing wastes for which
    metals removal treatment is not used, the Agency must
    specify a leaching test other than the TCLP (SW-846,
    Method 1311 (Toxicity Characteristic Leaching
    Procedure), in “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods,” USEPA publication number
    EPA-530/SW-846, incorporated by reference in 35 Ill.
    Adm. Code 720.111) 720.111(a) to measure treatment
    effectiveness, provided the Agency determines that an
    alternative leach testing protocol is appropriate for use, and
    that the alternative more accurately reflects conditions at
    the site that affect leaching.
     
    E) Adjusted standards. The Board will grant an adjusted standard
    pursuant to Section 28.1 of the Act to adjust the treatment level or
    method in subsection (e)(4)(D) of this Section to a higher or lower
    level, based on one or more of the following factors, as
    appropriate, if the owner or operator demonstrates that the adjusted
    level or method would be protective of human health and the
    environment, based on consideration of the following:
     
    i) The technical impracticability of treatment to the levels or
    by the methods in subsection (e)(4)(D) of this Section;
     
    ii) The levels or methods in subsection (e)(4)(D) of this
    Section would result in concentrations of principal
    hazardous constituents (PHCs) that are significantly above
    or below cleanup standards applicable to the site
    (established either site-specifically, or promulgated under
    State or federal law);
     
    iii) The views of the affected local community on the treatment
    levels or methods in subsection (e)(4)(D) of this Section, as
    applied at the site, and, for treatment levels, the treatment
    methods necessary to achieve these levels;
     
    iv) The short-term risks presented by the on-site treatment
    method necessary to achieve the levels or treatment
    methods in subsection (e)(4)(D) of this Section;
     
    v) The long-term protection offered by the engineering design
    of the CAMU and related engineering controls under the
    circumstances set forth in subsection (e)(4)(I) of this
    Section.
     
    BOARD NOTE: The Board has codified 40 CFR

     
    373
    264.552(e)(4)(v)(E)(
    1
    ) through (e)(4)(v)(E)(
    5
    ) as
    subsections (e)(4)(I)(i) through (e)(4)(I)(v) of this Section
    in order to comply with Illinois Administrative Code
    codification requirements.
     
    F) The treatment required by the treatment standards must be
    completed prior to, or within a reasonable time after, placement in
    the CAMU.
     
    G) For the purpose of determining whether wastes placed in a CAMU
    have met site-specific treatment standards, the Agency must
    specify a subset of the principal hazardous constituents in the
    waste as analytical surrogates for determining whether treatment
    standards have been met for other principal hazardous constituents
    if it determines that the specification is appropriate based on the
    degree of difficulty of treatment and analysis of constituents with
    similar treatment properties.
     
    H) Principal hazardous constituents that the Agency must designate
    are the following:
     
    i) Carcinogens that pose a potential direct risk from ingestion
    or inhalation at the site at or above 10
    -3
    ; and
     
    ii) Non-carcinogens that pose a potential direct risk from
    ingestion or inhalation at the site an order of magnitude or
    greater over their reference dose.
     
    I) Circumstances relating to the long-term protection offered by
    engineering design of the CAMU and related engineering controls
    are the following:
     
    i) Where the treatment standards in subsection (e)(4)(D) of
    this Section are substantially met and the principal
    hazardous constituents in the waste or residuals are of very
    low mobility;
     
    ii) Where cost-effective treatment has been used and the
    CAMU meets the Subtitle C liner and leachate collection
    requirements for new land disposal units at Section
    724.401(c) and (d);
     
    iii) Where, after review of appropriate treatment technologies,
    the Board determines that cost-effective treatment is not
    reasonably available, and the CAMU meets the Subtitle C
    liner and leachate collection requirements for new land

     
    374
    disposal units at Section 724.401(c) and (d);
     
    iv) Where cost-effective treatment has been used and the
    principal hazardous constituents in the treated wastes are of
    very low mobility; or
     
    v) Where, after review of appropriate treatment technologies,
    the Board determines that cost-effective treatment is not
    reasonably available, the principal hazardous constituents
    in the wastes are of very low mobility, and either the
    CAMU meets or exceeds the liner standards for new,
    replacement, or a laterally expanded CAMU in subsections
    (e)(3)(A) and (e)(3)(B) of this Section or the CAMU
    provides substantially equivalent or greater protection.
     
    5) Except as provided in subsection (f) of this Section, requirements for
    groundwater monitoring and corrective action that are sufficient to do the
    following:
     
    A) Continue to detect and to characterize the nature, extent,
    concentration, direction, and movement of existing releases of
    hazardous constituents in groundwater from sources located within
    the CAMU;
     
    B) Detect and subsequently characterize releases of hazardous
    constituents to groundwater that may occur from areas of the
    CAMU in which wastes will remain in place after closure of the
    CAMU; and
     
    C) Require notification to the Agency and corrective action as
    necessary to protect human health and the environment for releases
    to groundwater from the CAMU.
     
    6) Except as provided in subsection (f) of this Section, closure and post-
    closure requirements, as follows:
     
    A) Closure of corrective action management units must do the
    following:
     
    i) Minimize the need for further maintenance; and
     
    ii) Control, minimize, or eliminate, to the extent necessary to
    protect human health and the environment, for areas where
    wastes remain in place, post-closure escape of hazardous
    wastes, hazardous constituents, leachate, contaminated
    runoff, or hazardous waste decomposition products to the

     
    375
    ground, to surface waters, or to the atmosphere.
     
    B) Requirements for closure of a CAMU must include the following,
    as appropriate and as deemed necessary by the Agency for a given
    CAMU:
     
    i) Requirements for excavation, removal, treatment or
    containment of wastes; and
     
    ii) Requirements for removal and decontamination of
    equipment, devices, and structures used in CAMU-eligible
    waste management activities within the CAMU.
     
    C) In establishing specific closure requirements for a CAMU under
    this subsection (e), the Agency must consider the following
    factors:
     
    i) CAMU characteristics;
     
    ii) Volume of wastes that remain in place after closure;
     
    iii) Potential for releases from the CAMU;
     
    iv) Physical and chemical characteristics of the waste;
     
    v) Hydrological and other relevant environmental conditions
    at the facility that may influence the migration of any
    potential or actual releases; and
     
    vi) Potential for exposure of humans and environmental
    receptors if releases were to occur from the CAMU.
     
    D) Cap requirements:
     
    i) At final closure of the CAMU, for areas in which wastes
    will remain with constituent concentrations at or above
    remedial levels or goals applicable to the site after closure
    of the CAMU, the owner or operator must cover the
    CAMU with a final cover designed and constructed to meet
    the performance criteria listed in subsection (e)(6)(F) of
    this Section, except as provided in subsection (e)(6)(D)(ii)
    of this Section:
     
    BOARD NOTE: The Board has codified 40 CFR
    264.552(e)(6)(iv)(A)(
    1
    ) through (e)(6)(iv)(A)(
    5
    ) as
    subsections (e)(6)(F)(i) through (e)(6)(F)(v) of this Section

     
    376
    in order to comply with Illinois Administrative Code
    codification requirements.
     
    ii) The Agency must apply cap requirements that deviate from
    those prescribed in subsection (e)(6)(D)(i) of this Section if
    it determines that the modifications are needed to facilitate
    treatment or the performance of the CAMU (e.g., to
    promote biodegradation).
     
    E) Post-closure requirements as necessary to protect human health
    and the environment, to include, for areas where wastes will
    remain in place, monitoring and maintenance activities, and the
    frequency with which such activities must be performed to ensure
    the integrity of any cap, final cover, or other containment system.
     
    F) The final cover design and performance criteria are as follows:
     
    i) Provide long-term minimization of migration of liquids
    through the closed unit;
     
    ii) Function with minimum maintenance;
     
    iii) Promote drainage and minimize erosion or abrasion of the
    cover;
     
    iv) Accommodate settling and subsidence so that the cover’s
    integrity is maintained; and
     
    v) Have a permeability less than or equal to the permeability
    of any bottom liner system or natural subsoils present.
     
    f) A CAMU used for storage or treatment only is a CAMU in which wastes will not
    remain after closure. Such a CAMU must be designated in accordance with all of
    the requirements of this Section, except as follows:
     
    1) A CAMU that is used for storage or treatment only and that operates in
    accordance with the time limits established in the staging pile regulations
    at Section 724.654(d)(1)(C), (h), and (i) is subject to the requirements for
    staging piles at Section 724.654(d)(1)(A) and (d)(1)(B), (d)(2), (e), (f), (j),
    and (k) in lieu of the performance standards and requirements for a
    CAMU in subsections (c) and (e)(3) through (e)(6) of this Section.
     
    2) A CAMU that is used for storage or treatment only and that does not
    operate in accordance with the time limits established in the staging pile
    regulations at Section 724.654(d)(1)(C), (h), and (i):
     

     
    377
    A) The owner or operator must operate in accordance with a time
    limit, established by the Agency, that is no longer than necessary
    to achieve a timely remedy selected for the waste and
     
    B) The CAMU is subject to the requirements for staging piles at
    Section 724.654(d)(1)(A) and (d)(1)(B), (d)(2), (e), (f), (j), and (k)
    in lieu of the performance standards and requirements for a CAMU
    in subsections (c), (e)(4), and (6) of this Section.
     
    g) A CAMU into which wastes are placed where all wastes have constituent levels at
    or below remedial levels or goals applicable to the site do not have to comply
    with the requirements for liners at subsection (e)(3)(A) of this Section, caps at
    subsection (e)(6)(D) of this Section, groundwater monitoring requirements at
    subsection (e)(5) of this Section or, for treatment or storage-only a CAMU, the
    design standards at subsection (f) of this Section.
     
    h) The Agency must provide public notice and a reasonable opportunity for public
    comment before designating a CAMU. Such notice must include the rationale for
    any proposed adjustments under subsection (e)(4)(E) of this Section to the
    treatment standards in subsection (e)(4)(D) of this Section.
     
    i) Notwithstanding any other provision of this Section, the Agency must impose
    those additional requirements that it determines are necessary to protect human
    health and the environment.
     
    j) Incorporation of a CAMU into an existing permit must be approved by the
    Agency according to the procedures for Agency-initiated permit modifications
    under 35 Ill. Adm. Code 703.270 through 703.273, or according to the permit
    modification procedures of 35 Ill. Adm. Code 703.280 through 703.283.
     
    k) The designation of a CAMU does not change the Agency’s existing authority to
    address cleanup levels, media-specific points of compliance to be applied to
    remediation at a facility, or other remedy selection decisions.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART W: DRIP PADS
     
    Section 724.673 Design and Operating Requirements
     
    a) Drip pads must fulfill the following:
     
    1) Not be constructed of earthen materials, wood, or asphalt, unless the
    asphalt is structurally supported;
     
    2) Be sloped to free-drain to the associated collection system treated wood

     
    378
    drippage, rain, other waters, or solutions of drippage and water or other
    wastes;
     
    3) Have a curb or berm around the perimeter;
     
    4) In addition, the drip pad must fulfill the following:
     
    A) Have a hydraulic conductivity of less than or equal to 1 X 10
    -7
     
    centimeters per second (cm/sec), e.g., existing concrete drip pads
    must be sealed, coated, or covered with a surface material with a
    hydraulic conductivity of less than or equal to 1 X 10
    -7
    cm/sec
    such that the entire surface where drippage occurs or may run
    across is capable of containing such drippage and mixtures of
    drippage and precipitation, materials, or other wastes while being
    routed to an associated collection system. This surface material
    must be maintained free of cracks and gaps that could adversely
    affect its hydraulic conductivity, and the material must be
    chemically compatible with the preservatives that contact the drip
    pad. The requirements of this provision apply only to the existing
    drip pads and those drip pads for which the owner or operator
    elects to comply with Section 724.672(a) instead of Section
    724.672(b).
     
    B) The owner or operator must obtain and keep on file at the facility a
    written assessment of the drip pad, reviewed and certified by an
    independent qualified registered professional engineer that attests
    to the results of the evaluation. The assessment must be reviewed,
    updated and recertified annually. The evaluation must document
    the extent to which the drip pad meets the design and operating
    standards of this Section, except for in subsection (b) of this
    Section.
     
    5) Be of sufficient structural strength and thickness to prevent failure due to
    physical contact, climatic conditions, the stress of installation, and the
    stress of daily operations, e.g., variable and moving loads such as vehicle
    traffic, movement of wood, etc.
     
    BOARD NOTE: In judging the structural integrity requirement of this
    subsection (c), the Agency should generally consider applicable standards
    established by professional organizations generally recognized by the
    industry, including ACI 318 (Building Code Requirements for Reinforced
    Concrete), or ASTM C94 C 94-90 (Standard Specification for Ready-
    Mixed Concrete), each incorporated by reference in 35 Ill. Adm. Code
    720.111 720.111(a).
     
    b) If an owner or operator elects to comply with Section 724.672(b) instead of

     
    379
    Section 724.672(a), the drip pad must have the following:
     
    1) A synthetic liner installed below the drip pad that is designed, constructed,
    and installed to prevent leakage from the drip pad into the adjacent
    subsurface soil or groundwater or surface water at any time during the
    active life (including the closure period) of the drip pad. The liner must
    be constructed of materials that will prevent waste from being absorbed
    into the liner and to prevent releases into the adjacent subsurface soil or
    groundwater or surface water during the active life of the facility. The
    liner must fulfill the following:
     
    A) It must be constructed of materials that have appropriate chemical
    properties and sufficient strength and thickness to prevent failure
    due to pressure gradients (including static head and external
    hydrogeologic forces), physical contact with the waste or drip pad
    leakage to which they are exposed, climatic conditions, the stress
    of installation and the stress of daily operation (including stresses
    from vehicular traffic on the drip pad);
     
    B) It must be placed upon a foundation or base capable of providing
    support to the liner and resistance to pressure gradients above and
    below the liner to prevent failure of the liner due to settlement,
    compression or uplift; and
     
    C) It must be installed to cover all surrounding earth that could come
    in contact with the waste or leakage; and
     
    2) A leakage detection system immediately above the liner that is designed,
    constructed, maintained, and operated to detect leakage from the drip pad.
    The leakage detection system must fulfill the following:
     
    A) It must be constructed of materials that are as follows:
     
    i) Chemically resistant to the waste managed in the drip pad
    and the leakage that might be generated; and
     
    ii) Of sufficient strength and thickness to prevent collapse
    under the pressures exerted by overlaying materials and by
    any equipment used at the drip pad; and
     
    B) It must be designed and operated to function without clogging
    through the scheduled closure of the drip pad; and
     
    C) It must be designed so that it will detect the failure of the drip pad
    or the presence of a release of hazardous waste or accumulated
    liquid at the earliest practicable time.

     
    380
     
    3) A leaking collection system immediately above the liner that is designed,
    constructed, maintained, and operated to collect leakage from the drip pad
    such that it can be removed from below the drip pad. The date, time, and
    quantity of any leakage collected in this system and removed must be
    documented in the operating log.
     
    A) The drip pad surface must be cleaned thoroughly in a manner and
    frequency such that accumulated residues of hazardous waste or
    other materials are removed, with residues being properly managed
    as to allow weekly inspections of the entire drip pad surface
    without interference of hindrance from accumulated residues of
    hazardous waste or other materials on the drip pad. The owner or
    operator must document the date and time of each cleaning and
    cleaning procedure used in the facility’s operating log. The owner
    or operator must determine if the residues are hazardous, as per 35
    Ill. Adm. Code 722.111, and, if so, the owner or operator must
    manage them under 35 Ill. Adm. Code 721 through 728, and
    Section 3010 of RCRA.
     
    B) The Federal
    federal rules do not contain a 40 CFR
    264.573(b)(3)(B). This subsection (b) is added to conform to
    Illinois Administrative Code rules.
     
    c) Drip pads must be maintained such that they remain free of cracks, gaps,
    corrosion, or other deterioration that could cause hazardous waste to be released
    from the drip pad.
     
    BOARD NOTE: See subsection (m) of this Section for remedial action required
    if deterioration or leakage is detected.
     
    d) The drip pad and associated collection system must be designed and operated to
    convey, drain, and collect liquid resulting from drippage or precipitation in order
    to prevent run-off.
     
    e) Unless the drip pad is protected by a structure, as described in Section 724.670(b),
    the owner or operator must design, construct, operate, and maintain a run-on
    control system capable of preventing flow onto the drip pad during peak
    discharge from at least a 24-hour, 25-year storm, unless the system has sufficient
    excess capacity to contain any run-on that might enter the system.
     
    f) Unless the drip pad is protected by a structure or cover, as described in Section
    724.670(b), the owner or operator must design, construct, operate, and maintain a
    run-off management system to collect and control at least the water volume
    resulting from a 24-hour, 25-year storm.
     

     
    381
    g) The drip pad must be evaluated to determine that it meets the requirements of
    subsections (a) through (f) of this Section. The owner or operator must obtain a
    statement from an independent, qualified registered professional engineer
    certifying that the drip pad design meets the requirements of this Section.
     
    h) Drippage and accumulated precipitation must be removed from the associated
    collection system as necessary to prevent overflow onto the drip pad.
     
    i) The drip surface must be cleaned thoroughly at least once every seven days such
    that accumulated residues of hazardous waste or other materials are removed,
    using an appropriate and effective cleaning technique, including but not limited
    to, rinsing, washing with detergents or other appropriate solvents, or steam
    cleaning. The owner or operator must document, in the facility’s operating log,
    the date and time of each cleaning and the cleaning procedure used.
     
    j) Drip pads must be operated and maintained in a manner to minimize tracking of
    hazardous waste or hazardous waste constituents off the drip pad as a result of
    activities by personnel or equipment.
     
    k) After being removed from the treatment vessel, treated wood from pressure and
    non-pressure processes must be held on the drip pad until drippage has ceased.
    The owner or operator must maintain records sufficient to document that all
    treated wood is held on the pad, in accordance with this Section, following
    treatment.
     
    l) Collection and holding units associated with run-on and run-off control systems
    must be emptied or otherwise managed as soon as possible after storms to
    maintain design capacity of the system.
     
    m) Throughout the active life of the drip pad and as specified in the permit, if the
    owner or operator detects a condition that could lead to or has caused a release of
    hazardous waste, the condition must be repaired within a reasonably prompt
    period of time following discovery, in accordance with the following procedures:
     
    1) Upon detection of a condition that may have caused or has caused a
    release of hazardous waste (e.g., upon detection of leakage in the leak
    detection system), the owner or operator must do the following:
     
    A) Enter a record of the discovery in the facility operating log;
     
    B) Immediately remove from service the portion of the drip pad
    affected by the condition;
     
    C) Determine what steps must be taken to repair the drip pad, clean up
    any leakage from below the drip pad, and establish a schedule for
    accomplishing the clean up and repairs;

     
    382
     
    D) Within 24 hours after discovery of the condition, notify the
    Agency of the condition and, within 10 working days, provide
    written notice to the Agency with a description of the steps that
    will be taken to repair the drip pad and clean up any leakage, and
    the schedule for accomplishing this work.
     
    2) The Agency must do the following: review the information submitted,
    make a determination regarding whether the pad must be removed from
    service completely or partially until repairs and clean up are complete, and
    notify the owner or operator of the determination and the underlying
    rationale in writing.
     
    3) Upon completing all repairs and clean up, the owner or operator must
    notify the Agency in writing and provide a certification, signed by an
    independent, qualified registered professional engineer, that the repairs
    and clean up have been completed according to the written plan submitted
    in accordance with subsection (m)(1)(D) of this Section.
     
    n) If a permit is necessary, the Agency must specify in the permit all design and
    operating practices that are necessary to ensure that the requirements of this
    Section are satisfied.
     
    o) The owner or operator must maintain, as part of the facility operating log,
    documentation of past operating and waste handling practices. This must include
    identification of preservative formulations used in the past, a description of
    drippage management practices, and a description of treated wood storage and
    handling practices.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART X: MISCELLANEOUS UNITS
     
    Section 724.701 Environmental Performance Standards
     
    A miscellaneous unit must be located, designed, constructed, operated, maintained, and closed in
    a manner that will ensure protection of human health and the environment. Permits for
    miscellaneous units are to contain such terms and provisions as are necessary to protect human
    health and the environment, including, but not limited to, as appropriate, design and operating
    requirements, detection and monitoring requirements, and requirements for responses to releases
    of hazardous waste or hazardous constituents from the unit. Permit terms and provisions must
    include those requirements of Subparts I through O and AA through CC of this Part; 35 Ill. Adm.
    Code 702, 703, and 730; and federal subpart EEE of 40 CFR 63, Subpart EEE, incorporated by
    reference in 35 Ill. Adm. Code 720.111 720.111(b), that are appropriate for the miscellaneous
    unit being permitted. Protection of human health and the environment includes, but is not
    limited to the following:

     
    383
     
    a) Prevention of any releases that may have adverse effects on human health or the
    environment due to migration of waste constituents in the groundwater or
    subsurface environment, considering the following:
     
    1) The volume and physical and chemical characteristics of the waste in the
    unit, including its potential for migration through soil, liners, or other
    containing structures;
     
    2) The hydrologic and geologic characteristics of the unit and the
    surrounding area;
     
    3) The existing quality of groundwater, including other sources of
    contamination and their cumulative impact on the groundwater;
     
    4) The quantity and direction of groundwater flow;
     
    5) The proximity to and withdrawal rates of current and potential
    groundwater users;
     
    6) The patterns of land use in the region;
     
    7) The potential for deposition or migration of waste constituents into
    subsurface physical structures and the root zone of food-chain crops and
    other vegetation;
     
    8) The potential for health risks caused by human exposure to waste
    constituents; and
     
    9) The potential for damage to domestic animals, wildlife, crops, vegetation,
    and physical structures caused by exposure to waste constituents.
     
    b) Prevention of any releases that may have adverse effects on human health or the
    environment due to migration of waste constituents in surface water, in wetlands,
    or on the soil surface, considering the following:
     
    1) The volume and physical and chemical characteristics of the waste in the
    unit;
     
    2) The effectiveness and reliability of containing, confining, and collecting
    systems and structures in preventing migration;
     
    3) The hydrologic characteristics of the unit and surrounding area, including
    the topography of the land around the unit;
     
    4) The patterns of precipitation in the region;

     
    384
     
    5) The quantity, quality, and direction of groundwater flow;
     
    6) The proximity of the unit to surface waters;
     
    7) The current and potential uses of the nearby surface waters and any water
    quality standards in 35 Ill. Adm. Code 302 or 303;
     
    8) The existing quality of surface waters and surface soils, including other
    sources of contamination and their cumulative impact on surface waters
    and surface soils;
     
    9) The patterns of land use in the region;
     
    10) The potential for health risks caused by human exposure to waste
    constituents; and
     
    11) The potential for damage to domestic animals, wildlife, crops, vegetation,
    and physical structures caused by exposure to waste constituents.
     
    c) Prevention of any release that may have adverse effects on human health or the
    environment due to migration of waste constituents in the air, considering the
    following:
     
    1) The volume and physical and chemical characteristics of the waste in the
    unit, including its potential for the emission and dispersal of gases,
    aerosols, and particulates;
     
    2) The effectiveness and reliability of systems and structures to reduce or
    prevent emissions of hazardous constituents to the air;
     
    3) The operating characteristics of the unit;
     
    4) The atmospheric, meteorologic, and topographic characteristics of the unit
    and the surrounding area;
     
    5) The existing quality of the air, including other sources of contamination
    and their cumulative impact on the air;
     
    6) The potential for health risks caused by human exposure to waste
    constituents; and
     
    7) The potential for damage to domestic animals, wildlife, crops, vegetation,
    and physical structures caused by waste constituents.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)

     
    385
     
    SUBPART AA: AIR EMISSION STANDARDS FOR PROCESS VENTS
     
    Section 724.933 Standards: Closed-Vent Systems and Control Devices
     
    a) Compliance Required.
     
    1) Owners or operators of closed-vent systems and control devices used to
    comply with provisions of this Part must comply with the provisions of
    this Section.
     
    2) Implementation Schedule.
     
    A) The owner or operator of an existing facility that cannot install a
    closed-vent system and control device to comply with the
    provisions of this Subpart AA on the effective date that the facility
    becomes subject to the provisions of this Subpart AA must prepare
    an implementation schedule that includes dates by which the
    closed-vent system and control device will be installed and in
    operation. The controls must be installed as soon as possible, but
    the implementation schedule may allow up to 30 months after the
    effective date that the facility becomes subject to this Subpart AA
    for installation and startup.
     
    B) Any unit that began operation after December 21, 1990 and which
    was subject to the provisions of this Subpart AA when operation
    began must comply with the rules immediately (i.e., must have
    control devices installed and operating on startup of the affected
    unit); the 30-month implementation schedule does not apply.
     
    C) The owner or operator of any facility in existence on the effective
    date of a statutory or regulatory amendment that renders the
    facility subject to this Subpart AA must comply with all
    requirements of this Subpart AA as soon as practicable, but no
    later than 30 months after the effective date of the amendment.
    When control equipment required by this Subpart AA can not be
    installed and begin operation by the effective date of the
    amendment, the facility owner or operator must prepare an
    implementation schedule that includes the following information:
    specific calendar dates for award of contracts or issuance of
    purchase orders for the control equipment, initiation of on-site
    installation of the control equipment, completion of the control
    equipment installation, and performance of any testing to
    demonstrate that the installed equipment meets the applicable
    standards of this Subpart AA. The owner or operator must enter
    the implementation schedule in the operating record or in a

     
    386
    permanent, readily available file located at the facility.
     
    D) An owner or operator of a facility or unit that becomes newly
    subject to the requirements of this Subpart AA after December 8,
    1997 due to an action other than those described in subsection
    (a)(2)(C) of this Section must comply with all applicable
    requirements immediately (i.e., the facility or unit must have
    control devices installed and operating on the date the facility or
    unit becomes subject to this Subpart AA; the 30-month
    implementation schedule does not apply).
     
    b) A control device involving vapor recovery (e.g., a condenser or adsorber) must be
    designed and operated to recover the organic vapors vented to it with an
    efficiency of 95 weight percent or greater unless the total organic emission limits
    of Section 724.932(a)(1) for all affected process vents is attained at an efficiency
    less than 95 weight percent.
     
    c) An enclosed combustion device (e.g., a vapor incinerator, boiler, or process
    heater) must be designed and operated to reduce the organic emissions vented to
    it by 95 weight percent or greater; to achieve a total organic compound
    concentration of 20 ppmv, expressed as the sum of the actual compounds and not
    in carbon equivalents, on a dry basis, corrected to three percent oxygen; or to
    provide a minimum residence time of 0.50 seconds at a minimum temperature of
    760° C. If a boiler or process heater is used as the control device, then the vent
    stream must be introduced into the flame zone of the boiler or process heater.
     
    d) Flares.
     
    1) A flare must be designed for and operated with no visible emissions, as
    determined by the methods specified in subsection (e)(1) of this Section,
    except for periods not to exceed a total of five minutes during any two
    consecutive hours.
     
    2) A flare must be operated with a flame present at all times, as determined
    by the methods specified in subsection (f)(2)(C) of this Section.
     
    3) A flare must be used only if the net heating value of the gas being
    combusted is 11.2 MJ/scm (300 Btu/scf) or greater and the flare is steam-
    assisted or air-assisted or if the net heating value of the gas being
    combusted is 7.45 MJ/scm (200 Btu/scf) or greater and the flare is
    nonassisted. The net heating value of the gas being combusted must be
    determined by the methods specified in subsection (e)(2) of this Section.
     
    4) Exit Velocity.
     
    A) A steam-assisted or nonassisted flare must be designed for and

     
    387
    operated with an exit velocity, as determined by the methods
    specified in subsection (e)(3) of this Section, less than 18.3 m/s (60
    ft/s), except as provided in subsections (d)(4)(B) and (d)(4)(C) of
    this Section.
     
    B) A steam-assisted or nonassisted flare designed for and operated
    with an exit velocity, as determined by the methods specified in
    subsection (e)(3) of this Section, equal to or greater than 18.3 m/s
    (60 ft/s) but less than 122 m/s (400 ft/s) is allowed if the net
    heating value of the gas being combusted is greater than 37.3
    MJ/scm (1000 1,000 Btu/scf).
     
    C) A steam-assisted or nonassisted flare designed for and operated
    with an exit velocity, as determined by the methods specified in
    subsection (e)(3) of this Section, less than the velocity, V, as
    determined by the method specified in subsection (e)(4) of this
    Section, and less than 122 m/s (400 ft/s) is allowed.
     
    5) An air-assisted flare must be designed and operated with an exit velocity
    less than the velocity, V, as determined by the method specified in
    subsection (e)(5) of this Section.
     
    6) A flare used to comply with this Section must be steam-assisted, air-
    assisted, or nonassisted.
     
    e) Compliance determination and equations.
     
    1) Reference Method 22 (Visual Determination of Fugitive Emissions from
    Material Sources and Smoke Emissions from Flares) in appendix A to 40
    CFR 60 (Test Methods), incorporated by reference in 35 Ill. Adm. Code
    720.111 720.111(b), must be used to determine the compliance of a flare
    with the visible emission provisions of this Subpart AA. The observation
    period is two hours and must be used according to Method 22.
     
    2) The net heating value of the gas being combusted in a flare must be
    calculated using the following equation:
    =
    ×
    ×
    n
    1
    i
    Hi
    Ci
    K
    =
    HT
      
    Where:
     
    HT is the net heating value of the sample in MJ/scm; where the net
    enthalpy per mole of offgas is based on combustion at 25° C and
    760 mm Hg, but the standard temperature for determining the

     
    388
    volume corresponding to 1 mole is 20° C.
     
    K = 1.74
    ×
    10
    7
    10
    -7
    (1/ppm)(g mol/scm)(MJ/kcal) where the
    standard temperature for (g mol/scm) is 20° C.
     
    Σ
    (Xi) means the sum of the values of X for each component i,
    from i=1 to n.
     
    Ci is the concentration of sample component i in ppm on a wet
    basis, as measured for organics by Reference Method 18
    (Measurement of Gaseous Organic Compound Emissions by Gas
    Chromatography) in appendix A to 40 CFR 60 (Test Methods),
    and for carbon monoxide, by ASTM D 1946-90 (Standard Practice
    for Analysis of Reformed Gas by Gas Chromatography), each
    incorporated by reference in 35 Ill. Adm. Code 720.111.
     
    Hi is the net heat of combustion of sample component i, kcal/gmol
    at 25° C and 760 mm Hg. The heats of combustion must be
    determined using ASTM D 2382-88 (Standard Test Method for
    Heat of Combustion of Hydrocarbon Fuels by Bomb Calorimeter
    (High Precision Method)), incorporated by reference in 35 Ill.
    Adm. Code 720.111 720.111(a), if published values are not
    available or cannot be calculated.
     
    3) The actual exit velocity of a flare must be determined by dividing the
    volumetric flow rate (in units of standard temperature and pressure), as
    determined by Reference Methods 2 (Determination of Stack Gas Velocity
    and Volumetric Flow Rate (Type S Pitot Tube)), 2A (Direct Measurement
    of Gas Volume through Pipes and Small Ducts), 2C (Determination of Gas
    Velocity and Volumetric Flow Rate in Small Stacks or Ducts (Standard
    Pitot Tube)), or 2D (Measurement of Gas Volume Flow Rates in Small
    Pipes and Ducts) in appendix A to 40 CFR 60 (Test Methods),
    incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(b), as
    appropriate, by the unobstructed (free) cross-sectional area of the flare tip.
     
    4) The maximum allowed velocity in m/s, Vmax, for a flare complying with
    subsection (d)(4)(C) of this Section must be determined by the following
    equation:
     
    ()
    log V
    H 28.8
    31.7
    10 max
    T
    =
    +
     
     
    Where:
     
    log10 means logarithm to the base 10
     

     
    389
    HT is the net heating value as determined in subsection (e)(2) of
    this Section.
     
    5) The maximum allowed velocity in m/s, Vmax, for an air-assisted flare must
    be determined by the following equation:
     
    max
    T
    V
    8.706 0.7084H
    =+
      
    Where:
     
    HT is the net heating value as determined in subsection (e)(2) of
    this Section.
     
    f) The owner or operator must monitor and inspect each control device required to
    comply with this Section to ensure proper operation and maintenance of the
    control device by implementing the following requirements:
     
    1) Install, calibrate, maintain, and operate according to the manufacturer’s
    specifications a flow indicator that provides a record of stream flow from
    each affected process vent to the control device at least once every hour.
    The flow indicator sensor must be installed in the vent stream at the
    nearest feasible point to the control device inlet but before the point at
    which the vent streams are combined.
     
    2) Install, calibrate, maintain, and operate according to the manufacturer’s
    specifications a device to continuously monitor control device operation,
    as follows:
     
    A) For a thermal vapor incinerator, a temperature monitoring device
    equipped with a continuous recorder. The device must have
    accuracy of ±1 percent of the temperature being monitored in ° C
    or ±0.5° C, whichever is greater. The temperature sensor must be
    installed at a location in the combustion chamber downstream of
    the combustion zone.
     
    B) For a catalytic vapor incinerator, a temperature monitoring device
    equipped with a continuous recorder. The device must be capable
    of monitoring temperature at two locations and have an accuracy
    of ±1 percent of the temperature being monitored in ° C or ±0.5° C,
    whichever is greater. One temperature sensor must be installed in
    the vent stream at the nearest feasible point to the catalyst bed inlet
    and a second temperature sensor must be installed in the vent
    stream at the nearest feasible point to the catalyst bed outlet.
     
    C) For a flare, a heat sensing monitoring device equipped with a
    continuous recorder that indicates the continuous ignition of the

     
    390
    pilot flame.
     
    D) For a boiler or process heater having a design heat input capacity
    less than 44 MW, a temperature monitoring device equipped with a
    continuous recorder. The device must have an accuracy of ±1
    percent of the temperature being monitored in ° C or ±0.5° C,
    whichever is greater. The temperature sensor must be installed at a
    location in the furnace downstream of the combustion zone.
     
    E) For a boiler or process heater having a design heat input capacity
    greater than or equal to 44 MW, a monitoring device equipped
    with a continuous recorder to measure parameters that indicate
    good combustion operating practices are being used.
     
    F) For a condenser, either of the following:
     
    i) A monitoring device equipped with a continuous recorder
    to measure the concentration level of the organic
    compounds in the exhaust vent stream from the condenser;
    or
     
    ii) A temperature monitoring device equipped with a
    continuous recorder. The device must be capable of
    monitoring temperature with an accuracy of ±1 percent of
    the temperature being monitored in ° C or ±0.5° C,
    whichever is greater. The temperature sensor must be
    installed at a location in the exhaust vent stream from the
    condenser exit (i.e., product side).
     
    G) For a carbon adsorption system that regenerates the carbon bed
    directly in the control device such as a fixed-bed carbon adsorber,
    either of the following:
     
    i) A monitoring device equipped with a continuous recorder
    to measure the concentration level of the organic
    compounds in the exhaust vent stream from the carbon bed,
    or
     
    ii) A monitoring device equipped with a continuous recorder
    to measure a parameter that indicates the carbon bed is
    regenerated on a regular, predetermined time cycle.
     
    3) Inspect the readings from each monitoring device required by subsections
    (f)(1) and (f)(2) of this Section at least once each operating day to check
    control device operation and, if necessary, immediately implement the
    corrective measures necessary to ensure the control device operates in

     
    391
    compliance with the requirements of this Section.
     
    g) An owner or operator using a carbon adsorption system such as a fixed-bed
    carbon adsorber that regenerates the carbon bed directly onsite in the control
    device must replace the existing carbon in the control device with fresh carbon at
    a regular, predetermined time interval that is no longer than the carbon service life
    established as a requirement of Section 724.935(b)(4)(C)(vi).
     
    h) An owner or operator using a carbon adsorption system such as a carbon canister
    that does not regenerate the carbon bed directly onsite in the control device must
    replace the existing carbon in the control device with fresh carbon on a regular
    basis by using one of the following procedures:
     
    1) Monitor the concentration level of the organic compounds in the exhaust
    vent stream from the carbon adsorption system on a regular schedule, and
    replace the existing carbon with fresh carbon immediately when carbon
    breakthrough is indicated. The monitoring frequency must be daily or at
    an interval no greater than 20 percent of the time required to consume the
    total carbon working capacity established as a requirement of Section
    724.935(b)(4)(C)(vii), whichever is longer.
     
    2) Replace the existing carbon with fresh carbon at a regular, predetermined
    time interval that is less than the design carbon replacement interval
    established as a requirement of Section 724.935(b)(4)(C)(vii).
     
    i) An alternative operational or process parameter may be monitored if the operator
    demonstrates that the parameter will ensure that the control device is operated in
    conformance with these standards and the control device’s design specifications.
     
    j) An owner or operator of an affected facility seeking to comply with the provisions
    of this Part by using a control device other than a thermal vapor incinerator,
    catalytic vapor incinerator, flare, boiler, process heater, condenser, or carbon
    adsorption system is required to develop documentation including sufficient
    information to describe the control device operation and identify the process
    parameter or parameters that indicate proper operation and maintenance of the
    control device.
     
    k) A closed-vent system must meet either of the following design requirements:
     
    1) A closed-vent system must be designed to operate with no detectable
    emissions, as indicated by an instrument reading of less than 500 ppmv
    above background, as determined by the methods specified at Section
    724.934(b), and by visual inspections; or
     
    2) A closed-vent system must be designed to operate at a pressure below
    atmospheric pressure. The system must be equipped with at least one

     
    392
    pressure gauge or other pressure measurement device that can be read
    from a readily accessible location to verify that negative pressure is being
    maintained in the closed-vent system when the control device is operating.
     
    l) The owner or operator must monitor and inspect each closed-vent system required
    to comply with this Section to ensure proper operation and maintenance of the
    closed-vent system by implementing the following requirements:
     
    1) Each closed-vent system that is used to comply with subsection (k)(1) of
    this Section must be inspected and monitored in accordance with the
    following requirements:
     
    A) An initial leak detection monitoring of the closed-vent system must
    be conducted by the owner or operator on or before the date that
    the system becomes subject to this Section. The owner or operator
    must monitor the closed-vent system components and connections
    using the procedures specified in Section 724.934(b) to
    demonstrate that the closed-vent system operates with no
    detectable emissions, as indicated by an instrument reading of less
    than 500 ppmv above background.
     
    B) After initial leak detection monitoring required in subsection
    (l)(1)(A) of this Section, the owner or operator must inspect and
    monitor the closed-vent system as follows:
     
    i) Closed-vent system joints, seams, or other connections that
    are permanently or semi-permanently sealed (e.g., a welded
    joint between two sections of hard piping or a bolted and
    gasketed ducting flange) must be visually inspected at least
    once per year to check for defects that could result in air
    pollutant emissions. The owner or operator must monitor a
    component or connection using the procedures specified in
    Section 724.934(b) to demonstrate that it operates with no
    detectable emissions following any time the component is
    repaired or replaced (e.g., a section of damaged hard piping
    is replaced with new hard piping) or the connection is
    unsealed (e.g., a flange is unbolted).
     
    ii) Closed-vent system components or connections other than
    those specified in subsection (l)(1)(B)(i) of this Section
    must be monitored annually and at other times as requested
    by the Regional Administrator, except as provided for in
    subsection (o) of this Section, using the procedures
    specified in Section 724.934(b) to demonstrate that the
    components or connections operate with no detectable
    emissions.

     
    393
     
    C) In the event that a defect or leak is detected, the owner or operator
    must repair the defect or leak in accordance with the requirements
    of subsection (l)(3) of this Section.
     
    D) The owner or operator must maintain a record of the inspection
    and monitoring in accordance with the requirements specified in
    Section 724.935.
     
    2) Each closed-vent system that is used to comply with subsection (k)(2) of
    this Section must be inspected and monitored in accordance with the
    following requirements:
     
    A) The closed-vent system must be visually inspected by the owner or
    operator to check for defects that could result in air pollutant
    emissions. Defects include, but are not limited to, visible cracks,
    holes, or gaps in ductwork or piping or loose connections.
     
    B) The owner or operator must perform an initial inspection of the
    closed-vent system on or before the date that the system becomes
    subject to this Section. Thereafter, the owner or operator must
    perform the inspections at least once every year.
     
    C) In the event that a defect or leak is detected, the owner or operator
    must repair the defect in accordance with the requirements of
    subsection (l)(3) of this Section.
     
    D) The owner or operator must maintain a record of the inspection
    and monitoring in accordance with the requirements specified in
    Section 724.935.
     
    3) The owner or operator must repair all detected defects as follows:
     
    A) Detectable emissions, as indicated by visual inspection or by an
    instrument reading greater than 500 ppmv above background, must
    be controlled as soon as practicable, but not later than 15 calendar
    days after the emission is detected, except as provided for in
    subsection (l)(3)(C) of this Section.
     
    B) A first attempt at repair must be made no later than five calendar
    days after the emission is detected.
     
    C) Delay of repair of a closed-vent system for which leaks have been
    detected is allowed if the repair is technically infeasible without a
    process unit shutdown, or if the owner or operator determines that
    emissions resulting from immediate repair would be greater than

     
    394
    the fugitive emissions likely to result from delay of repair. Repair
    of such equipment must be completed by the end of the next
    process unit shutdown.
     
    D) The owner or operator must maintain a record of the defect repair
    in accordance with the requirements specified in Section 724.935.
     
    m) A closed-vent system or control device used to comply with provisions of this
    Subpart AA must be operated at all times when emissions may be vented to it.
     
    n) The owner or operator using a carbon adsorption system to control air pollutant
    emissions must document that all carbon removed that is a hazardous waste and
    that is removed from the control device is managed in one of the following
    manners, regardless of the volatile organic concentration of the carbon:
     
    1) It is regenerated or reactivated in a thermal treatment unit that meets one
    of the following:
     
    A) The owner or operator of the unit has been issued a final permit
    under 35 Ill. Adm. Code 702, 703, and 705 that implements the
    requirements of Subpart X of this Part; or
     
    B) The unit is equipped with and operating air emission controls in
    accordance with the applicable requirements of Subparts AA and
    CC of this Part or Subparts AA and CC of 35 Ill. Adm. Code 725;
    or
     
    C) The unit is equipped with and operating air emission controls in
    accordance with a national emission standard for hazardous air
    pollutants under 40 CFR 61 (National Emission Standards for
    Hazardous Air Pollutants) or 40 CFR 63 (National Emission
    Standards for Hazardous Air Pollutants for Source Categories),
    each incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    2) It is incinerated in a hazardous waste incinerator for which the owner or
    operator has done either of the following:
     
    A) The owner or operator has been issued a final permit under 35 Ill.
    Adm. Code 702, 703, and 705 that implements the requirements of
    Subpart O of this Part; or
     
    B) The owner or operator has certified compliance in accordance with
    the interim status requirements of Subpart O of 35 Ill. Adm. Code
    725.
     
    3) It is burned in a boiler or industrial furnace for which the owner or

     
    395
    operator has done either of the following:
     
    A) The owner or operator has been issued a final permit under 35 Ill.
    Adm. Code 702, 703, and 705 that implements the requirements of
    Subpart H of 35 Ill. Adm. Code 726; or
     
    B) The owner or operator has designed and operates the boiler or
    industrial furnace in accordance with the interim status
    requirements of Subpart H of 35 Ill. Adm. Code 726.
     
    o) Any components of a closed-vent system that are designated, as described in
    Section 724.935(c)(9), as unsafe to monitor are exempt from the requirements of
    subsection (l)(1)(B)(ii) of this Section if both of the following conditions are
    fulfilled:
     
    1) The owner or operator of the closed-vent system has determined that the
    components of the closed-vent system are unsafe to monitor because
    monitoring personnel would be exposed to an immediate danger as a
    consequence of complying with subsection (l)(1)(B)(ii) of this Section;
    and
     
    2) The owner or operator of the closed-vent system adheres to a written plan
    that requires monitoring the closed-vent system components using the
    procedure specified in subsection (l)(1)(B)(ii) of this Section as frequently
    as practicable during safe-to-monitor times.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.934 Test Methods and Procedures
     
    a) Each owner or operator subject to the provisions of this Subpart AA must comply
    with the test methods and procedures requirements provided in this Section
     
    b) When a closed-vent system is tested for compliance with no detectable emissions,
    as required in Section 724.933(l), the test must comply with the following
    requirements:
     
    1) Monitoring must comply with Reference Method 21 (Determination of
    Volatile Organic Compound Leaks) in appendix A to 40 CFR 60 (Test
    Methods), incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(b).
     
    2) The detection instrument must meet the performance criteria of Reference
    Method 21.
     
    3) The instrument must be calibrated before use on each day of its use by the

     
    396
    procedures specified in Reference Method 21.
     
    4) Calibration gases must be as follows:
     
    A) Zero air (less than 10 ppm of hydrocarbon in air); and
     
    B) A mixture of methane or n-hexane and air at a concentration of
    approximately, but less than, 10,000 ppm methane or n-hexane.
     
    5) The background level must be determined as set forth in Reference
    Method 21.
     
    6) The instrument probe must be traversed around all potential leak
    interfaces as close to the interface as possible as described in Reference
    Method 21.
     
    7) The arithmetic difference between the maximum concentration indicated
    by the instrument and the background level is compared with 500 ppm for
    determining compliance.
     
    c) Performance tests to determine compliance with Section 724.932(a) and with the
    total organic compound concentration limit of Section 724.933(c) must comply
    with the following:
     
    1) Performance tests to determine total organic compound concentrations and
    mass flow rates entering and exiting control devices must be conducted
    and data reduced in accordance with the following reference methods and
    calculation procedures:
     
    A) Method 2 (Determination of Stack Gas Velocity and Volumetric
    Flow Rate (Type S Pitot Tube)) in appendix A to 40 CFR 60 (Test
    Methods), incorporated by reference in 35 Ill. Adm. Code
    720.111(b), for velocity and volumetric flow rate.
     
    B) Method 18 (Measurement of Gaseous Organic Compound
    Emissions by Gas Chromatography) or Method 25A
    (Determination of Total Gaseous Organic Concentration Using a
    Flame Ionization Analyzer) in appendix A to 40 CFR 60 (Test
    Methods), incorporated by reference in 35 Ill. Adm. Code
    720.111(b), for organic content. If Method 25A is used, the
    organic HAP used as the calibration gas must be the single organic
    HAP representing the largest percent by volume of the emissions.
    The use of Method 25A is acceptable if the response from the
    high-level calibration gas is at least 20 times the standard deviation
    of the response from the zero calibration gas when the instrument
    is zeroed on the most sensitive scale.

     
    397
     
    C) Each performance test must consist of three separate runs, each run
    conducted for at least one hour under the conditions that exist
    when the hazardous waste management unit is operating at the
    highest load or capacity level reasonably expected to occur. For
    the purpose of determining total organic compound concentrations
    and mass flow rates, the average of results of all runs applies. The
    average must be computed on a time-weighed basis.
     
    D) Total organic mass flow rates must be determined by the following
    equation:
     
    i) For a source using Method 18:
     
    h
    2sd
    i
    i
    -6
    E
    = Q
    x(
    n
    i = 1
    C x MW )x0.0416x10
      
    Where:
     
    Eh = The total organic mass flow rate, kg/h.
     
    Q2sd = The volumetric flow rate of gases entering
    or exiting control device, dscm/h, as
    determined by Method 2 in 40 CFR 60,
    incorporated by reference in 35 Ill. Adm.
    Code 720.111.
     
    n = The number of organic compounds in the
    vent gas.
     
    Ci = The organic concentration in ppm, dry basis,
    of compound i in the vent gas, as determined
    by Method 18 in 40 CFR 60.
     
    MWi = The molecular weight of organic compound
    i in the vent gas, kg/kg-mol.
     
    0.0416 = The conversion factor for molar volume,
    kg-mol/m
    3
    , at 293 K and 760 mm Hg.
     
    10
    -6
    = The conversion factor from ppm.
     
    ii) For a source using Method 25A:
     

     
    398
    -6
    h
    10
    0.0416
    MW
    C
    Q
      
    =
    E
    ×
    ×
    ×
    ×
      
     
    Where:
     
    Eh = The total organic mass flow rate, kg/h.
     
    Q = The volumetric flow rate of gases entering
    or exiting control device, dscm/h, as
    determined by Method 2.
     
    C = The organic concentration in ppm, dry basis,
    of compound i in the vent gas, as determined
    by Method 25A.
     
    MW = The molecular weight of propane, 44 kg/kg-
    mol.
     
    0.0416 = The conversion factor for molar volume,
    kg-mol/m
    3
    , at 293 K and 760 mm Hg.
     
    10
    -6
    = The conversion factor from ppm.
     
    E) The annual total organic emission rate must be determined by the
    following equation:
     
    A = F
    ×
    H
     
    Where:
     
    A is total organic emission rate, kg/y.
     
    F is the total organic mass flow rate, kg/h, as calculated in
    subsection (c)(1)(D) of this Section.
     
    H is the total annual hours of operation for the affected
    unit.
     
    F) Total organic emissions from all affected process vents at the
    facility must be determined by summing the hourly total organic
    mass emissions rates (F as determined in subsection (c)(1)(D) of
    this Section) and by summing the annual total organic mass
    emission rates (A as determined in subsection (c)(1)(E) of this
    Section) for all affected process vents at the facility.
     

     
    399
    2) The owner or operator must record such process information as is
    necessary to determine the conditions of the performance tests.
    Operations during periods of startup, shutdown, and malfunction do not
    constitute representative conditions for the purpose of a performance test.
     
    3) The owner or operator of an affected facility must provide, or cause to be
    provided, performance testing facilities as follows:
     
    A) Sampling ports adequate for the test methods specified in
    subsection (c)(1) of this Section.
     
    B) Safe sampling platforms.
     
    C) Safe access to sampling platforms.
     
    D) Utilities for sampling and testing equipment.
     
    4) For the purpose of making compliance determinations, the time-weighted
    average of the results of the three runs must apply. In the event that a
    sample is accidentally lost or conditions occur in which one of the three
    runs must be discontinued because of forced shutdown, failure of an
    irreplaceable portion of the sample train, extreme meteorological
    conditions or other circumstances beyond the owner or operator’s control,
    compliance may, upon the Agency’s approval, be determined using the
    average of the results of the two other runs.
     
    d) To show that a process vent associated with a hazardous waste distillation,
    fractionation, thin-film evaporation, solvent extraction, or air or steam stripping
    operation is not subject to the requirements of this Subpart AA, the owner or
    operator must make an initial determination that the time-weighted, annual
    average total organic concentration of the waste managed by the waste
    management unit is less than 10 ppmw using one of the following two methods:
     
    1) Direct measurement of the organic concentration of the waste using the
    following procedures:
     
    A) The owner or operator must take a minimum of four grab samples
    of waste for each wastestream managed in the affected unit under
    process conditions expected to cause the maximum waste organic
    concentration.
     
    B) For waste generated onsite, the grab samples must be collected at a
    point before the waste is exposed to the atmosphere such as in an
    enclosed pipe or other closed system that is used to transfer the
    waste after generation to the first affected distillation,
    fractionation, thin-film evaporation, solvent extraction, or air or

     
    400
    steam stripping operation. For waste generated offsite, the grab
    samples must be collected at the inlet to the first waste
    management unit that receives the waste provided the waste has
    been transferred to the facility in a closed system such as a tank
    truck and the waste is not diluted or mixed with other waste.
     
    C) Each sample must be analyzed and the total organic concentration
    of the sample must be computed using Method 9060 9060A (Total
    Organic Carbon) or 8260 of “Test Methods for Evaluating Solid
    Waste, Physical/Chemical Methods,” USEPA publication number
    EPA-530/SW-846, incorporated by reference under 35 Ill. Adm.
    Code 720.111 720.111(a), or analyzed for its individual
    constituents.
     
    D) The arithmetic mean of the results of the analyses of the four
    samples apply for each wastestream managed in the unit in
    determining the time-weighted, annual average total organic
    concentration of the waste. The time-weighted average is to be
    calculated using the annual quantity of each waste stream
    processed and the mean organic concentration of each wastestream
    managed in the unit.
     
    2) Using knowledge of the waste to determine that its total organic
    concentration is less than 10 ppmw. Documentation of the waste
    determination is required. Examples of documentation that must be used
    to support a determination under this subsection (d)(2) include the
    following:
     
    A) Production process information documenting that no organic
    compounds are used;
     
    B) Information that the waste is generated by a process that is
    identical to a process at the same or another facility that has
    previously been demonstrated by direct measurement to generate a
    wastestream having a total organic content less than 10 ppmw; or
     
    C) Prior speciation analysis results on the same wastestream where it
    is also documented that no process changes have occurred since
    that analysis that could affect the waste total organic concentration.
     
    e) The determination that a distillation, fractionation, thin-film evaporation, solvent
    extraction, or air or steam stripping operation that manages hazardous wastes that
    have time-weighted, annual average total organic concentrations less than 10
    ppmw must be made as follows:
     
    1) By the effective date that the facility becomes subject to the provisions of

     
    401
    this Subpart AA or by the date when the waste is first managed in a waste
    management unit, whichever is later; and either of the following:
     
    2) For continuously generated waste, annually; or
     
    3) Whenever there is a change in the waste being managed or a change in the
    process that generates or treats the waste.
     
    f) When an owner or operator and the Agency do not agree on whether a distillation,
    fractionation, thin-film evaporation, solvent extraction, or air or steam stripping
    operation manages a hazardous waste with organic concentrations of at least 10
    ppmw based on knowledge of the waste, the procedures in Method 8260 in SW-
    846, incorporated by reference in 35 Ill. Adm. Code 720.111, direct measurement
    may be used to resolve the dispute, as specified in subsection (d)(1) of this
    Section.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART BB: AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS
     
    Section 724.935 Recordkeeping Requirements
     
    a) Compliance Required.
     
    1) Each owner or operator subject to the provisions of this Subpart AA must
    comply with the recordkeeping requirements of this Section.
     
    2) An owner or operator of more than one hazardous waste management unit
    subject to the provisions of this Subpart AA may comply with the
    recordkeeping requirements for these hazardous waste management units
    in one recordkeeping system if the system identifies each record by each
    hazardous waste management unit.
     
    b) Owners and operators must record the following information in the facility
    operating record:
     
    1) For facilities that comply with the provisions of Section 724.933(a)(2), an
    implementation schedule that includes dates by which the closed-vent
    system and control device will be installed and in operation. The schedule
    must also include a rationale of why the installation cannot be completed
    at an earlier date. The implementation schedule must be in the facility
    operating record by the effective date that the facility becomes subject to
    the provisions of this Subpart AA.
     
    2) Up-to-date documentation of compliance with the process vent standards
    in Section 724.932, including the following:

     
    402
     
    A) Information and data identifying all affected process vents, annual
    throughput, and operating hours of each affected unit, estimated
    emission rates for each affected vent and for the overall facility
    (i.e., the total emissions for all affected vents at the facility), and
    the approximate location within the facility of each affected unit
    (e.g., identify the hazardous waste management units on a facility
    plot plan).
     
    B) Information and data supporting determination of vent emissions
    and emission reductions achieved by add-on control devices based
    on engineering calculations or source tests. For the purpose of
    determining compliance, determinations of vent emissions and
    emission reductions must be made using operating parameter
    values (e.g., temperatures, flow rates, or vent stream organic
    compounds and concentrations) that represent the conditions that
    result in maximum organic emissions, such as when the waste
    management unit is operating at the highest load or capacity level
    reasonably expected to occur. If the owner or operator takes any
    action (e.g., managing a waste of different composition or
    increasing operating hours of affected waste management units)
    that would result in an increase in total organic emissions from
    affected process vents at the facility, then a new determination is
    required.
     
    3) Where an owner or operator chooses to use test data to determine the
    organic removal efficiency or total organic compound concentration
    achieved by the control device, a performance test plan. The test plan
    must include the following:
     
    A) A description of how it is determined that the planned test is going
    to be conducted when the hazardous waste management unit is
    operating at the highest load or capacity level reasonably expected
    to occur. This must include the estimated or design flow rate and
    organic content of each vent stream and define the acceptable
    operating ranges of key process and control device parameters
    during the test program.
     
    B) A detailed engineering description of the closed-vent system and
    control device including the following:
     
    i) Manufacturer’s name and model number of control device;
     
    ii) Type of control device;
     
    iii) Dimensions of the control device;

     
    403
     
    iv) Capacity; and
     
    v) Construction materials.
     
    C) A detailed description of sampling and monitoring procedures,
    including sampling and monitoring locations in the system, the
    equipment to be used, sampling and monitoring frequency, and
    planned analytical procedures for sample analysis.
     
    4) Documentation of compliance with Section 724.933 must include the
    following information:
     
    A) A list of all information references and sources used in preparing
    the documentation.
     
    B) Records, including the dates of each compliance test required by
    Section 724.933(k).
     
    C) If engineering calculations are used, a design analysis,
    specifications, drawings, schematics, and piping and
    instrumentation diagrams based on the appropriate sections of
    “APTI Course 415: Control of Gaseous Emissions,” (USEPA
    publication number 450/2-81-005, incorporated by reference in 35
    Ill. Adm. Code 720.111) 720.111(a), or other engineering texts,
    approved by the Agency, that present basic control device design
    information. Documentation provided by the control device
    manufacturer or vendor that describes the control device design in
    accordance with subsections (b)(4)(C)(i) through (b)(4)(C)(vii) of
    this Section may be used to comply with this requirement. The
    design analysis must address the vent stream characteristics and
    control device operation parameters as specified below.
     
    i) For a thermal vapor incinerator, the design analysis must
    consider the vent stream composition, constituent
    concentrations and flow rate. The design analysis must
    also establish the design minimum and average temperature
    in the combustion zone and the combustion zone residence
    time.
     
    ii) For a catalytic vapor incinerator, the design analysis must
    consider the vent stream composition, constituent
    concentrations, and flow rate. The design analysis must
    also establish the design minimum and average
    temperatures across the catalyst bed inlet and outlet.
     

     
    404
    iii) For a boiler or process heater, the design analysis must
    consider the vent stream composition, constituent
    concentrations and flow rate. The design analysis must
    also establish the design minimum and average flame zone
    temperatures, combustion zone residence time and
    description of method and location where the vent stream is
    introduced into the combustion zone.
     
    iv) For a flare, the design analysis must consider the vent
    stream composition, constituent concentrations, and flow
    rate. The design analysis must also consider the
    requirements specified in Section 724.933(d).
     
    v) For a condenser, the design analysis must consider the vent
    stream composition, constituent concentrations, flow rate,
    relative humidity and temperature. The design analysis
    must also establish the design outlet organic compound
    concentration level, design average temperature of the
    condenser exhaust vent stream and design average
    temperatures of the coolant fluid at the condenser inlet and
    outlet.
     
    vi) For a carbon adsorption system such as a fixed-bed
    adsorber that regenerates the carbon bed directly onsite in
    the control device, the design analysis must consider the
    vent stream composition, constituent concentrations, flow
    rate, relative humidity and temperature. The design
    analysis must also establish the design exhaust vent stream
    organic compound concentration level, number and
    capacity of carbon beds, type and working capacity of
    activated carbon used for carbon beds, design total steam
    flow over the period of each complete carbon bed
    regeneration cycle, duration of the carbon bed steaming and
    cooling/drying cycles, design carbon bed temperature after
    regeneration, design carbon bed regeneration time and
    design service life of carbon.
     
    vii) For a carbon adsorption system such as a carbon canister
    that does not regenerate the carbon bed directly onsite in
    the control device, the design analysis must consider the
    vent stream composition, constituent concentrations, flow
    rate, relative humidity and temperature. The design
    analysis must also establish the design outlet organic
    concentration level, capacity of carbon bed, type and
    working capacity of activated carbon used for carbon bed
    and design carbon replacement interval based on the total

     
    405
    carbon working capacity of the control device and source
    operating schedule.
     
    D) A statement signed and dated by the owner or operator certifying
    that the operating parameters used in the design analysis
    reasonably represent the conditions that exist when the hazardous
    waste management unit is or would be operating at the highest load
    or capacity level reasonably expected to occur.
     
    E) A statement signed and dated by the owner or operator certifying
    that the control device is designed to operate at an efficiency of 95
    percent or greater unless the total organic concentration limit of
    Section 724.932(a) is achieved at an efficiency less than 95 weight
    percent or the total organic emission limits of Section 724.932(a)
    for affected process vents at the facility are attained by a control
    device involving vapor recovery at an efficiency less than 95
    weight percent. A statement provided by the control device
    manufacturer or vendor certifying that the control equipment meets
    the design specifications may be used to comply with this
    requirement.
     
    F) If performance tests are used to demonstrate compliance, all test
    results.
     
    c) Design documentation and monitoring operating and inspection information for
    each closed-vent system and control device required to comply with the
    provisions of this Part must be recorded and kept up-to-date in the facility
    operating record. The information must include the following:
     
    1) Description and date of each modification that is made to the closed-vent
    system or control device design.
     
    2) Identification of operating parameter, description of monitoring device,
    and diagram of monitoring sensor location or locations used to comply
    with Section 724.933(f)(1) and (f)(2).
     
    3) Monitoring, operating and inspection information required by Section
    724.933(f) through (k).
     
    4) Date, time, and duration of each period that occurs while the control
    device is operating when any monitored parameter exceeds the value
    established in the control device design analysis as specified below:
     
    A) For a thermal vapor incinerator designed to operate with a
    minimum residence time of 0.50 second at a minimum temperature
    of 760° C, any period when the combustion temperature is below

     
    406
    760° C.
     
    B) For a thermal vapor incinerator designed to operate with an
    organic emission reduction efficiency of 95 weight percent or
    greater, any period when the combustion zone temperature is more
    than 28° C below the design average combustion zone temperature
    established as a requirement of subsection (b)(4)(C)(i) of this
    Section.
     
    C) For a catalytic vapor incinerator, any period when:
     
    i) Temperature of the vent stream at the catalyst bed inlet is
    more than 28° C below the average temperature of the inlet
    vent stream established as a requirement of subsection
    (b)(4)(C)(ii) of this Section; or
     
    ii) Temperature difference across the catalyst bed is less than
    80% of the design average temperature difference
    established as a requirement of subsection (b)(4)(C)(ii) of
    this Section.
     
    D) For a boiler or process heater, any period when either of the
    following occurs:
     
    i) Flame zone temperature is more than 28° C below the
    design average flame zone temperature established as a
    requirement of subsection (b)(4)(C)(iii) of this Section; or
     
    ii) Position changes where the vent stream is introduced to the
    combustion zone from the location established as a
    requirement of subsection (b)(4)(C)(iii) of this Section.
     
    E) For a flare, period when the pilot flame is not ignited.
     
    F) For a condenser that complies with Section 724.933(f)(2)(F)(i),
    any period when the organic compound concentration level or
    readings of organic compounds in the exhaust vent stream from the
    condenser are more than 20 percent greater than the design outlet
    organic compound concentration level established as a requirement
    of subsection (b)(4)(C)(v) of this Section.
     
    G) For a condenser that complies with Section 724.933(f)(2)(F)(ii),
    any period when the following occurs:
     
    i) Temperature of the exhaust vent stream from the condenser
    is more than 6° C above the design average exhaust vent

     
    407
    stream temperature established as a requirement of
    subsection (b)(4)(C)(v) of this Section.
     
    ii) Temperature of the coolant fluid exiting the condenser is
    more than 6° C above the design average coolant fluid
    temperature at the condenser outlet established as a
    requirement of subsection (b)(4)(C)(v) of this Section.
     
    H) For a carbon adsorption system such as a fixed-bed carbon
    adsorber that regenerates the carbon bed directly onsite in the
    control device and complies with Section 724.933(f)(2)(G)(i), any
    period when the organic compound concentration level or readings
    of organic compounds in the exhaust vent stream from the carbon
    bed are more than 20 percent greater than the design exhaust vent
    stream organic compound concentration level established as a
    requirement of subsection (b)(4)(C)(vi) of this Section.
     
    I) For a carbon adsorption system such as a fixed-bed carbon
    adsorber that regenerates the carbon bed directly onsite in the
    control device and complies with Section 724.933(f)(2)(G)(ii), any
    period when the vent stream continues to flow through the control
    device beyond the predetermined carbon bed regeneration time
    established as a requirement of subsection (b)(4)(C)(vi) of this
    Section.
     
    5) Explanation for each period recorded under subsection (c)(4) of this
    Section of the cause for control device operating parameter exceeding the
    design value and the measures implemented to correct the control device
    operation.
     
    6) For a carbon adsorption system operated subject to requirements specified
    in Section 724.933(g) or (h)(2), any date when existing carbon in the
    control device is replaced with fresh carbon.
     
    7) For a carbon adsorption system operated subject to requirements specified
    in Section 724.933(h)(1), a log that records the following:
     
    A) Date and time when control device is monitored for carbon
    breakthrough and the monitoring device reading; and
     
    B) Date when existing carbon in the control device is replaced with
    fresh carbon.
     
    8) Date of each control device startup and shutdown.
     
    9) An owner or operator designating any components of a closed-vent system

     
    408
    as unsafe to monitor pursuant to Section 724.933(o) must record in a log
    that is kept in the facility operating record the identification of closed-vent
    system components that are designated as unsafe to monitor in accordance
    with the requirements of Section 724.933(o), an explanation for each
    closed-vent system component stating why the closed-vent system
    component is unsafe to monitor, and the plan for monitoring each closed-
    vent system component.
     
    10) When each leak is detected, as specified in Section 724.933(l), the
    following information must be recorded:
     
    A) The instrument identification number; the closed-vent system
    component identification number; and the operator name, initials,
    or identification number.
     
    B) The date the leak was detected and the date of first attempt to
    repair the leak.
     
    C) The date of successful repair of the leak.
     
    D) Maximum instrument reading measured by Method 21
    (Determination of Volatile Organic Compound Leaks) of appendix
    A to 40 CFR 60, appendix A (Test Methods), incorporated by
    reference in 35 Ill. Adm. Code 720.111 720.111(b), after it is
    successfully repaired or determined to be nonrepairable.
     
    E) “Repair delayed” and the reason for the delay if a leak is not
    repaired within 15 calendar days after discovery of the leak.
     
    i) The owner or operator may develop a written procedure
    that identifies the conditions that justify a delay of repair.
    In such cases, reasons for delay of repair may be
    documented by citing the relevant sections of the written
    procedure.
     
    ii) If delay of repair was caused by depletion of stocked parts,
    there must be documentation that the spare parts were
    sufficiently stocked on-site before depletion and the reason
    for depletion.
     
    d) Records of the monitoring, operating, and inspection information required by
    subsections (c)(3) through (c)(10) of this Section must be kept at least three years
    following the date of each occurrence, measurement, corrective action, or record.
     
    e) For a control device other than a thermal vapor incinerator, catalytic vapor
    incinerator, flare, boiler, process heater, condenser, or carbon adsorption system,

     
    409
    the Agency must specify the appropriate recordkeeping requirements.
     
    f) Up-to-date information and data used to determine whether or not a process vent
    is subject to the requirements in Section 724.932, including supporting
    documentation as required by Section 724.934(d)(2), when application of the
    knowledge of the nature of the hazardous wastestream or the process by which it
    was produced is used, must be recorded in a log that is kept in the facility
    operating record.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART BB: AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS
     
    Section 724.950 Applicability
     
    a) The regulations in this Subpart BB apply to owners and operators of facilities that
    treat, store, or dispose of hazardous wastes (except as provided in Section
    724.101).
     
    b) Except as provided in Section 724.964(k), this Subpart BB applies to equipment
    that contains or contacts hazardous wastes with organic concentrations of at least
    10 percent by weight that are managed in one of the following:
     
    1) A unit that is subject to the RCRA permitting requirements of 35 Ill. Adm.
    Code 702, 703, and 705,
     
    2) A unit (including a hazardous waste recycling unit) that is not exempt
    from permitting under the provisions of 35 Ill. Adm. Code 722.134(a)
    (i.e., a hazardous waste recycling unit that is not a “90-day” tank or
    container) and that is located at a hazardous waste management facility
    otherwise subject to the permitting requirements of 35 Ill. Adm. Code 702,
    703, and 705, or
     
    3) A unit that is exempt from permitting under the provisions of 35 Ill. Adm.
    Code 722.134(a) (i.e., a “90-day” tank or container) and which is not a
    recycling unit under the provisions of 35 Ill. Adm. Code 721.106.
     
    c) For the owner or operator of a facility subject to this Subpart BB that received a
    final permit under 35 Ill. Adm. Code 702, 703, and 705 prior to December 6,
    1996, the requirements of this Subpart BB must be incorporated into the permit
    when the permit is reissued, renewed, or modified in accordance with the
    requirements of 35 Ill. Adm. Code 703 and 705. Until such date when the owner
    or operator receives a final permit incorporating the requirements of this Subpart
    BB, the owner or operator is subject to the requirements of Subpart BB of 35 Ill.
    Adm. Code 725.
     

     
    410
    d) Each piece of equipment to which this Subpart BB applies must be marked in
    such a manner that it can be distinguished readily from other pieces of equipment.
     
    e) Equipment that is in vacuum service is excluded from the requirements of
    Sections 724.952 to 724.960, if it is identified as required in Section
    724.964(g)(5).
     
    f) Equipment that contains or contacts hazardous waste with an organic
    concentration of at least 10 percent by weight for less than 300 hours per calendar
    year is excluded from the requirements of Sections 724.952 through 724.960 if it
    is identified as required in Section 724.964(g)(6).
     
    g) This subsection (g) corresponds with 40 CFR 264.1050(g), which relates
    exclusively to a facility outside Illinois. This statement maintains structural
    consistency with the corresponding federal regulations.
     
    h) Purged coatings and solvents from surface coating operations subject to the
    federal national emission standards for hazardous air pollutants (NESHAPs) for
    the surface coating of automobiles and light-duty trucks at Subpart IIII of 40 CFR
    63, incorporated by reference in 35 Ill. Adm. Code 720.111(b), (National
    Emission Standards for Hazardous Air Pollutants: Surface Coating of
    Automobiles and Light-Duty Trucks) are not subject to the requirements of this
    Subpart BB.
     
    BOARD NOTE: The requirements of Sections 724.952 through 724.965 apply to equipment
    associated with hazardous waste recycling units previously exempt under 35 Ill. Adm. Code
    721.106(c)(1). Other exemptions under 35 Ill. Adm. Code 721.104 and 724.101(g) are not
    affected by these requirements.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.963 Test Methods and Procedures
     
    a) Each owner or operator subject to the provisions of this Subpart BB must comply
    with the test methods and procedures requirements provided in this Section.
     
    b) Leak detection monitoring, as required in Sections 724.952 through 724.962,
    must comply with the following requirements:
     
    1) Monitoring must comply with Reference Method 21 (Determination of
    Volatile Organic Compound Leaks) in appendix A to 40 CFR 60 (Test
    Methods), incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(b).
     
    2) The detection instrument must meet the performance criteria of Reference
    Method 21.

     
    411
     
    3) The instrument must be calibrated before use on each day of its use by the
    procedures specified in Reference Method 21.
     
    4) Calibration gases must be as follows:
     
    A) Zero air (less than 10 ppm of hydrocarbon in air); and
     
    B) A mixture of methane or n-hexane and air at a concentration of
    approximately, but less than 10,000 ppm methane or n-hexane.
     
    5) The instrument probe must be traversed around all potential leak
    interfaces as close to the interface as possible as described in Reference
    Method 21.
     
    c) When equipment is tested for compliance with no detectable emissions, as
    required in Sections 724.952(e), 724.953(i), 724.954, and 724.957(f), the test
    must comply with the following requirements:
     
    1) The requirements of subsections (b)(1) through (b)(4) of this Section
    apply.
     
    2) The background level must be determined as set forth in Reference
    Method 21.
     
    3) The instrument probe must be traversed around all potential leak
    interfaces as close to the interface as possible as described in Reference
    Method 21.
     
    4) This arithmetic difference between the maximum concentration indicated
    by the instrument and the background level is compared with 500 ppm for
    determining compliance.
     
    d) In accordance with the waste analysis plan required by Section 724.113(b), an
    owner or operator of a facility must determine, for each piece of equipment,
    whether the equipment contains or contacts a hazardous waste with organic
    concentration that equals or exceeds 10 percent by weight using the following:
     
    1) Methods described in ASTM Methods D 2267-88 (Standard Test Method
    for Aromatics in Light Naphthas and Aviation Gasolines by Gas
    Chromatography), E 168-88 (Standard Practices for General Techniques
    of Infrared Quantitative Analysis), E 169-87 (Standard Practices for
    General Techniques of Ultraviolet-Visible Quantitative Analysis), and or
    E 260-85 (Standard Practice for Packed Column Gas Chromatography),
    each incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(a);
     

     
    412
    2) Method 9060 or 8260 9060A (Total Organic Carbon) of “Test Methods
    for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    publication number EPA-530/SW-846, incorporated by reference in 35 Ill.
    Adm. Code 720.111 720.111(a), for computing total organic concentration
    of the sample, or analyzed for its individual constituents; or
     
    3) Application of the knowledge of the nature of the hazardous wastestream
    or the process by which it was produced. Documentation of a waste
    determination by knowledge is required. Examples of documentation that
    must be used to support a determination under this provision include
    production process information documenting that no organic compounds
    are used, information that the waste is generated by a process that is
    identical to a process at the same or another facility that has previously
    been demonstrated by direct measurement to have a total organic content
    less than 10 percent, or prior speciation analysis results on the same
    wastestream where it is also documented that no process changes have
    occurred since that analysis that could affect the waste total organic
    concentration.
     
    e) If an owner or operator determines that a piece of equipment contains or contacts
    a hazardous waste with organic concentrations at least 10 percent by weight, the
    determination can be revised only after following the procedures in subsection
    (d)(1) or (d)(2) of this Section.
     
    f) When an owner or operator and the Agency do not agree on whether a piece of
    equipment contains or contacts a hazardous waste with organic concentrations at
    least 10 percent by weight, the procedures in subsection (d)(1) or (d)(2) of this
    Section must be used to resolve the dispute.
     
    g) Samples used in determining the percent organic content must be representative
    of the highest total organic content hazardous waste that is expected to be
    contained in or contact the equipment.
     
    h) To determine if pumps or valves are in light liquid service, the vapor pressures of
    constituents must either be obtained from standard reference texts or be
    determined by ASTM D 2879-92 (Standard Test Method for Vapor Pressure-
    Temperature Relationship and Initial Decomposition Temperature of Liquids by
    Isoteniscope), incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(a).
     
    i) Performance tests to determine if a control device achieves 95 weight percent
    organic emission reduction must comply with the procedures of Section
    724.934(c)(1) through (c)(4).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    413
    Section 724.964 Recordkeeping Requirements
     
    a) Lumping Units.
     
    1) Each owner or operator subject to the provisions of this Subpart BB must
    comply with the recordkeeping requirements of this Section.
     
    2) An owner or operator of more than one hazardous waste management unit
    subject to the provisions of this Subpart BB may comply with the
    recordkeeping requirements for these hazardous waste management units
    in one recordkeeping system if the system identifies each record by each
    hazardous waste management unit.
     
    b) Owners and operators must record the following information in the facility
    operating record:
     
    1) For each piece of equipment to which this Subpart BB applies, the
    following:
     
    A) Equipment identification number and hazardous waste
    management unit identification.
     
    B) Approximate locations within the facility (e.g., identify the
    hazardous waste management unit on a facility plot plan).
     
    C) Type of equipment (e.g., a pump or pipeline valve).
     
    D) Percent-by-weight total organics in the hazardous wastestream at
    the equipment.
     
    E) Hazardous waste state at the equipment (e.g., gas-vapor or liquid).
     
    F) Method of compliance with the standard (e.g., “monthly leak
    detection and repair” or “equipped with dual mechanical seals”).
     
    2) For facilities that comply with the provisions of Section 724.933(a)(2), an
    implementation schedule, as specified in that Section.
     
    3) Where an owner or operator chooses to use test data to demonstrate the
    organic removal efficiency or total organic compound concentration
    achieved by the control device, a performance test plan, as specified in
    Section 724.935(b)(3).
     
    4) Documentation of compliance with Section 724.960, including the
    detailed design documentation or performance test results specified in
    Section 724.935(b)(4).

     
    414
     
    c) When each leak is detected as specified in Sections 724.952, 724.953, 724.957, or
    724.958, the following requirements apply:
     
    1) A weatherproof and readily visible identification, marked with the
    equipment identification number, the date evidence of a potential leak was
    found in accordance with Section 724.958(a), and the date the leak was
    detected, must be attached to the leaking equipment.
     
    2) The identification on equipment except on a valve, may be removed after
    it has been repaired.
     
    3) The identification on a valve may be removed after it has been monitored
    for two successive months as specified in Section 724.957(c) and no leak
    has been detected during those two months.
     
    d) When each leak is detected as specified in Section 724.952, 724.953, 724.957, or
    724.958, the following information must be recorded in an inspection log and
    must be kept in the facility operating record:
     
    1) The instrument and operator identification numbers and the equipment
    identification number.
     
    2) The date evidence of a potential leak was found in accordance with
    Section 724.958(a).
     
    3) The date the leak was detected and the dates of each attempt to repair the
    leak.
     
    4) Repair methods applied in each attempt to repair the leak.
     
    5) “Above 10,000,” if the maximum instrument reading measured by the
    methods specified in Section 724.963(b) after each repair attempt is equal
    to or greater than 10,000 ppm.
     
    6) “Repair delayed” and the reason for the delay if a leak is not repaired
    within 15 calendar days after discovery of the leak.
     
    7) Documentation supporting the delay of repair of a valve in compliance
    with Section 724.959(c).
     
    8) The signature of the owner or operator (or designate) whose decision it
    was that repair could not be effected without a hazardous waste
    management unit shutdown.
     
    9) The expected date of successful repair of the leak if a leak is not repaired

     
    415
    within 15 calendar days.
     
    10) The date of successful repair of the leak.
     
    e) Design documentation and monitoring, operating, and inspection information for
    each closed-vent system and control device required to comply with the
    provisions of Section 724.960 must be recorded and kept up-to-date in the facility
    operating record, as specified in Section 724.935(c)(1) and (c)(2), and monitoring,
    operating and inspection information in Section 724.935(c)(3) through (c)(8).
     
    f) For a control device other than a thermal vapor incinerator, catalytic vapor
    incinerator, flare, boiler, process heater, condenser, or carbon adsorption system,
    the Agency must specify the appropriate recordkeeping requirements, indicating
    proper operation and maintenance of the control device, in the RCRA permit.
     
    g) The following information pertaining to all equipment subject to the requirements
    in Sections 724.952 through 724.960 must be recorded in a log that is kept in the
    facility operating record:
     
    1) A list of identification numbers for equipment (except welded fittings)
    subject to the requirements of this Subpart BB.
     
    2) List of Equipment
     
    A) A list of identification numbers for equipment that the owner or
    operator elects to designate for no detectable emissions, as
    indicated by an instrument reading of less than 500 ppm above
    background, under the provisions of Sections 724.952(e),
    724.953(i) and 724.957(f).
     
    B) The designation of this equipment as subject to the requirements of
    Section 724.952(e), 724.953(i), or 724.957(f) must be signed by
    the owner or operator.
     
    3) A list of equipment identification numbers for pressure relief devices
    required to comply with Section 724.954(a).
     
    4) Compliance tests.
     
    A) The dates of each compliance test required in Sections 724.952(e),
    724.953(i), 724.954, and 724.957(f).
     
    B) The background level measured during each compliance test.
     
    C) The maximum instrument reading measured at the equipment
    during each compliance test.

     
    416
     
    5) A list of identification numbers for equipment in vacuum service.
     
    6) Identification, either by list or location (area or group), of equipment that
    contains or contacts hazardous waste with an organic concentration of at
    least 10 percent by weight for less than 300 hours per year.
     
    h) The following information pertaining to all valves subject to the requirements of
    Section 724.957(g) and (h) must be recorded in a log that is kept in the facility
    operating record:
     
    1) A list of identification numbers for valves that are designated as unsafe to
    monitor, an explanation for each valve stating why the valve is unsafe to
    monitor, and the plan for monitoring each valve.
     
    2) A list of identification numbers for valves that are designated as difficult
    to monitor, an explanation for each valve stating why the valve is difficult
    to monitor, and the planned schedule for monitoring each valve.
     
    i) The following information must be recorded in the facility operating record for
    valves complying with Section 724.962:
     
    1) A schedule of monitoring.
     
    2) The percent of valves found leaking during each monitoring period.
     
    j) The following information must be recorded in a log that is kept in the facility
    operating record:
     
    1) Criteria required in Sections 724.952(d)(5)(B) and 724.953(e)(2) and an
    explanation of the design criteria.
     
    2) Any changes to these criteria and the reasons for the changes.
     
    k) The following information must be recorded in a log that is kept in the facility
    operating record for use in determining exemptions, as provided in Section
    724.950 and other specific Subparts:
     
    1) An analysis determining the design capacity of the hazardous waste
    management unit.
     
    2) A statement listing the hazardous waste influent to and effluent from each
    hazardous waste management unit subject to the requirements in Section
    724.960 and an analysis determining whether these hazardous wastes are
    heavy liquids.
     

     
    417
    3) An up-to-date analysis and the supporting information and data used to
    determine whether or not equipment is subject to the requirements in
    Sections 724.952 through 724.960. The record must include supporting
    documentation as required by Section 724.963(d)(3) when application of
    the knowledge of the nature of the hazardous wastestream or the process
    by which it was produced is used. If the owner or operator takes any
    action (e.g., changing the process that produced the waste) that could
    result in an increase in the total organic content of the waste contained in
    or contacted by equipment determined not to be subject to the
    requirements in Sections 724.952 through 724.960, then a new
    determination is required.
     
    l) Records of the equipment leak information required by subsection (d) of this
    Section and the operating information required by subsection (e) of this Section
    need be kept only three years.
     
    m) The owner or operator of any facility with equipment that is subject to this
    Subpart BB and to regulations at federal 40 CFR 60 (Standards of Performance
    for New Stationary Sources), 61 (National Emission Standards for Hazardous Air
    Pollutants), or 63 (National Emission Standards for Hazardous Air Pollutants for
    Source Categories), incorporated by reference in 35 Ill. Adm. Code 720.111, may
    elect to determine compliance with this Subpart BB by documentation of
    compliance either pursuant to Section 724.964 or by documentation of
    compliance with the regulations at 40 CFR 60, 61, or 63, pursuant to the relevant
    provisions of 40 CFR 60, 61, or 63, each incorporated by reference in 35 Ill.
    Adm. Code 720.111(b). The documentation of compliance under the regulation
    at 40 CFR 60, 61, or 63 must be kept with or made readily available with the
    facility operating record.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE
    IMPOUNDMENTS, AND CONTAINERS
     
    Section 724.980 Applicability
     
    a) The requirements of this Subpart CC apply to owners and operators of all
    facilities that treat, store, or dispose of hazardous waste in tanks, surface
    impoundments, or containers subject to Subpart I, J, or K of this Part, except as
    Section 724.101 and subsection (b) of this Section provide otherwise.
     
    b) The requirements of this Subpart CC do not apply to the following waste
    management units at the facility:
     
    1) A waste management unit that holds hazardous waste placed in the unit
    before December 6, 1996, and in which no hazardous waste is added to the

     
    418
    unit on or after December 6, 1996.
     
    2) A container that has a design capacity less than or equal to 0.1 m
    3
    (3.5 ft
    3
     
    or 26.4 gal).
     
    3) A tank in which an owner or operator has stopped adding hazardous waste
    and the owner or operator has begun implementing or completed closure
    pursuant to an approved closure plan.
     
    4) A surface impoundment in which an owner or operator has stopped adding
    hazardous waste (except to implement an approved closure plan) and the
    owner or operator has begun implementing or completed closure pursuant
    to an approved closure plan.
     
    5) A waste management unit that is used solely for on-site treatment or
    storage of hazardous waste that is placed in the unit as a result of
    implementing remedial activities required pursuant to the Act or Board
    regulations or under the corrective action authorities of RCRA section
    3004(u), 3004(v), or 3008(h); CERCLA authorities; or similar federal or
    State authorities.
     
    6) A waste management unit that is used solely for the management of
    radioactive mixed waste in accordance with all applicable regulations
    under the authority of the Atomic Energy Act of 1954 (42 USC 2011 et
    seq.) and the Nuclear Waste Policy Act of 1982 (42 USC 10101 et seq.).
     
    7) A hazardous waste management unit that the owner or operator certifies is
    equipped with and operating air emission controls in accordance with the
    requirements of an applicable federal Clean Air Act regulation codified
    under 40 CFR 60 (Standards of Performance for New Stationary Sources),
    61 (National Emission Standards for Hazardous Air Pollutants), or 63
    (National Emission Standards for Hazardous Air Pollutants for Source
    Categories). For the purpose of complying with this subsection (b)(7), a
    tank for which the air emission control includes an enclosure, as opposed
    to a cover, must be in compliance with the enclosure and control device
    requirements of Section 724.984(i), except as provided in Section
    724.982(c)(5).
     
    8) A tank that has a process vent, as defined in 35 Ill. Adm. Code 724.931.
     
    c) For the owner and operator of a facility subject to this Subpart CC and that
    received a final RCRA permit prior to December 6, 1996, the requirements of this
    Subpart CC must be incorporated into the permit when the permit is reissued,
    renewed, or modified in accordance with the requirements of 35 Ill. Adm. Code
    703 and 705. Until the date when the owner and operator receives a final permit
    incorporating the requirements of this Subpart CC, the owner and operator are

     
    419
    subject to the requirements of Subpart CC of 35 Ill. Adm. Code 725.
     
    d) The requirements of this Subpart CC, except for the recordkeeping requirements
    specified in Section 724.989(i), are stayed for a tank or container used for the
    management of hazardous waste generated by organic peroxide manufacturing
    and its associated laboratory operations, when the owner or operator of the unit
    meets all of the following conditions:
     
    1) The owner or operator identifies that the tank or container receives
    hazardous waste generated by an organic peroxide manufacturing process
    producing more than one functional family of organic peroxides or
    multiple organic peroxides within one functional family, that one or more
    of these organic peroxides could potentially undergo self-accelerating
    thermal decomposition at or below ambient temperatures, and that organic
    peroxides are the predominant products manufactured by the process. For
    the purposes of this subsection (d), “organic peroxide” means an organic
    compound that contains the bivalent -O-O- structure and which may be
    considered to be a structural derivative of hydrogen peroxide where one or
    both of the hydrogen atoms has been replaced by an organic radical.
     
    2) The owner or operator prepares documentation, in accordance with
    Section 724.989(i), explaining why an undue safety hazard would be
    created if air emission controls specified in Sections 724.984 through
    724.987 are installed and operated on the tanks and containers used at the
    facility to manage the hazardous waste generated by the organic peroxide
    manufacturing process or processes meeting the conditions of subsection
    (d)(1) of this Section.
     
    3) The owner or operator notifies the Agency in writing that hazardous waste
    generated by an organic peroxide manufacturing process or processes
    meeting the conditions of subsection (d)(1) of this Section are managed at
    the facility in tanks or containers meeting the conditions of subsection
    (d)(2) of this Section. The notification must state the name and address of
    the facility and be signed and dated by an authorized representative of the
    facility owner or operator.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.982 Standards: General
     
    a) This Section applies to the management of hazardous waste in tanks, surface
    impoundments, and containers subject to this Subpart CC.
     
    b) The owner or operator must control air pollutant emissions from each waste
    management unit in accordance with the standards specified in Sections 724.984
    through 724.987, as applicable to the waste management unit, except as provided

     
    420
    for in subsection (c) of this Section.
     
    c) A tank, surface impoundment, or container is exempt from standards specified in
    Sections 724.984 through 724.987, as applicable, provided that all hazardous
    waste placed in the waste management unit is one of the following:
     
    1) A tank, surface impoundment, or container for which all hazardous waste
    entering the unit has an average VO concentration at the point of waste
    origination of less than 500 parts per million by weight (ppmw). The
    average VO concentration must be determined by the procedures specified
    in Section 724.983(a). The owner or operator must review and update, as
    necessary, this determination at least once every 12 months following the
    date of the initial determination for the hazardous waste streams entering
    the unit.
     
    2) A tank, surface impoundment, or container for which the organic content
    of all the hazardous waste entering the waste management unit has been
    reduced by an organic destruction or removal process that achieves any
    one of the following conditions:
     
    A) The process removes or destroys the organics contained in the
    hazardous waste to a level such that the average VO concentration
    of the hazardous waste at the point of waste treatment is less than
    the exit concentration limit (Ct) established for the process. The
    average VO concentration of the hazardous waste at the point of
    waste treatment and the exit concentration limit for the process
    must be determined using the procedures specified in Section
    724.983(b).
     
    B) The process removes or destroys the organics contained in the
    hazardous waste to a level such that the organic reduction
    efficiency (R) for the process is equal to or greater than 95 percent,
    and the average VO concentration of the hazardous waste at the
    point of waste treatment is less than 100 ppmw. The organic
    reduction efficiency for the process and the average VO
    concentration of the hazardous waste at the point of waste
    treatment must be determined using the procedures specified in
    Section 724.983(b).
     
    C) The process removes or destroys the organics contained in the
    hazardous waste to such a level that the actual organic mass
    removal rate (MR) for the process is equal to or greater than the
    required organic mass removal rate (RMR) established for the
    process. The required organic mass removal rate and the actual
    organic mass removal rate for the process must be determined
    using the procedures specified in Section 724.983(b).

     
    421
     
    D) The process is a biological process that destroys or degrades the
    organics contained in the hazardous waste so that either of the
    following conditions are met:
     
    i) The organic reduction efficiency (R) for the process is
    equal to or greater than 95 percent, and the organic
    biodegradation efficiency (Rbio) for the process is equal to
    or greater than 95 percent. The organic reduction
    efficiency and the organic biodegradation efficiency for the
    process must be determined using the procedures specified
    in Section 724.983(b).
     
    ii) The total actual organic mass biodegradation rate (MRbio)
    for all hazardous waste treated by the process is equal to or
    greater than the required organic mass removal rate (RMR).
    The required organic mass removal rate and the actual
    organic mass biodegradation rate for the process must be
    determined using the procedures specified in Section
    724.983(b).
     
    E) The process removes or destroys the organics contained in the
    hazardous waste and meets all of the following conditions:
     
    i) From the point of waste origination through the point
    where the hazardous waste enters the treatment process, the
    hazardous waste is continuously managed in waste
    management units that use air emission controls in
    accordance with the standards specified in Sections
    724.984 through 724.987, as applicable to the waste
    management unit.
     
    ii) From the point of waste origination through the point
    where the hazardous waste enters the treatment process,
    any transfer of the hazardous waste is accomplished
    through continuous hard-piping or other closed system
    transfer that does not allow exposure of the waste to the
    atmosphere.
     
    BOARD NOTE: The USEPA considers a drain system that
    meets the requirements of federal subpart RR of 40 CFR
    63, subpart RR, “(National Emission Standards for
    Individual Drain Systems,”) to be a closed system.
     
    iii) The average VO concentration of the hazardous waste at
    the point of waste treatment is less than the lowest average

     
    422
    VO concentration at the point of waste origination,
    determined for each of the individual hazardous waste
    streams entering the process or 500 ppmw, whichever value
    is lower. The average VO concentration of each individual
    hazardous waste stream at the point of waste origination
    must be determined using the procedures specified in
    Section 724.983(a). The average VO concentration of the
    hazardous waste at the point of waste treatment must be
    determined using the procedures specified in Section
    724.983(b).
     
    F) A process that removes or destroys the organics contained in the
    hazardous waste to a level such that the organic reduction
    efficiency (R) for the process is equal to or greater than 95 percent
    and the owner or operator certifies that the average VO
    concentration at the point of waste origination for each of the
    individual waste streams entering the process is less than 10,000
    ppmw. The organic reduction efficiency for the process and the
    average VO concentration of the hazardous waste at the point of
    waste origination must be determined using the procedures
    specified in Section 724.983(b) and Section 724.983(a),
    respectively.
     
    G) A hazardous waste incinerator for which either of the following
    conditions is true:
     
    i) The owner or operator has been issued a final permit under
    35 Ill. Adm. Code 702, 703, and 705 that implements the
    requirements of Subpart H of 35 Ill. Adm. Code 726; or
     
    ii) The owner or operator has designed and operates the
    incinerator in accordance with the interim status
    requirements of Subpart O of 35 Ill. Adm. Code 725.
     
    H) A boiler or industrial furnace for which either of the following
    conditions is true:
     
    i) The owner or operator has been issued a final permit under
    35 Ill. Adm. Code 702, 703, and 705 that implements the
    requirements of Subpart H of 35 Ill. Adm. Code 726; or
     
    ii) The owner or operator has designed and operates the boiler
    or industrial furnace in accordance with the interim status
    requirements of Subpart O of 35 Ill. Adm. Code 725.
     
    I) For the purpose of determining the performance of an organic

     
    423
    destruction or removal process in accordance with the conditions
    in each of subsections (c)(2)(A) through (c)(2)(F) of this Section,
    the owner or operator must account for VO concentrations
    determined to be below the limit of detection of the analytical
    method by using the following VO concentration:
     
    i) If Method 25D (Determination of the Volatile Organic
    Concentration of Waste Samples) in appendix A to 40 CFR
    60, appendix A (Test Methods), incorporated by reference
    in 35 Ill. Adm. Code 720.111 720.111(b), is used for the
    analysis, one-half the blank value determined in Section
    4.4 of the method or a value of 25 ppmw, whichever is less.
     
    ii) If any other analytical method is used, one-half the sum of
    the limits of detection established for each organic
    constituent in the waste that has a Henry’s law constant
    value at least 0.1 mole-fraction-in-the-gas-phase/mole-
    fraction-in-the-liquid-phase (0.1 Y/X) (which can also be
    expressed as 1.8 x 10
    -6
    atmospheres/gram-mole/m
    3
    ) at 25°
    C.
     
    3) A tank or surface impoundment used for biological treatment of hazardous
    waste in accordance with the requirements of subsection (c)(2)(D) of this
    Section.
     
    4) A tank, surface impoundment, or container for which all hazardous waste
    placed in the unit fulfills either of the following conditions:
     
    A) It meets the numerical concentration limits for organic hazardous
    constituents, applicable to the hazardous waste, as specified in
    Table T to 35 Ill. Adm. Code 728; or
     
    B) The organic hazardous constituents in the waste have been treated
    by the treatment technology established by USEPA for the waste,
    as set forth in 35 Ill. Adm. Code 728.142(a), or have been removed
    or destroyed by an equivalent method of treatment approved by the
    Agency pursuant to 35 Ill. Adm. Code 728.142(b).
     
    5) A tank used for bulk feed of hazardous waste to a waste incinerator and all
    of the following conditions are met:
     
    A) The tank is located inside an enclosure vented to a control device
    that is designed and operated in accordance with all applicable
    requirements specified under federal subpart FF of 40 CFR 61,
    subpart FF, “(National Emission Standard for Benzene Waste
    Operations),” incorporated by reference in 35 Ill. Adm. Code

     
    424
    720.111 720.111(b), for a facility at which the total annual benzene
    quantity from the facility waste is equal to or greater than 10
    megagrams (11 tons) per year;
     
    B) The enclosure and control device serving the tank were installed
    and began operation prior to November 25, 1996; and
     
    C) The enclosure is designed and operated in accordance with the
    criteria for a permanent total enclosure as specified in “Procedure
    T--Criteria for and Verification of a Permanent or Temporary Total
    Enclosure” under appendix B to 40 CFR 52.741, appendix B
    (VOM Measurement Techniques for Capture Efficiency),
    incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(b). The enclosure may have permanent or temporary
    openings to allow worker access; passage of material into or out of
    the enclosure by conveyor, vehicles, or other mechanical or
    electrical equipment; or to direct air flow into the enclosure. The
    owner or operator must perform the verification procedure for the
    enclosure as specified in Section 5.0 to “Procedure T--Criteria for
    and Verification of a Permanent or Temporary Total Enclosure”
    annually.
     
    d) The Agency may at any time perform or request that the owner or operator
    perform a waste determination for a hazardous waste managed in a tank, surface
    impoundment, or container that is exempted from using air emission controls
    under the provisions of this Section, as follows:
     
    1) The waste determination for average VO concentration of a hazardous
    waste at the point of waste origination must be performed using direct
    measurement in accordance with the applicable requirements of Section
    724.983(a). The waste determination for a hazardous waste at the point of
    waste treatment must be performed in accordance with the applicable
    requirements of Section 724.983(b).
     
    2) In performing a waste determination pursuant to subsection (d)(1) of this
    Section, the sample preparation and analysis must be conducted as
    follows:
     
    A) In accordance with the method used by the owner or operator to
    perform the waste analysis, except in the case specified in
    subsection (d)(2)(B) of this Section.
     
    B) If the Agency determines that the method used by the owner or
    operator was not appropriate for the hazardous waste managed in
    the tank, surface impoundment, or container, then the Agency may
    choose an appropriate method.

     
    425
     
    3) Where the owner or operator is requested to perform the waste
    determination, the Agency may elect to have an authorized representative
    observe the collection of the hazardous waste samples used for the
    analysis.
     
    4) Where the results of the waste determination performed or requested by
    the Agency do not agree with the results of a waste determination
    performed by the owner or operator using knowledge of the waste, then
    the results of the waste determination performed in accordance with the
    requirements of subsection (d)(1) of this Section must be used to establish
    compliance with the requirements of this Subpart CC.
     
    5) Where the owner or operator has used an averaging period greater than
    one hour for determining the average VO concentration of a hazardous
    waste at the point of waste origination, the Agency may elect to establish
    compliance with this Subpart CC by performing or requesting that the
    owner or operator perform a waste determination using direct
    measurement based on waste samples collected within a one-hour period,
    as follows:
     
    A) The average VO concentration of the hazardous waste at the point
    of waste origination must be determined by direct measurement in
    accordance with the requirements of Section 724.983(a).
     
    B) Results of the waste determination performed or requested by the
    Agency showing that the average VO concentration of the
    hazardous waste at the point of waste origination is equal to or
    greater than 500 ppmw must constitute noncompliance with this
    Subpart CC, except in a case as provided for in subsection
    (d)(5)(C) of this Section.
     
    C) Where the average VO concentration of the hazardous waste at the
    point of waste origination previously has been determined by the
    owner or operator using an averaging period greater than one hour
    to be less than 500 ppmw but because of normal operating process
    variations the VO concentration of the hazardous waste determined
    by direct measurement for any given one-hour period may be equal
    to or greater than 500 ppmw, information that was used by the
    owner or operator to determine the average VO concentration of
    the hazardous waste (e.g., test results, measurements, calculations,
    and other documentation) and recorded in the facility records in
    accordance with the requirements of Section 724.983(a) and
    Section 724.989 must be considered by the Agency together with
    the results of the waste determination performed or requested by
    the Agency in establishing compliance with this Subpart CC.

     
    426
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.984 Standards: Tanks
     
    a) The provisions of this Section apply to the control of air pollutant emissions from
    tanks for which Section 724.982(b) references the use of this Section for such air
    emission control.
     
    b) The owner or operator must control air pollutant emissions from each tank subject
    to this Section in accordance with the following requirements, as applicable:
     
    1) For a tank that manages hazardous waste that meets all of the conditions
    specified in subsections (b)(1)(A) through (b)(1)(C) of this Section, the
    owner or operator must control air pollutant emissions from the tank in
    accordance with the Tank Level 1 controls specified in subsection (c) of
    this Section or the Tank Level 2 controls specified in subsection (d) of this
    Section.
     
    A) The hazardous waste in the tank has a maximum organic vapor
    pressure that is less than the maximum organic vapor pressure
    limit for the tank’s design capacity category, as follows:
     
    i) For a tank design capacity equal to or greater than 151 m
    3
     
    (39,900 gal), the maximum organic vapor pressure limit for
    the tank is 5.2 kPa (0.75 psig).
     
    ii) For a tank design capacity equal to or greater than 75 m
    3
     
    (19,800 gal) but less than 151 m
    3
    (39,900 gal), the
    maximum organic vapor pressure limit for the tank is 27.6
    kPa (4.00 psig).
     
    iii) For a tank design capacity less than 75 m
    3
    (19,800 gal), the
    maximum organic vapor pressure limit for the tank is 76.6
    kPa (11.1 psig).
     
    B) The hazardous waste in the tank is not heated by the owner or
    operator to a temperature that is greater than the temperature at
    which the maximum organic vapor pressure of the hazardous waste
    is determined for the purpose of complying with subsection
    (b)(1)(A) of this Section.
     
    C) The owner or operator does not treat the hazardous waste in the
    tank using a waste stabilization process, as defined in 35 Ill. Adm.
    Code 725.981.
     

     
    427
    2) For a tank that manages hazardous waste that does not meet all of the
    conditions specified in subsections (b)(1)(A) through (b)(1)(C) of this
    Section, the owner or operator must control air pollutant emissions from
    the tank by using Tank Level 2 controls in accordance with the
    requirements of subsection (d) of this Section. Examples of tanks required
    to use Tank Level 2 controls include a tank used for a waste stabilization
    process and a tank for which the hazardous waste in the tank has a
    maximum organic vapor pressure that is equal to or greater than the
    maximum organic vapor pressure limit for the tank’s design capacity
    category, as specified in subsection (b)(1)(A) of this Section.
     
    c) Owners and operators controlling air pollutant emissions from a tank using Tank
    Level 1 controls must meet the requirements specified in subsections (c)(1)
    through (c)(4) of this Section:
     
    1) The owner or operator must determine the maximum organic vapor
    pressure for a hazardous waste to be managed in the tank using Tank
    Level 1 controls before the first time the hazardous waste is placed in the
    tank. The maximum organic vapor pressure must be determined using the
    procedures specified in Section 724.983(c). Thereafter, the owner or
    operator must perform a new determination whenever changes to the
    hazardous waste managed in the tank could potentially cause the
    maximum organic vapor pressure to increase to a level that is equal to or
    greater than the maximum organic vapor pressure limit for the tank design
    capacity category specified in subsection (b)(1)(A) of this Section, as
    applicable to the tank.
     
    2) The tank must be equipped with a fixed roof designed to meet the
    following specifications:
     
    A) The fixed roof and its closure devices must be designed to form a
    continuous barrier over the entire surface area of the hazardous
    waste in the tank. The fixed roof may be a separate cover installed
    on the tank (e.g., a removable cover mounted on an open-top tank)
    or may be an integral part of the tank structural design (e.g., a
    horizontal cylindrical tank equipped with a hatch).
     
    B) The fixed roof must be installed in such a manner that there are no
    visible cracks, holes, gaps, or other open spaces between roof
    section joints or between the interface of the roof edge and the tank
    wall.
     
    C) Either of the following must be true of each opening in the fixed
    roof and of any manifold system associated with the fixed roof:
     
    i) The opening or manifold system is equipped with a closure

     
    428
    device designed to operate so that when the closure device
    is secured in the closed position there are no visible cracks,
    holes, gaps, or other open spaces in the closure device or
    between the perimeter of the opening and the closure
    device; or
     
    ii) The opening or manifold system is connected by a closed-
    vent system that is vented to a control device. The control
    device must remove or destroy organics in the vent stream,
    and it must be operating whenever hazardous waste is
    managed in the tank, except as provided for in subsection
    (c)(2)(E) of this Section.
     
    D) The fixed roof and its closure devices must be made of suitable
    materials that will minimize exposure of the hazardous waste to
    the atmosphere, to the extent practical, and will maintain the
    integrity of the fixed roof and closure devices throughout their
    intended service life. Factors to be considered when selecting the
    materials for and designing the fixed roof and closure devices must
    include the following: the organic vapor permeability; the effects
    of any contact with the hazardous waste or its vapors managed in
    the tank; the effects of outdoor exposure to wind, moisture, and
    sunlight; and the operating practices used for the tank on which the
    fixed roof is installed.
     
    E) The control device operated pursuant to subsection (c)(2)(C) of
    this Section needs not remove or destroy organics in the vent
    stream under the following conditions:
     
    i) During periods when it is necessary to provide access to the
    tank for performing the activities of subsection (c)(2)(E)(ii)
    of this Section, venting of the vapor headspace underneath
    the fixed roof to the control device is not required, opening
    of closure devices is allowed, and removal of the fixed roof
    is allowed. Following completion of the activity, the owner
    or operator must promptly secure the closure device in the
    closed position or reinstall the cover, as applicable, and
    resume operation of the control device; and
     
    ii) During periods of routine inspection, maintenance, or other
    activities needed for normal operations, and for removal of
    accumulated sludge or other residues from the bottom of
    the tank.
     
    BOARD NOTE: Subsections (c)(2)(E)(i) and (c)(2)(E)(ii) of this
    Section are derived from 40 CFR 264.1084(c)(2)(iii)(B)(
    1
    ) and

     
    429
    (c)(2)(iii)(B)(
    2
    ), which the Board has codified here to comport
    with Illinois Administrative Code format requirements.
     
    3) Whenever a hazardous waste is in the tank, the fixed roof must be
    installed with each closure device secured in the closed position, except as
    follows:
     
    A) Opening of closure devices or removal of the fixed roof is allowed
    at the following times:
     
    i) To provide access to the tank for performing routine
    inspection, maintenance, or other activities needed for
    normal operations. Examples of such activities include
    those times when a worker needs to open a port to sample
    the liquid in the tank, or when a worker needs to open a
    hatch to maintain or repair equipment. Following
    completion of the activity, the owner or operator must
    promptly secure the closure device in the closed position or
    reinstall the cover, as applicable, to the tank.
     
    ii) To remove accumulated sludge or other residues from the
    bottom of the tank.
     
    B) Opening of a spring-loaded pressure-vacuum relief valve,
    conservation vent, or similar type of pressure relief device that
    vents to the atmosphere is allowed during normal operations for
    the purpose of maintaining the tank internal pressure in accordance
    with the tank design specifications. The device must be designed
    to operate with no detectable organic emissions when the device is
    secured in the closed position. The settings at which the device
    opens must be established so that the device remains in the closed
    position whenever the tank internal pressure is within the internal
    pressure operating range determined by the owner or operator
    based on the tank manufacturer recommendations, applicable
    regulations, fire protection and prevention codes, standard
    engineering codes and practices, or other requirements for the safe
    handling of flammable, ignitable, explosive, reactive, or hazardous
    materials. Examples of normal operating conditions that may
    require these devices to open are during those times when the tank
    internal pressure exceeds the internal pressure operating range for
    the tank as a result of loading operations or diurnal ambient
    temperature fluctuations.
     
    C) Opening of a safety device, as defined in 35 Ill. Adm. Code
    725.981, is allowed at any time conditions require doing so to
    avoid an unsafe condition.

     
    430
     
    4) The owner or operator must inspect the air emission control equipment in
    accordance with the following requirements.
     
    A) The fixed roof and its closure devices must be visually inspected
    by the owner or operator to check for defects that could result in
    air pollutant emissions. Defects include, but are not limited to,
    visible cracks, holes, or gaps in the roof sections or between the
    roof and the tank wall; broken, cracked, or otherwise damaged
    seals or gaskets on closure devices; and broken or missing hatches,
    access covers, caps, or other closure devices.
     
    B) The owner or operator must perform an initial inspection of the
    fixed roof and its closure devices on or before the date that the
    tank becomes subject to this Section. Thereafter, the owner or
    operator must perform the inspections at least once every year
    except under the special conditions provided for in subsection (l)
    of this Section.
     
    C) In the event that a defect is detected, the owner or operator must
    repair the defect in accordance with the requirements of subsection
    (k) of this Section.
     
    D) The owner or operator must maintain a record of the inspection in
    accordance with the requirements specified in Section 724.989(b).
     
    d) Owners and operators controlling air pollutant emissions from a tank using Tank
    Level 2 controls must use one of the following tanks:
     
    1) A fixed-roof tank equipped with an internal floating roof in accordance
    with the requirements specified in subsection (e) of this Section;
     
    2) A tank equipped with an external floating roof in accordance with the
    requirements specified in subsection (f) of this Section;
     
    3) A tank vented through a closed-vent system to a control device in
    accordance with the requirements specified in subsection (g) of this
    Section;
     
    4) A pressure tank designed and operated in accordance with the
    requirements specified in subsection (h) of this Section; or
     
    5) A tank located inside an enclosure that is vented through a closed-vent
    system to an enclosed combustion control device in accordance with the
    requirements specified in subsection (i) of this Section.
     

     
    431
    e) The owner or operator that controls air pollutant emissions from a tank using a
    fixed roof with an internal floating roof must meet the requirements specified in
    subsections (e)(1) through (e)(3) of this Section.
     
    1) The tank must be equipped with a fixed roof and an internal floating roof
    in accordance with the following requirements:
     
    A) The internal floating roof must be designed to float on the liquid
    surface except when the floating roof must be supported by the leg
    supports.
     
    B) The internal floating roof must be equipped with a continuous seal
    between the wall of the tank and the floating roof edge that meets
    either of the following requirements:
     
    i) A single continuous seal that is either a liquid-mounted seal
    or a metallic shoe seal, as defined in 35 Ill. Adm. Code
    725.981; or
     
    ii) Two continuous seals mounted one above the other. The
    lower seal may be a vapor-mounted seal.
     
    C) The internal floating roof must meet the following specifications:
     
    i) Each opening in a noncontact internal floating roof except
    for automatic bleeder vents (vacuum breaker vents) and the
    rim space vents is to provide a projection below the liquid
    surface.
     
    ii) Each opening in the internal floating roof must be equipped
    with a gasketed cover or a gasketed lid except for leg
    sleeves, automatic bleeder vents, rim space vents, column
    wells, ladder wells, sample wells, and stub drains.
     
    iii) Each penetration of the internal floating roof for the
    purpose of sampling must have a slit fabric cover that
    covers at least 90 percent of the opening.
     
    iv) Each automatic bleeder vent and rim space vent must be
    gasketed.
     
    v) Each penetration of the internal floating roof that allows for
    passage of a ladder must have a gasketed sliding cover.
     
    vi) Each penetration of the internal floating roof that allows for
    passage of a column supporting the fixed roof must have a

     
    432
    flexible fabric sleeve seal or a gasketed sliding cover.
     
    2) The owner or operator must operate the tank in accordance with the
    following requirements:
     
    A) When the floating roof is resting on the leg supports, the process of
    filling, emptying, or refilling must be continuous and must be
    completed as soon as practical.
     
    B) Automatic bleeder vents are to be set closed at all times when the
    roof is floating, except when the roof is being floated off or is
    being landed on the leg supports.
     
    C) Prior to filling the tank, each cover, access hatch, gauge float well
    or lid on any opening in the internal floating roof must be bolted or
    fastened closed (i.e., no visible gaps). Rim space vents must be set
    to open only when the internal floating roof is not floating or when
    the pressure beneath the rim exceeds the manufacturer’s
    recommended setting.
     
    3) The owner or operator must inspect the internal floating roof in
    accordance with the procedures specified as follows:
     
    A) The floating roof and its closure devices must be visually inspected
    by the owner or operator to check for defects that could result in
    air pollutant emissions. Defects include, but are not limited to, any
    of the following: when the internal floating roof is not floating on
    the surface of the liquid inside the tank; when liquid has
    accumulated on top of the internal floating roof; when any portion
    of the roof seals have detached from the roof rim; when holes,
    tears, or other openings are visible in the seal fabric; when the
    gaskets no longer close off the hazardous waste surface from the
    atmosphere; or when the slotted membrane has more than 10
    percent open area.
     
    B) The owner or operator must inspect the internal floating roof
    components as follows, except as provided in subsection (e)(3)(C)
    of this Section:
     
    i) Visually inspect the internal floating roof components
    through openings on the fixed-roof (e.g., manholes and roof
    hatches) at least once every 12 months after initial fill, and
     
    ii) Visually inspect the internal floating roof, primary seal,
    secondary seal (if one is in service), gaskets, slotted
    membranes, and sleeve seals (if any) each time the tank is

     
    433
    emptied and degassed and at least once every 10 years.
     
    C) As an alternative to performing the inspections specified in
    subsection (e)(3)(B) of this Section for an internal floating roof
    equipped with two continuous seals mounted one above the other,
    the owner or operator may visually inspect the internal floating
    roof, primary and secondary seals, gaskets, slotted membranes, and
    sleeve seals (if any) each time the tank is emptied and degassed
    and at least every five years.
     
    D) Prior to each inspection required by subsection (e)(3)(B) or
    (e)(3)(C) of this Section, the owner or operator must notify the
    Agency in advance of each inspection to provide the Agency with
    the opportunity to have an observer present during the inspection.
    The owner or operator must notify the Agency of the date and
    location of the inspection, as follows:
     
    i) Prior to each visual inspection of an internal floating roof
    in a tank that has been emptied and degassed, written
    notification must be prepared and sent by the owner or
    operator so that it is received by the Agency at least 30
    calendar days before refilling the tank, except when an
    inspection is not planned, as provided for in subsection
    (e)(3)(D)(ii) of this Section.
     
    ii) When a visual inspection is not planned and the owner or
    operator could not have known about the inspection 30
    calendar days before refilling the tank, the owner or
    operator must notify the Agency as soon as possible, but no
    later than seven calendar days before refilling of the tank.
    This notification may be made by telephone and
    immediately followed by a written explanation for why the
    inspection is unplanned. Alternatively, written notification,
    including the explanation for the unplanned inspection,
    may be sent so that it is received by the Agency at least
    seven calendar days before refilling the tank.
     
    E) In the event that a defect is detected, the owner or operator must
    repair the defect in accordance with the requirements of subsection
    (k) of this Section.
     
    F) The owner or operator must maintain a record of the inspection in
    accordance with the requirements specified in Section 724.989(b).
     
    4) Safety devices, as defined in 35 Ill. Adm. Code 725.981, may be installed
    and operated as necessary on any tank complying with the requirements of

     
    434
    this subsection (e).
     
    f) The owner or operator that controls air pollutant emissions from a tank using an
    external floating roof must meet the requirements specified in subsections (f)(1)
    through (f)(3) of this Section.
     
    1) The owner or operator must design the external floating roof in
    accordance with the following requirements:
     
    A) The external floating roof must be designed to float on the liquid
    surface except when the floating roof must be supported by the leg
    supports.
     
    B) The floating roof must be equipped with two continuous seals, one
    above the other, between the wall of the tank and the roof edge.
    The lower seal is referred to as the primary seal, and the upper seal
    is referred to as the secondary seal.
     
    i) The primary seal must be a liquid-mounted seal or a
    metallic shoe seal, as defined in 35 Ill. Adm. Code
    725.981. The total area of the gaps between the tank wall
    and the primary seal must not exceed 212 square
    centimeters (cm
    2
    ) per meter (10.0 square inches (in
    2
    ) per
    foot) of tank diameter, and the width of any portion of
    these gaps must not exceed 3.8 centimeters (cm) (1.5 in).
    If a metallic shoe seal is used for the primary seal, the
    metallic shoe seal must be designed so that one end extends
    into the liquid in the tank and the other end extends a
    vertical distance of at least 61 cm (24 in) above the liquid
    surface.
     
    ii) The secondary seal must be mounted above the primary
    seal and cover the annular space between the floating roof
    and the wall of the tank. The total area of the gaps between
    the tank wall and the secondary seal must not exceed 21.2
    cm
    2
    per meter (1.00 in
    2
    per foot) of tank diameter, and the
    width of any portion of these gaps must not exceed 1.3 cm
    (0.51 in).
     
    C) The external floating roof must meet the following specifications:
     
    i) Except for automatic bleeder vents (vacuum breaker vents)
    and rim space vents, each opening in a noncontact external
    floating roof must provide a projection below the liquid
    surface.
     

     
    435
    ii) Except for automatic bleeder vents, rim space vents, roof
    drains, and leg sleeves, each opening in the roof must be
    equipped with a gasketed cover, seal, or lid.
     
    iii) Each access hatch and each gauge float well must be
    equipped with a cover designed to be bolted or fastened
    when the cover is secured in the closed position.
     
    iv) Each automatic bleeder vent and each rim space vent must
    be equipped with a gasket.
     
    v) Each roof drain that empties into the liquid managed in the
    tank must be equipped with a slotted membrane fabric
    cover that covers at least 90 percent of the area of the
    opening.
     
    vi) Each unslotted and slotted guide pole well must be
    equipped with a gasketed sliding cover or a flexible fabric
    sleeve seal.
     
    vii) Each unslotted guide pole must be equipped with a
    gasketed cap on the end of the pole.
     
    viii) Each slotted guide pole must be equipped with a gasketed
    float or other device that closes off the liquid surface from
    the atmosphere.
     
    ix) Each gauge hatch and each sample well must be equipped
    with a gasketed cover.
     
    2) The owner or operator must operate the tank in accordance with the
    following requirements:
     
    A) When the floating roof is resting on the leg supports, the process of
    filling, emptying, or refilling must be continuous and must be
    completed as soon as practical.
     
    B) Except for automatic bleeder vents, rim space vents, roof drains,
    and leg sleeves, each opening in the roof must be secured and
    maintained in a closed position at all times except when the
    closure device must be open for access.
     
    C) Covers on each access hatch and each gauge float well must be
    bolted or fastened when secured in the closed position.
     
    D) Automatic bleeder vents must be set closed at all times when the

     
    436
    roof is floating, except when the roof is being floated off or is
    being landed on the leg supports.
     
    E) Rim space vents must be set to open only at those times that the
    roof is being floated off the roof leg supports or when the pressure
    beneath the rim seal exceeds the manufacturer’s recommended
    setting.
     
    F) The cap on the end of each unslotted guide pole must be secured in
    the closed position at all times except when measuring the level or
    collecting samples of the liquid in the tank.
     
    G) The cover on each gauge hatch or sample well must be secured in
    the closed position at all times except when the hatch or well must
    be opened for access.
     
    H) Both the primary seal and the secondary seal must completely
    cover the annular space between the external floating roof and the
    wall of the tank in a continuous fashion except during inspections.
     
    3) The owner or operator must inspect the external floating roof in
    accordance with the procedures specified as follows:
     
    A) The owner or operator must measure the external floating roof seal
    gaps in accordance with the following requirements:
     
    i) The owner or operator must perform measurements of gaps
    between the tank wall and the primary seal within 60
    calendar days after initial operation of the tank following
    installation of the floating roof and, thereafter, at least once
    every five years.
     
    ii) The owner or operator must perform measurements of gaps
    between the tank wall and the secondary seal within 60
    calendar days after initial operation of the tank following
    installation of the floating roof and, thereafter, at least once
    every year.
     
    iii) If a tank ceases to hold hazardous waste for a period of one
    year or more, subsequent introduction of hazardous waste
    into the tank must be considered an initial operation for the
    purposes of subsections (f)(3)(A)(i) and (f)(3)(A)(ii) of this
    Section.
     
    iv) The owner or operator must determine the total surface area
    of gaps in the primary seal and in the secondary seal

     
    437
    individually using the procedure of subsection (f)(3)(D) of
    this Section.
     
    v) In the event that the seal gap measurements do not conform
    to the specifications in subsection (f)(1)(B) of this Section,
    the owner or operator must repair the defect in accordance
    with the requirements of subsection (k) of this Section.
     
    vi) The owner or operator must maintain a record of the
    inspection in accordance with the requirements specified in
    Section 724.989(b).
     
    B) The owner or operator must visually inspect the external floating
    roof in accordance with the following requirements:
     
    i) The floating roof and its closure devices must be visually
    inspected by the owner or operator to check for defects that
    could result in air pollutant emissions. Defects include, but
    are not limited to, any of the following conditions: holes,
    tears, or other openings in the rim seal or seal fabric of the
    floating roof; a rim seal detached from the floating roof; all
    or a portion of the floating roof deck being submerged
    below the surface of the liquid in the tank; broken, cracked,
    or otherwise damaged seals or gaskets on closure devices;
    and broken or missing hatches, access covers, caps, or
    other closure devices.
     
    ii) The owner or operator must perform an initial inspection of
    the external floating roof and its closure devices on or
    before the date that the tank becomes subject to this
    Section. Thereafter, the owner or operator must perform
    the inspections at least once every year except for the
    special conditions provided for in subsection (l) of this
    Section.
     
    iii) In the event that a defect is detected, the owner or operator
    must repair the defect in accordance with the requirements
    of subsection (k) of this Section.
     
    iv) The owner or operator must maintain a record of the
    inspection in accordance with the requirements specified in
    Section 724.989(b).
     
    C) Prior to each inspection required by subsection (f)(3)(A) or
    (f)(3)(B) of this Section, the owner or operator must notify the
    Agency in advance of each inspection to provide the Agency with

     
    438
    the opportunity to have an observer present during the inspection.
    The owner or operator must notify the Agency of the date and
    location of the inspection, as follows:
     
    i) Prior to each inspection to measure external floating roof
    seal gaps as required under subsection (f)(3)(A) of this
    Section, written notification must be prepared and sent by
    the owner or operator so that it is received by the Agency at
    least 30 calendar days before the date the measurements are
    scheduled to be performed.
     
    ii) Prior to each visual inspection of an external floating roof
    in a tank that has been emptied and degassed, written
    notification must be prepared and sent by the owner or
    operator so that it is received by the Agency at least 30
    calendar days before refilling the tank, except when an
    inspection is not planned as provided for in subsection
    (f)(3)(C)(iii) of this Section.
     
    iii) When a visual inspection is not planned and the owner or
    operator could not have known about the inspection 30
    calendar days before refilling the tank, the owner or
    operator must notify the Agency as soon as possible, but no
    later than seven calendar days before refilling of the tank.
    This notification may be made by telephone and
    immediately followed by a written explanation for why the
    inspection is unplanned. Alternatively, written notification,
    including the explanation for the unplanned inspection,
    may be sent so that it is received by the Agency at least
    seven calendar days before refilling the tank.
     
    D) Procedure for determining the total surface area of gaps in the
    primary seal and the secondary seal:
     
    i) The seal gap measurements must be performed at one or
    more floating roof levels when the roof is floating off the
    roof supports.
     
    ii) Seal gaps, if any, must be measured around the entire
    perimeter of the floating roof in each place where a 0.32
    cm (0.125 in) diameter uniform probe passes freely
    (without forcing or binding against the seal) between the
    seal and the wall of the tank and measure the
    circumferential distance of each such location.
     
    iii) For a seal gap measured under subsection (f)(3) of this

     
    439
    Section, the gap surface area must be determined by using
    probes of various widths to measure accurately the actual
    distance from the tank wall to the seal and multiplying each
    such width by its respective circumferential distance.
     
    iv) The total gap area must be calculated by adding the gap
    surface areas determined for each identified gap location
    for the primary seal and the secondary seal individually,
    and then dividing the sum for each seal type by the nominal
    diameter of the tank. These total gap areas for the primary
    seal and secondary seal are then compared to the respective
    standards for the seal type, as specified in subsection
    (f)(1)(B) of this Section.
     
    BOARD NOTE: Subsections (f)(3)(D)(i) through (f)(3)(D)(iv) of
    this Section are derived from 40 CFR 264.1084(f)(3)(i)(D)(
    1
    )
    through (f)(3)(i)(D)(
    4
    ), which the Board has codified here to
    comport with Illinois Administrative Code format requirements.
     
    4) Safety devices, as defined in 35 Ill. Adm. Code 725.981, may be installed
    and operated as necessary on any tank complying with the requirements of
    subsection (f) of this Section.
     
    g) The owner or operator that controls air pollutant emissions from a tank by venting
    the tank to a control device must meet the requirements specified in subsections
    (g)(1) through (g)(3) of this Section.
     
    1) The tank must be covered by a fixed roof and vented directly through a
    closed-vent system to a control device in accordance with the following
    requirements:
     
    A) The fixed roof and its closure devices must be designed to form a
    continuous barrier over the entire surface area of the liquid in the
    tank.
     
    B) Each opening in the fixed roof not vented to the control device
    must be equipped with a closure device. If the pressure in the
    vapor headspace underneath the fixed roof is less than atmospheric
    pressure when the control device is operating, the closure device
    must be designed to operate so that when the closure device is
    secured in the closed position there are no visible cracks, holes,
    gaps, or other open spaces in the closure device or between the
    perimeter of the cover opening and the closure device. If the
    pressure in the vapor headspace underneath the fixed roof is equal
    to or greater than atmospheric pressure when the control device is
    operating, the closure device must be designed to operate with no

     
    440
    detectable organic emissions.
     
    C) The fixed roof and its closure devices must be made of suitable
    materials that will minimize exposure of the hazardous waste to
    the atmosphere, to the extent practical, and will maintain the
    integrity of the fixed roof and closure devices throughout their
    intended service life. Factors to be considered when selecting the
    materials for and designing the fixed roof and closure devices must
    include the following: organic vapor permeability; the effects of
    any contact with the liquid and its vapor managed in the tank; the
    effects of outdoor exposure to wind, moisture, and sunlight; and
    the operating practices used for the tank on which the fixed roof is
    installed.
     
    D) The closed-vent system and control device must be designed and
    operated in accordance with the requirements of Section 724.987.
     
    2) Whenever a hazardous waste is in the tank, the fixed roof must be
    installed with each closure device secured in the closed position and the
    vapor headspace underneath the fixed roof vented to the control device,
    except as follows:
     
    A) Venting to the control device is not required, and opening of
    closure devices or removal of the fixed roof is allowed at the
    following times:
     
    i) To provide access to the tank for performing routine
    inspection, maintenance, or other activities needed for
    normal operations. Examples of such activities include
    those times when a worker needs to open a port to sample
    liquid in the tank, or when a worker needs to open a hatch
    to maintain or repair equipment. Following completion of
    the activity, the owner or operator must promptly secure
    the closure device in the closed position or reinstall the
    cover, as applicable, to the tank.
     
    ii) To remove accumulated sludge or other residues from the
    bottom of a tank.
     
    B) Opening of a safety device, as defined in 35 Ill. Adm. Code
    725.981, is allowed at any time conditions require doing so to
    avoid an unsafe condition.
     
    3) The owner or operator must inspect and monitor the air emission control
    equipment in accordance with the following procedures:
     

     
    441
    A) The fixed roof and its closure devices must be visually inspected
    by the owner or operator to check for defects that could result in
    air pollutant emissions. Defects include, but are not limited to, any
    of the following: visible cracks, holes, or gaps in the roof sections
    or between the roof and the tank wall; broken, cracked, or
    otherwise damaged seals or gaskets on closure devices; and broken
    or missing hatches, access covers, caps, or other closure devices.
     
    B) The closed-vent system and control device must be inspected and
    monitored by the owner or operator in accordance with the
    procedures specified in Section 724.987.
     
    C) The owner or operator must perform an initial inspection of the air
    emission control equipment on or before the date that the tank
    becomes subject to this Section. Thereafter, the owner or operator
    must perform the inspections at least once every year except for
    the special conditions provided for in subsection (l) of this Section.
     
    D) In the event that a defect is detected, the owner or operator must
    repair the defect in accordance with the requirements of subsection
    (k) of this Section.
     
    E) The owner or operator must maintain a record of the inspection in
    accordance with the requirements specified in Section 724.989(b).
     
    h) The owner or operator that controls air pollutant emissions by using a pressure
    tank must meet the following requirements:
     
    1) The tank must be designed not to vent to the atmosphere as a result of
    compression of the vapor headspace in the tank during filling of the tank
    to its design capacity.
     
    2) All tank openings must be equipped with closure devices designed to
    operate with no detectable organic emissions, as determined using the
    procedure specified in Section 724.983(d).
     
    3) Whenever a hazardous waste is in the tank, the tank must be operated as a
    closed-vent system that does not vent to the atmosphere, except under
    either of the following two conditions:
     
    A) The tank does not need to be operated as a closed-vent system at
    those times when the opening of a safety device, as defined in 35 Ill.
    Adm. Code 725.981, is required to avoid an unsafe condition.
     
    B) The tank does not need to be operated as a closed-vent system at
    those times when the purging of inerts from the tank is required and

     
    442
    the purge stream is routed to a closed-vent system and control device
    designed and operated in accordance with the requirements of
    Section 724.987.
     
    i) The owner or operator that controls air pollutant emissions by using an enclosure
    vented through a closed-vent system to an enclosed combustion control device
    must meet the requirements specified in subsections (i)(1) through (i)(4) of this
    Section.
     
    1) The tank must be located inside an enclosure. The enclosure must be
    designed and operated in accordance with the criteria for a permanent total
    enclosure, as specified in “Procedure T—Criteria for and Verification of a
    Permanent or Temporary Total Enclosure” under appendix B to 40 CFR
    52.741, appendix B (VOM Measurement Techniques for Capture
    Efficiency), incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(b). The enclosure may have permanent or temporary openings to
    allow worker access; passage of material into or out of the enclosure by
    conveyor, vehicles, or other mechanical means; entry of permanent
    mechanical or electrical equipment; or direct airflow into the enclosure.
    The owner or operator must perform the verification procedure for the
    enclosure, as specified in Section 5.0 to “Procedure T—Criteria for and
    Verification of a Permanent or Temporary Total Enclosure,” initially
    when the enclosure is first installed and, thereafter, annually.
     
    2) The enclosure must be vented through a closed-vent system to an enclosed
    combustion control device that is designed and operated in accordance
    with the standards for either a vapor incinerator, boiler, or process heater
    specified in Section 724.987.
     
    3) Safety devices, as defined in 35 Ill. Adm. Code 725.981, may be installed
    and operated as necessary on any enclosure, closed-vent system, or control
    device used to comply with the requirements of subsections (i)(1) and
    (i)(2) of this Section.
     
    4) The owner or operator must inspect and monitor the closed-vent system
    and control device, as specified in Section 724.987.
     
    j) The owner or operator must transfer hazardous waste to a tank subject to this
    Section in accordance with the following requirements:
     
    1) Transfer of hazardous waste, except as provided in subsection (j)(2) of this
    Section, to the tank from another tank subject to this Section or from a
    surface impoundment subject to Section 724.985 must be conducted using
    continuous hard-piping or another closed system that does not allow
    exposure of the hazardous waste to the atmosphere. For the purpose of
    complying with this provision, an individual drain system is considered to

     
    443
    be a closed system when it meets the requirements of subpart RR of 40
    CFR 63, subpart RR, “(National Emission Standards for Individual Drain
    Systems,”), incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(b).
     
    2) The requirements of subsection (j)(1) of this Section do not apply when
    transferring a hazardous waste to the tank under any of the following
    conditions:
     
    A) The hazardous waste meets the average VO concentration
    conditions specified in Section 724.982(c)(1) at the point of waste
    origination.
     
    B) The hazardous waste has been treated by an organic destruction or
    removal process to meet the requirements in Section
    724.982(c)(2).
     
    C) The hazardous waste meets the requirements of Section
    724.982(c)(4).
     
    k) The owner or operator must repair each defect detected during an inspection
    performed in accordance with the requirements of subsection (c)(4), (e)(3), (f)(3),
    or (g)(3) of this Section, as follows:
     
    1) The owner or operator must make first efforts at repair of the defect no
    later than five calendar days after detection, and repair must be completed
    as soon as possible but no later than 45 calendar days after detection
    except as provided in subsection (k)(2) of this Section.
     
    2) Repair of a defect may be delayed beyond 45 calendar days if the owner
    or operator determines that repair of the defect requires emptying or
    temporary removal from service of the tank and no alternative tank
    capacity is available at the site to accept the hazardous waste normally
    managed in the tank. In this case, the owner or operator must repair the
    defect the next time the process or unit that is generating the hazardous
    waste managed in the tank stops operation. Repair of the defect must be
    completed before the process or unit resumes operation.
     
    l) Following the initial inspection and monitoring of the cover, as required by the
    applicable provisions of this Subpart CC, subsequent inspection and monitoring
    may be performed at intervals longer than one year under the following special
    conditions:
     
    1) In the case when inspecting or monitoring the cover would expose a
    worker to dangerous, hazardous, or other unsafe conditions, then the
    owner or operator may designate a cover as an “unsafe to inspect and

     
    444
    monitor cover” and comply with all of the following requirements:
     
    A) Prepare a written explanation for the cover stating the reasons why
    the cover is unsafe to visually inspect or to monitor, if required.
     
    B) Develop and implement a written plan and schedule to inspect and
    monitor the cover, using the procedures specified in the applicable
    Section of this Subpart CC, as frequently as practicable during
    those times when a worker can safely access the cover.
     
    2) In the case when a tank is buried partially or entirely underground, an
    owner or operator is required to inspect and monitor, as required by the
    applicable provisions of this Section, only those portions of the tank cover
    and those connections to the tank (e.g., fill ports, access hatches, gauge
    wells, etc.) that are located on or above the ground surface.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.985 Standards: Surface Impoundments
     
    a) The provisions of this Section apply to the control of air pollutant emissions from
    surface impoundments for which Section 724.982(b) references the use of this
    Section for such air emission control.
     
    b) The owner or operator must control air pollutant emissions from the surface
    impoundment by installing and operating either of the following:
     
    1) A floating membrane cover in accordance with the provisions specified in
    subsection (c) of this Section; or
     
    2) A cover that is vented through a closed-vent system to a control device in
    accordance with the provisions specified in subsection (d) of this Section.
     
    c) The owner or operator that controls air pollutant emissions from a surface
    impoundment using a floating membrane cover must meet the requirements
    specified in subsections (c)(1) through (c)(3) of this Section.
     
    1) The surface impoundment must be equipped with a floating membrane
    cover designed to meet the following specifications:
     
    A) The floating membrane cover must be designed to float on the
    liquid surface during normal operations and form a continuous
    barrier over the entire surface area of the liquid.
     
    B) The cover must be fabricated from a synthetic membrane material
    that is either of the following:

     
    445
     
    i) High density polyethylene (HDPE) with a thickness no less
    than 2.5 millimeters (mm) (0.098 in); or
     
    ii) A material or a composite of different materials determined
    to have both organic permeability properties that are
    equivalent to those of the material listed in subsection
    (c)(1)(B)(i) of this Section and chemical and physical
    properties that maintain the material integrity for the
    intended service life of the material.
     
    C) The cover must be installed in such a manner that there are no
    visible cracks, holes, gaps, or other open spaces between cover
    section seams or between the interface of the cover edge and its
    foundation mountings.
     
    D) Except as provided for in subsection (c)(1)(E) of this Section, each
    opening in the floating membrane cover must be equipped with a
    closure device so designed as to operate that when the closure
    device is secured in the closed position there are no visible cracks,
    holes, gaps, or other open spaces in the closure device or between
    the perimeter of the cover opening and the closure device.
     
    E) The floating membrane cover may be equipped with one or more
    emergency cover drains for removal of stormwater. Each
    emergency cover drain must be equipped with a slotted membrane
    fabric cover that covers at least 90 percent of the area of the
    opening or a flexible fabric sleeve seal.
     
    F) The closure devices must be made of suitable materials that will
    minimize exposure of the hazardous waste to the atmosphere, to
    the extent practical, and will maintain the integrity of the closure
    devices throughout their intended service life. Factors to be
    considered when selecting the materials of construction and
    designing the cover and closure devices must include the
    following: the organic vapor permeability; the effects of any
    contact with the liquid and its vapor managed in the surface
    impoundment; the effects of outdoor exposure to wind, moisture,
    and sunlight; and the operating practices used for the surface
    impoundment on which the floating membrane cover is installed.
     
    2) Whenever a hazardous waste is in the surface impoundment, the floating
    membrane cover must float on the liquid and each closure device must be
    secured in the closed position, except as follows:
     
    A) Opening of closure devices or removal of the cover is allowed at

     
    446
    the following times:
     
    i) To provide access to the surface impoundment for
    performing routine inspection, maintenance, or other
    activities needed for normal operations. Examples of such
    activities include those times when a worker needs to open
    a port to sample the liquid in the surface impoundment, or
    when a worker needs to open a hatch to maintain or repair
    equipment. Following completion of the activity, the
    owner or operator must promptly replace the cover and
    secure the closure device in the closed position, as
    applicable.
     
    ii) To remove accumulated sludge or other residues from the
    bottom of surface impoundment.
     
    B) Opening of a safety device, as defined in 35 Ill. Adm. Code
    725.981, is allowed at any time conditions require doing so to
    avoid an unsafe condition.
     
    3) The owner or operator must inspect the floating membrane cover in
    accordance with the following procedures:
     
    A) The floating membrane cover and its closure devices must be
    visually inspected by the owner or operator to check for defects
    that could result in air pollutant emissions. Defects include, but
    are not limited to, visible cracks, holes, or gaps in the cover section
    seams or between the interface of the cover edge and its foundation
    mountings; broken, cracked, or otherwise damaged seals or gaskets
    on closure devices; and broken or missing hatches, access covers,
    caps, or other closure devices.
     
    B) The owner or operator must perform an initial inspection of the
    floating membrane cover and its closure devices on or before the
    date that the surface impoundment becomes subject to this
    Section. Thereafter, the owner or operator must perform the
    inspections at least once every year except for the special
    conditions provided for in subsection (g) of this Section.
     
    C) In the event that a defect is detected, the owner or operator must
    repair the defect in accordance with the requirements of subsection
    (f) of this Section.
     
    D) The owner or operator must maintain a record of the inspection in
    accordance with the requirements specified in Section 724.989(c).
     

     
    447
    d) The owner or operator that controls air pollutant emissions from a surface
    impoundment using a cover vented to a control device must meet the
    requirements specified in subsections (d)(1) through (d)(3) of this Section.
     
    1) The surface impoundment must be covered by a cover and vented directly
    through a closed-vent system to a control device in accordance with the
    following requirements:
     
    A) The cover and its closure devices must be designed to form a
    continuous barrier over the entire surface area of the liquid in the
    surface impoundment.
     
    B) Each opening in the cover not vented to the control device must be
    equipped with a closure device. If the pressure in the vapor
    headspace underneath the cover is less than atmospheric pressure
    when the control device is operating, the closure devices must be
    designed to operate such that when the closure device is secured in
    the closed position there are no visible cracks, holes, gaps, or other
    open spaces in the closure device or between the perimeter of the
    cover opening and the closure device. If the pressure in the vapor
    headspace underneath the cover is equal to or greater than
    atmospheric pressure when the control device is operating, the
    closure device must be designed to operate with no detectable
    organic emissions using the procedure specified in Section
    724.983(d).
     
    C) The cover and its closure devices must be made of suitable
    materials that will minimize exposure of the hazardous waste to
    the atmosphere to the extent practical and which will maintain the
    integrity of the cover and closure devices throughout their intended
    service life. Factors to be considered when selecting the materials
    of construction and designing the cover and closure devices must
    include the following: the organic vapor permeability; the effects
    of any contact with the liquid or its vapors managed in the surface
    impoundment; the effects of outdoor exposure to wind, moisture,
    and sunlight; and the operating practices used for the surface
    impoundment on which the cover is installed.
     
    D) The closed-vent system and control device must be designed and
    operated in accordance with the requirements of Section 724.987.
     
    2) Whenever a hazardous waste is in the surface impoundment, the cover
    must be installed with each closure device secured in the closed position
    and the vapor headspace underneath the cover vented to the control device
    except as follows:
     

     
    448
    A) Venting to the control device is not required, and opening of
    closure devices or removal of the cover is allowed at the following
    times:
     
    i) To provide access to the surface impoundment for
    performing routine inspection, maintenance, or other
    activities needed for normal operations. Examples of such
    activities include those times when a worker needs to open
    a port to sample liquid in the surface impoundment, or
    when a worker needs to open a hatch to maintain or repair
    equipment. Following completion of the activity, the
    owner or operator must promptly secure the closure device
    in the closed position or reinstall the cover, as applicable,
    to the surface impoundment.
     
    ii) To remove accumulated sludge or other residues from the
    bottom of the surface impoundment.
     
    B) Opening of a safety device, as defined in 35 Ill. Adm. Code
    725.981, is allowed at any time conditions require doing so to
    avoid an unsafe condition.
     
    3) The owner or operator must inspect and monitor the air emission control
    equipment in accordance with the following procedures:
     
    A) The surface impoundment cover and its closure devices must be
    visually inspected by the owner or operator to check for defects
    that could result in air pollutant emissions. Defects include, but
    are not limited to, visible cracks, holes, or gaps in the cover section
    seams or between the interface of the cover edge and its foundation
    mountings; broken, cracked, or otherwise damaged seals or gaskets
    on closure devices; and broken or missing hatches, access covers,
    caps, or other closure devices.
     
    B) The closed-vent system and control device must be inspected and
    monitored by the owner or operator in accordance with the
    procedures specified in Section 724.987.
     
    C) The owner or operator must perform an initial inspection of the air
    emission control equipment on or before the date that the surface
    impoundment becomes subject to this Section. Thereafter, the
    owner or operator must perform the inspections at least once every
    year except for the special conditions provided for in subsection
    (g) of this Section.
     
    D) In the event that a defect is detected, the owner or operator must

     
    449
    repair the defect in accordance with the requirements of subsection
    (f) of this Section.
     
    E) The owner or operator must maintain a record of the inspection in
    accordance with the requirements specified in Section 724.989(c).
     
    e) The owner or operator must transfer hazardous waste to a surface impoundment
    subject to this Section in accordance with the following requirements:
     
    1) Transfer of hazardous waste, except as provided in subsection (e)(2) of
    this Section, to the surface impoundment from another surface
    impoundment subject to this Section or from a tank subject to Section
    724.984 must be conducted using continuous hard-piping or another
    closed system that does not allow exposure of the waste to the
    atmosphere. For the purpose of complying with this provision, an
    individual drain system is considered to be a closed system when it meets
    the requirements of subpart RR of 40 CFR 63, Subpart RR, “(National
    Emission Standards for Individual Drain Systems,”), incorporated by
    reference in 35 Ill. Adm. Code 720.111 720.111(b).
     
    2) The requirements of subsection (e)(1) of this Section do not apply when
    transferring a hazardous waste to the surface impoundment under any of
    the following conditions:
     
    A) The hazardous waste meets the average VO concentration
    conditions specified in Section 724.982(c)(1) at the point of waste
    origination.
     
    B) The hazardous waste has been treated by an organic destruction or
    removal process to meet the requirements in Section
    724.982(c)(2).
     
    C) The hazardous waste meets the requirements of Section
    724.982(c)(4).
     
    f) The owner or operator must repair each defect detected during an inspection
    performed in accordance with the requirements of subsection (c)(3) or (d)(3) of
    this Section as follows:
     
    1) The owner or operator must make first efforts at repair of the defect no
    later than five calendar days after detection and repair must be completed
    as soon as possible but no later than 45 calendar days after detection
    except as provided in subsection (f)(2) of this Section.
     
    2) Repair of a defect may be delayed beyond 45 calendar days if the owner
    or operator determines that repair of the defect requires emptying or

     
    450
    temporary removal from service of the surface impoundment and no
    alternative capacity is available at the site to accept the hazardous waste
    normally managed in the surface impoundment. In this case, the owner or
    operator must repair the defect the next time the process or unit that is
    generating the hazardous waste managed in the surface impoundment
    stops operation. Repair of the defect must be completed before the
    process or unit resumes operation.
     
    g) Following the initial inspection and monitoring of the cover, as required by the
    applicable provisions of this Subpart CC, subsequent inspection and monitoring
    may be performed at intervals longer than one year in the case when inspecting or
    monitoring the cover would expose a worker to dangerous, hazardous, or other
    unsafe conditions. In this case, the owner or operator may designate the cover as
    an “unsafe to inspect and monitor cover” and comply with all of the following
    requirements:
     
    1) Prepare a written explanation for the cover stating the reasons why the
    cover is unsafe to visually inspect or to monitor, if required.
     
    2) Develop and implement a written plan and schedule to inspect and
    monitor the cover using the procedures specified in the applicable Section
    of this Subpart CC as frequently as practicable during those times when a
    worker can safely access the cover.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.986 Standards: Containers
     
    a) The provisions of this Section apply to the control of air pollutant emissions from
    containers for which Section 724.982(b) references the use of this Section for
    such air emission control.
     
    b) General requirements.
     
    1) The owner or operator must control air pollutant emissions from each
    container subject to this Section in accordance with the following
    requirements, as applicable to the container, except when the special
    provisions for waste stabilization processes specified in subsection (b)(2)
    of this Section apply to the container.
     
    A) For a container having a design capacity greater than 0.1 m
    3
    (26
    gal) and less than or equal to 0.46 m
    3
    (120 gal), the owner or
    operator must control air pollutant emissions from the container in
    accordance with the Container Level 1 standards specified in
    subsection (c) of this Section.
     

     
    451
    B) For a container having a design capacity greater than 0.46 m
    3
    (120
    gal) that is not in light material service, the owner or operator must
    control air pollutant emissions from the container in accordance
    with the Container Level 1 standards, specified in subsection (c) of
    this Section.
     
    C) For a container having a design capacity greater than 0.46 m
    3
    (120
    gal) that is in light material service, the owner or operator must
    control air pollutant emissions from the container in accordance
    with the Container Level 2 standards specified in subsection (d) of
    this Section.
     
    2) When a container having a design capacity greater than 0.1 m
    3
    (26 gal) is
    used for treatment of a hazardous waste by a waste stabilization process,
    the owner or operator must control air pollutant emissions from the
    container in accordance with the Container Level 3 standards specified in
    subsection (e) of this Section at those times during the waste stabilization
    process when the hazardous waste in the container is exposed to the
    atmosphere.
     
    c) Container Level 1 standards.
     
    1) A container using Container Level 1 controls is one of the following:
     
    A) A container that meets the applicable USDOT regulations on
    packaging hazardous materials for transportation, as specified in
    subsection (f) of this Section.
     
    B) A container equipped with a cover and closure devices that form a
    continuous barrier over the container openings so that when the
    cover and closure devices are secured in the closed position there
    are no visible holes, gaps, or other open spaces into the interior of
    the container. The cover may be a separate cover installed on the
    container (e.g., a lid on a drum or a suitably secured tarp on a roll-
    off box) or may be an integral part of the container structural
    design (e.g., a “portable tank” or bulk cargo container equipped
    with a screw-type cap).
     
    C) An open-top container in which an organic-vapor suppressing
    barrier is placed on or over the hazardous waste in the container so
    that no hazardous waste is exposed to the atmosphere. One
    example of such a barrier is application of a suitable organic-vapor
    suppressing foam.
     
    2) A container used to meet the requirements of subsection (c)(1)(B) or
    (c)(1)(C) of this Section must be equipped with covers and closure

     
    452
    devices, as applicable to the container, that are composed of suitable
    materials to minimize exposure of the hazardous waste to the atmosphere
    and to maintain the equipment integrity for as long as it is in service.
    Factors to be considered in selecting the materials of construction and
    designing the cover and closure devices must include the following: the
    organic vapor permeability; the effects of contact with the hazardous
    waste or its vapor managed in the container; the effects of outdoor
    exposure of the closure device or cover material to wind, moisture, and
    sunlight; and the operating practices for which the container is intended to
    be used.
     
    3) Whenever a hazardous waste is in a container using Container Level 1
    controls, the owner or operator must install all covers and closure devices
    for the container, as applicable to the container, and secure and maintain
    each closure device in the closed position, except as follows:
     
    A) Opening of a closure device or cover is allowed for the purpose of
    adding hazardous waste or other material to the container, as
    follows:
     
    i) In the case when the container is filled to the intended final
    level in one continuous operation, the owner or operator
    must promptly secure the closure devices in the closed
    position and install the covers, as applicable to the
    container, upon conclusion of the filling operation.
     
    ii) In the case when discrete quantities or batches of material
    intermittently are added to the container over a period of
    time, the owner or operator must promptly secure the
    closure devices in the closed position and install covers, as
    applicable to the container, upon either the container being
    filled to the intended final level; the completion of a batch
    loading after which no additional material will be added to
    the container within 15 minutes; the person performing the
    loading operation leaving the immediate vicinity of the
    container; or the shutdown of the process generating the
    material being added to the container, whichever condition
    occurs first.
     
    B) Opening of a closure device or cover is allowed for the purpose of
    removing hazardous waste from the container, as follows:
     
    i) For the purpose of meeting the requirements of this
    Section, an empty container, as defined in 35 Ill. Adm.
    Code 721.107(b), may be open to the atmosphere at any
    time (i.e., covers and closure devices are not required to be

     
    453
    secured in the closed position on an empty container).
     
    ii) In the case when discrete quantities or batches of material
    are removed from the container but the container does not
    meet the conditions to be an empty container, as defined in
    35 Ill. Adm. Code 721.107(b), the owner or operator must
    promptly secure the closure devices in the closed position
    and install covers, as applicable to the container, upon the
    completion of a batch removal after which no additional
    material will be removed from the container within 15
    minutes or the person performing the unloading operation
    leaves the immediate vicinity of the container, whichever
    condition occurs first.
     
    C) Opening of a closure device or cover is allowed when access inside
    the container is needed to perform routine activities other than
    transfer of hazardous waste. Examples of such activities include
    those times when a worker needs to open a port to measure the
    depth of or sample the material in the container, or when a worker
    needs to open a manhole hatch to access equipment inside the
    container. Following completion of the activity, the owner or
    operator must promptly secure the closure device in the closed
    position or reinstall the cover, as applicable to the container.
     
    D) Opening of a spring-loaded pressure-vacuum relief valve,
    conservation vent, or similar type of pressure relief device that
    vents to the atmosphere is allowed during normal operations for
    the purpose of maintaining the internal pressure of the container in
    accordance with the container design specifications. The device
    must be designed to operate with no detectable organic emissions
    when the device is secured in the closed position. The settings at
    which the device opens must be established so that the device
    remains in the closed position whenever the internal pressure of
    the container is within the internal pressure operating range
    determined by the owner or operator based on container
    manufacturer recommendations, applicable regulations, fire
    protection and prevention codes, standard engineering codes and
    practices, or other requirements for the safe handling of
    flammable, ignitable, explosive, reactive, or hazardous materials.
    Examples of normal operating conditions that may require these
    devices to open are during those times when the internal pressure
    of the container exceeds the internal pressure operating range for
    the container as a result of loading operations or diurnal ambient
    temperature fluctuations.
     
    E) Opening of a safety device, as defined in 35 Ill. Adm. Code

     
    454
    725.981, is allowed at any time conditions require doing so to
    avoid an unsafe condition.
     
    4) The owner or operator of containers using Container Level 1 controls must
    inspect the containers and their covers and closure devices, as follows:
     
    A) In the case when a hazardous waste already is in the container at
    the time the owner or operator first accepts possession of the
    container at the facility and the container is not emptied within 24
    hours after the container is accepted at the facility (i.e., it does not
    meet the conditions for an empty container, as specified in 35 Ill.
    Adm. Code 721.107(b)), the owner or operator must visually
    inspect the container and its cover and closure devices to check for
    visible cracks, holes, gaps, or other open spaces into the interior of
    the container when the cover and closure devices are secured in the
    closed position. The container visual inspection must be
    conducted on or before the date on which the container is accepted
    at the facility (i.e., the date when the container becomes subject to
    the Subpart CC container standards). For the purposes of this
    requirement, the date of acceptance is the date of signature that the
    facility owner or operator enters on Item 20 of the Uniform
    Hazardous Waste Manifest, as set forth in the appendix to 40 CFR
    262 (Uniform Hazardous Waste Manifest and Instructions (EPA
    Forms 8700–22 and 8700–22a and Their Instructions)),
    incorporated by reference in Appendix A to 35 Ill. Adm. Code 722
    720.111(b) (USEPA Forms 8700-22 and 8700-22A), as required
    under Section 724.171. If a defect is detected, the owner or
    operator must repair the defect in accordance with the
    requirements of subsection (c)(4)(C) of this Section.
     
    B) In the case when a container used for managing hazardous waste
    remains at the facility for a period of one year or more, the owner
    or operator must visually inspect the container and its cover and
    closure devices initially and thereafter, at least once every 12
    months, to check for visible cracks, holes, gaps, or other open
    spaces into the interior of the container when the cover and closure
    devices are secured in the closed position. If a defect is detected,
    the owner or operator must repair the defect in accordance with the
    requirements of subsection (c)(4)(C) of this Section.
     
    C) When a defect is detected for the container, cover, or closure
    devices, the owner or operator must make first efforts at repair of
    the defect no later than 24 hours after detection and repair must be
    completed as soon as possible but no later than five calendar days
    after detection. If repair of a defect cannot be completed within
    five calendar days, then the hazardous waste must be removed

     
    455
    from the container and the container must not be used to manage
    hazardous waste until the defect is repaired.
     
    5) The owner or operator must maintain at the facility a copy of the
    procedure used to determine that containers with capacity of 0.46 m
    3
    (120
    gal) or greater that do not meet applicable USDOT regulations, as
    specified in subsection (f) of this Section, are not managing hazardous
    waste in light material service.
     
    d) Container Level 2 standards.
     
    1) A container using Container Level 2 controls is one of the following:
     
    A) A container that meets the applicable USDOT regulations on
    packaging hazardous materials for transportation, as specified in
    subsection (f) of this Section.
     
    B) A container that operates with no detectable organic emissions, as
    defined in 35 Ill. Adm. Code 725.981, and determined in
    accordance with the procedure specified in subsection (g) of this
    Section.
     
    C) A container that has been demonstrated within the preceding 12
    months to be vapor-tight by using Method 27 (Determination of
    Vapor Tightness of Gasoline Delivery Tank Using Pressure-
    Vacuum Test) in appendix A to 40 CFR 60, appendix A, Method
    27 (Test Methods), incorporated by reference in 35 Ill. Adm. Code
    720.111 720.111(b), in accordance with the procedure specified in
    subsection (h) of this Section.
     
    2) Transfer of hazardous waste in or out of a container using Container Level
    2 controls must be conducted in such a manner as to minimize exposure of
    the hazardous waste to the atmosphere, to the extent practical, considering
    the physical properties of the hazardous waste and good engineering and
    safety practices for handling flammable, ignitable, explosive, reactive, or
    other hazardous materials. Examples of container loading procedures that
    the USEPA considers to meet the requirements of this subsection (d)(2)
    include using any one of the following: a submerged-fill pipe or other
    submerged-fill method to load liquids into the container; a vapor-
    balancing system or a vapor-recovery system to collect and control the
    vapors displaced from the container during filling operations; or a fitted
    opening in the top of a container through which the hazardous waste is
    filled and subsequently purging the transfer line before removing it from
    the container opening.
     
    3) Whenever a hazardous waste is in a container using Container Level 2

     
    456
    controls, the owner or operator must install all covers and closure devices
    for the container, and secure and maintain each closure device in the
    closed position, except as follows:
     
    A) Opening of a closure device or cover is allowed for the purpose of
    adding hazardous waste or other material to the container, as
    follows:
     
    i) In the case when the container is filled to the intended final
    level in one continuous operation, the owner or operator
    must promptly secure the closure devices in the closed
    position and install the covers, as applicable to the
    container, upon conclusion of the filling operation.
     
    ii) In the case when discrete quantities or batches of material
    intermittently are added to the container over a period of
    time, the owner or operator must promptly secure the
    closure devices in the closed position and install covers, as
    applicable to the container, upon either the container being
    filled to the intended final level; the completion of a batch
    loading after which no additional material will be added to
    the container within 15 minutes; the person performing the
    loading operation leaving the immediate vicinity of the
    container; or the shutdown of the process generating the
    material being added to the container, whichever condition
    occurs first.
     
    B) Opening of a closure device or cover is allowed for the purpose of
    removing hazardous waste from the container, as follows:
     
    i) For the purpose of meeting the requirements of this
    Section, an empty container, as defined in 35 Ill. Adm.
    Code 721.107(b), may be open to the atmosphere at any
    time (i.e., covers and closure devices are not required to be
    secured in the closed position on an empty container).
     
    ii) In the case when discrete quantities or batches of material
    are removed from the container but the container does not
    meet the conditions to be an empty container, as defined in
    35 Ill. Adm. Code 721.107(b), the owner or operator must
    promptly secure the closure devices in the closed position
    and install covers, as applicable to the container, upon the
    completion of a batch removal after which no additional
    material will be removed from the container within 15
    minutes or the person performing the unloading operation
    leaves the immediate vicinity of the container, whichever

     
    457
    condition occurs first.
     
    C) Opening of a closure device or cover is allowed when access inside
    the container is needed to perform routine activities other than
    transfer of hazardous waste. Examples of such activities include
    those times when a worker needs to open a port to measure the
    depth of or sample the material in the container, or when a worker
    needs to open a manhole hatch to access equipment inside the
    container. Following completion of the activity, the owner or
    operator must promptly secure the closure device in the closed
    position or reinstall the cover, as applicable to the container.
     
    D) Opening of a spring-loaded, pressure-vacuum relief valve,
    conservation vent, or similar type of pressure relief device that
    vents to the atmosphere is allowed during normal operations for
    the purpose of maintaining the internal pressure of the container in
    accordance with the container design specifications. The device
    must be designed to operate with no detectable organic emission
    when the device is secured in the closed position. The settings at
    which the device opens must be established so that the device
    remains in the closed position whenever the internal pressure of
    the container is within the internal pressure operating range
    determined by the owner or operator based on container
    manufacturer recommendations, applicable regulations, fire
    protection and prevention codes, standard engineering codes and
    practices, or other requirements for the safe handling of
    flammable, ignitable, explosive, reactive, or hazardous materials.
    Examples of normal operating conditions that may require these
    devices to open are during those times when the internal pressure
    of the container exceeds the internal pressure operating range for
    the container as a result of loading operations or diurnal ambient
    temperature fluctuations.
     
    E) Opening of a safety device, as defined in 35 Ill. Adm. Code
    725.981, is allowed at any time conditions require doing so to
    avoid an unsafe condition.
     
    4) The owner or operator of containers using Container Level 2 controls must
    inspect the containers and their covers and closure devices, as follows:
     
    A) In the case when a hazardous waste already is in the container at
    the time the owner or operator first accepts possession of the
    container at the facility and the container is not emptied within 24
    hours after the container is accepted at the facility (i.e., it does not
    meet the conditions for an empty container as specified in 35 Ill.
    Adm. Code 721.107(b)), the owner or operator must visually

     
    458
    inspect the container and its cover and closure devices to check for
    visible cracks, holes, gaps, or other open spaces into the interior of
    the container when the cover and closure devices are secured in the
    closed position. The container visual inspection must be
    conducted on or before the date on which the container is accepted
    at the facility (i.e., the date when the container becomes subject to
    the Subpart CC container standards). For the purposes of this
    requirement, the date of acceptance is the date of signature that the
    facility owner or operator enters on Item 20 of the Uniform
    Hazardous Waste Manifest, in the appendix to 40 CFR 262
    incorporated by reference in the appendix to 40 CFR 262 (Uniform
    Hazardous Waste Manifest and Instructions (USEPA Forms 8700-
    22 and 8700-22A 8700-22a and Their Instructions)), as required
    under Section 724.171. If a defect is detected, the owner or
    operator must repair the defect in accordance with the
    requirements of subsection (d)(4)(C) of this Section.
     
    B) In the case when a container used for managing hazardous waste
    remains at the facility for a period of one year or more, the owner
    or operator must visually inspect the container and its cover and
    closure devices initially and thereafter, at least once every 12
    months, to check for visible cracks, holes, gaps, or other open
    spaces into the interior of the container when the cover and closure
    devices are secured in the closed position. If a defect is detected,
    the owner or operator must repair the defect in accordance with the
    requirements of subsection (d)(4)(C) of this Section.
     
    C) When a defect is detected for the container, cover, or closure
    devices, the owner or operator must make first efforts at repair of
    the defect no later than 24 hours after detection, and repair must be
    completed as soon as possible but no later than five calendar days
    after detection. If repair of a defect cannot be completed within
    five calendar days, then the hazardous waste must be removed
    from the container and the container must not be used to manage
    hazardous waste until the defect is repaired.
     
    e) Container Level 3 standards.
     
    1) A container using Container Level 3 controls is one of the following:
     
    A) A container that is vented directly through a closed-vent system to
    a control device in accordance with the requirements of subsection
    (e)(2)(B) of this Section.
     
    B) A container that is vented inside an enclosure that is exhausted
    through a closed-vent system to a control device in accordance

     
    459
    with the requirements of subsections (e)(2)(A) and (e)(2)(B) of this
    Section.
     
    2) The owner or operator must meet the following requirements, as
    applicable to the type of air emission control equipment selected by the
    owner or operator:
     
    A) The container enclosure must be designed and operated in
    accordance with the criteria for a permanent total enclosure, as
    specified in “Procedure T—Criteria for and Verification of a
    Permanent or Temporary Total Enclosure” under appendix B to 40
    CFR 52.741, appendix B, incorporated by reference in 35 Ill. Adm.
    Code 720.111 (VOM Measurement Techniques for Capture
    Efficiency). The enclosure may have permanent or temporary
    openings to allow worker access; passage of containers through the
    enclosure by conveyor or other mechanical means; entry of
    permanent mechanical or electrical equipment; or direct airflow
    into the enclosure. The owner or operator must perform the
    verification procedure for the enclosure, as specified in Section 5.0
    to “Procedure T—Criteria for and Verification of a Permanent or
    Temporary Total Enclosure” initially when the enclosure is first
    installed and, thereafter, annually.
     
    B) The closed-vent system and control device must be designed and
    operated in accordance with the requirements of Section 724.987.
     
    3) Safety devices, as defined in 35 Ill. Adm. Code 725.981, may be installed
    and operated as necessary on any container, enclosure, closed-vent
    system, or control device used to comply with the requirements of
    subsection (e)(1) of this Section.
     
    4) Owners and operators using Container Level 3 controls in accordance with
    the provisions of this Subpart CC must inspect and monitor the closed-
    vent systems and control devices, as specified in Section 724.987.
     
    5) Owners and operators that use Container Level 3 controls in accordance
    with the provisions of this Subpart CC must prepare and maintain the
    records specified in Section 724.989(d).
     
    6) The transfer of hazardous waste into or out of a container using Container
    Level 3 controls must be conducted in such a manner as to minimize
    exposure of the hazardous waste to the atmosphere, to the extent practical
    considering the physical properties of the hazardous waste and good
    engineering and safety practices for handling flammable, ignitable,
    explosive, reactive, or other hazardous materials. Examples of container
    loading procedures that USEPA considers to meet the requirements of this

     
    460
    subsection (e)(6) include using any one of the following: the use of a
    submerged-fill pipe or other submerged-fill method to load liquids into the
    container; the use of a vapor-balancing system or a vapor-recovery system
    to collect and control the vapors displaced from the container during filling
    operations; or the use of a fitted opening in the top of a container through
    which the hazardous waste is filled and subsequently purging the transfer
    line before removing it from the container opening.
     
    f) For the purpose of compliance with subsection (c)(1)(A) or (d)(1)(A) of this
    Section, containers must be used that meet the applicable USDOT regulations on
    packaging hazardous materials for transportation, as follows:
     
    1) The container meets the applicable requirements specified by USDOT in
    49 CFR 178, “(Specifications for Packaging),” or 49 CFR 179,
    “(Specifications for Tank Cars),” both each incorporated by reference in
    35 Ill. Adm. Code 720.111 720.111(b).
     
    2) Hazardous waste is managed in the container in accordance with the
    applicable requirements specified in by USDOT subpart B of 49 CFR 107,
    subpart B, “(Exemptions”;), 49 CFR 172, “(Hazardous Materials Table,
    Special Provisions, Hazardous Materials Communications, Emergency
    Response Information, and Training Requirements”;), 49 CFR 173,
    “(Shippers—General Requirements for Shipments and Packages”;), and
    49 CFR 180, “(Continuing Qualification and Maintenance of
    Packagings),” each incorporated by reference in 35 Ill. Adm. Code
    720.111 720.111(b).
     
    3) For the purpose of complying with this Subpart CC, no exceptions to the
    49 CFR 178 or 179 regulations are allowed, except as provided for in
    subsection (f)(4) of this Section.
     
    4) For a lab pack that is managed in accordance with the USDOT
    requirements of 49 CFR 178 (Specifications for Packagings), incorporated
    by reference in 35 Ill. Adm. Code 720.111, for the purpose of complying
    with this Subpart CC, an owner or operator may comply with the
    exceptions for combination packagings specified by USDOT in 49 CFR
    173.12(b) (Exceptions for Shipments of Waste Materials), incorporated by
    reference in 35 Ill. Adm. Code 720.111 720.111(b).
     
    g) To determine compliance with the no detectable organic emissions requirement of
    subsection (d)(1)(B) of this Section, the procedure specified in Section 724.983(d)
    must be used.
     
    1) Each potential leak interface (i.e., a location where organic vapor leakage
    could occur) on the container, its cover, and associated closure devices, as
    applicable to the container, must be checked. Potential leak interfaces that

     
    461
    are associated with containers include, but are not limited to, the
    following: the interface of the cover rim and the container wall; the
    periphery of any opening on the container or container cover and its
    associated closure device; and the sealing seat interface on a spring-loaded
    pressure-relief valve.
     
    2) The test must be performed when the container is filled with a material
    having a volatile organic concentration representative of the range of
    volatile organic concentrations for the hazardous wastes expected to be
    managed in this type of container. During the test, the container cover and
    closure devices must be secured in the closed position.
     
    h) Procedure for determining a container to be vapor-tight using Method 27 of 40
    CFR 60, appendix A for the purpose of complying with subsection (d)(1)(C) of
    this Section.
     
    1) The test must be performed in accordance with Method 27 of 40 CFR 60,
    appendix A, incorporated by reference in 35 Ill. Adm. Code 720.111.
     
    2) A pressure measurement device must be used that has a precision of ± 2.5
    mm (0.098 in) water and that is capable of measuring above the pressure
    at which the container is to be tested for vapor tightness.
     
    3) If the test results determined by Method 27 indicate that the container
    sustains a pressure change less than or equal to 750 Pascals (0.11 psig)
    within five minutes after it is pressurized to a minimum of 4,500 Pascals
    (0.65 psig), then the container is determined to be vapor-tight.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.989 Recordkeeping Requirements
     
    a) Each owner or operator of a facility subject to the requirements of this Subpart
    CC must record and maintain the information specified in subsections (b) through
    (j) of this Section, as applicable to the facility. Except for air emission control
    equipment design documentation and information required by subsections (i) and
    (j) of this Section, records required by this Section must be maintained in the
    operating record for a minimum of three years. Air emission control equipment
    design documentation must be maintained in the operating record until the air
    emission control equipment is replaced or is otherwise no longer in service.
    Information required by subsections (i) and (j) of this Section must be maintained
    in the operating record for as long as the waste management unit is not using air
    emission controls specified in Sections 724.984 through 724.987, in accordance
    with the conditions specified in Section 724.980(d) or (b)(7), respectively.
     
    b) The owner or operator of a tank using air emission controls in accordance with

     
    462
    the requirements of Section 724.984 must prepare and maintain records for the
    tank that include the following information:
     
    1) For each tank using air emission controls in accordance with the
    requirements of Section 724.984, the owner or operator must record the
    following:
     
    A) A tank identification number (or other unique identification
    description, as selected by the owner or operator).
     
    B) A record for each inspection required by Section 724.984 that
    includes the following information:
     
    i) Date inspection was conducted.
     
    ii) For each defect detected during the inspection: the location
    of the defect, a description of the defect, the date of
    detection, and corrective action taken to repair the defect.
    In the event that repair of the defect is delayed in
    accordance with the requirements of Section 724.984, the
    owner or operator must also record the reason for the delay
    and the date that completion of repair of the defect is
    expected.
     
    2) In addition to the information required by subsection (b)(1) of this
    Section, the owner or operator must record the following information, as
    applicable to the tank:
     
    A) The owner or operator using a fixed roof to comply with the Tank
    Level 1 control requirements specified in Section 724.984(c) must
    prepare and maintain records for each determination for the
    maximum organic vapor pressure of the hazardous waste in the
    tank performed in accordance with the requirements of Section
    724.984(c). The records must include the date and time the
    samples were collected, the analysis method used, and the analysis
    results.
     
    B) The owner or operator using an internal floating roof to comply
    with the Tank Level 2 control requirements specified in Section
    724.984(e) must prepare and maintain documentation describing
    the floating roof design.
     
    C) Owners and operators using an external floating roof to comply
    with the Tank Level 2 control requirements specified in Section
    724.984(f) must prepare and maintain the following records:
     

     
    463
    i) Documentation describing the floating roof design and the
    dimensions of the tank.
     
    ii) Records for each seal gap inspection required by Section
    724.984(f)(3) describing the results of the seal gap
    measurements. The records must include the date that the
    measurements were performed, the raw data obtained for
    the measurements, and the calculations of the total gap
    surface area. In the event that the seal gap measurements
    do not conform to the specifications in Section
    724.984(f)(1), the records must include a description of the
    repairs that were made, the date the repairs were made, and
    the date the tank was emptied, if necessary.
     
    D) Each owner or operator using an enclosure to comply with the
    Tank Level 2 control requirements specified in Section 724.984(i)
    must prepare and maintain the following records:
     
    i) Records for the most recent set of calculations and
    measurements performed by the owner or operator to verify
    that the enclosure meets the criteria of a permanent total
    enclosure as specified in “Procedure T--Criteria for and
    Verification of a Permanent or Temporary Total Enclosure”
    under appendix B to 40 CFR 52.741, appendix B (VOM
    Measurement Techniques for Capture Efficiency),
    incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(b).
     
    ii) Records required for the closed-vent system and control
    device in accordance with the requirements of subsection
    (e) of this Section.
     
    c) The owner or operator of a surface impoundment using air emission controls in
    accordance with the requirements of Section 724.985 must prepare and maintain
    records for the surface impoundment that include the following information:
     
    1) A surface impoundment identification number (or other unique
    identification description as selected by the owner or operator).
     
    2) Documentation describing the floating membrane cover or cover design,
    as applicable to the surface impoundment, that includes information
    prepared by the owner or operator or provided by the cover manufacturer
    or vendor describing the cover design, and certification by the owner or
    operator that the cover meets the specifications listed in Section
    724.985(c).
     

     
    464
    3) A record for each inspection required by Section 724.985 that includes the
    following information:
     
    A) Date inspection was conducted.
     
    B) For each defect detected during the inspection the following
    information: the location of the defect, a description of the defect,
    the date of detection, and corrective action taken to repair the
    defect. In the event that repair of the defect is delayed in
    accordance with the provisions of Section 724.985(f), the owner or
    operator must also record the reason for the delay and the date that
    completion of repair of the defect is expected.
     
    4) For a surface impoundment equipped with a cover and vented through a
    closed-vent system to a control device, the owner or operator must prepare
    and maintain the records specified in subsection (e) of this Section.
     
    d) The owner or operator of containers using Container Level 3 air emission controls
    in accordance with the requirements of Section 724.986 must prepare and
    maintain records that include the following information:
     
    1) Records for the most recent set of calculations and measurements
    performed by the owner or operator to verify that the enclosure meets the
    criteria of a permanent total enclosure as specified in “Procedure T--
    Criteria for and Verification of a Permanent or Temporary Total
    Enclosure” under appendix B to 40 CFR 52.741, appendix B, incorporated
    by reference in 35 Ill. Adm. Code 720.111 (VOM Measurement
    Techniques for Capture Efficiency).
     
    2) Records required for the closed-vent system and control device in
    accordance with the requirements of subsection (e) of this Section.
     
    e) The owner or operator using a closed-vent system and control device in
    accordance with the requirements of Section 724.987 must prepare and maintain
    records that include the following information:
     
    1) Documentation for the closed-vent system and control device that includes
    the following:
     
    A) Certification that is signed and dated by the owner or operator
    stating that the control device is designed to operate at the
    performance level documented by a design analysis as specified in
    subsection (e)(1)(B) of this Section or by performance tests as
    specified in subsection (e)(1)(C) of this Section when the tank,
    surface impoundment, or container is or would be operating at
    capacity or the highest level reasonably expected to occur.

     
    465
     
    B) If a design analysis is used, then design documentation, as
    specified in Section 724.935(b)(4). The documentation must
    include information prepared by the owner or operator or provided
    by the control device manufacturer or vendor that describes the
    control device design in accordance with Section 724.935(b)(4)(C)
    and certification by the owner or operator that the control
    equipment meets the applicable specifications.
     
    C) If performance tests are used, then a performance test plan as
    specified in Section 724.935(b)(3) and all test results.
     
    D) Information as required by Section 724.935(c)(1) and Section
    724.935(c)(2), as applicable.
     
    E) An owner or operator must record, on a semiannual basis, the
    information specified in subsections (e)(1)(E)(i) and (e)(1)(E)(ii)
    of this Section for those planned routine maintenance operations
    that would require the control device not to meet the requirements
    of Section 724.987(c)(1)(A), (c)(1)(B), or (c)(1)(C) of this Section,
    as applicable.
     
    i) A description of the planned routine maintenance that is
    anticipated to be performed for the control device during
    the next six-month period. This description must include
    the type of maintenance necessary, planned frequency of
    maintenance, and lengths of maintenance periods.
     
    ii) A description of the planned routine maintenance that was
    performed for the control device during the previous six-
    month period. This description must include the type of
    maintenance performed and the total number of hours
    during those six months that the control device did not
    meet the requirements of Section 724.987(c)(1)(A),
    (c)(1)(B), or (c)(1)(C), as applicable, due to planned
    routine maintenance.
     
    F) An owner or operator must record the information specified in
    subsections (e)(1)(F)(i) through (e)(1)(F)(iii) of this Section for
    those unexpected control device system malfunctions that would
    require the control device not to meet the requirements of Section
    724.987 (c)(1)(A), (c)(1)(B), or (c)(1)(C) of this Section, as
    applicable.
     
    i) The occurrence and duration of each malfunction of the
    control device system.

     
    466
     
    ii) The duration of each period during a malfunction when
    gases, vapors, or fumes are vented from the waste
    management unit through the closed-vent system to the
    control device while the control device is not properly
    functioning.
     
    iii) Actions taken during periods of malfunction to restore a
    malfunctioning control device to its normal or usual
    manner of operation.
     
    G) Records of the management of carbon removed from a carbon
    adsorption system conducted in accordance with Section
    724.987(c)(3)(B).
     
    f) The owner or operator of a tank, surface impoundment, or container exempted
    from standards in accordance with the provisions of Section 724.982(c) must
    prepare and maintain the following records, as applicable:
     
    1) For tanks, surface impoundments, or containers exempted under the
    hazardous waste organic concentration conditions specified in Section
    724.982(c)(1) or (c)(2)(A) through (c)(2)(E), the owner or operator must
    record the information used for each waste determination (e.g., test results,
    measurements, calculations, and other documentation) in the facility
    operating log. If analysis results for waste samples are used for the waste
    determination, then the owner or operator must record the date, time, and
    location that each waste sample is collected in accordance with the
    applicable requirements of Section 724.983.
     
    2) For tanks, surface impoundments, or containers exempted under the
    provisions of Section 724.982(c)(2)(G) or (c)(2)(H), the owner or operator
    must record the identification number for the incinerator, boiler, or
    industrial furnace in which the hazardous waste is treated.
     
    g) An owner or operator designating a cover as “unsafe to inspect and monitor”
    pursuant to Section 724.984(l) or Section 724.985(g) must record in a log that is
    kept in the facility operating record the following information: the identification
    numbers for waste management units with covers that are designated as “unsafe
    to inspect and monitor,” the explanation for each cover stating why the cover is
    unsafe to inspect and monitor, and the plan and schedule for inspecting and
    monitoring each cover.
     
    h) The owner or operator of a facility that is subject to this Subpart CC and to the
    control device standards in federal subpart VV of 40 CFR 60, Subpart VV
    (Standards of Performance for Equipment Leaks of VOC in the Synthetic Organic
    Chemicals Manufacturing Industry) or subpart V of 40 CFR 61, Subpart V

     
    467
    (National Emission Standard for Equipment Leaks (Fugitive Emission Sources)),
    each incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(b), may
    elect to demonstrate compliance with the applicable Sections of this Subpart CC
    by documentation either pursuant to this Subpart CC, or pursuant to the
    provisions of subpart VV of 40 CFR 60, Subpart VV or subpart V of 40 CFR 61,
    Subpart V, to the extent that the documentation required by 40 CFR 60 or 61
    duplicates the documentation required by this Section.
     
    i) For each tank or container not using air emission controls specified in Sections
    724.984 through 724.987 in accordance with the conditions specified in Section
    724.980(d), the owner or operator must record and maintain the following
    information:
     
    1) A list of the individual organic peroxide compounds manufactured at the
    facility that meet the conditions specified in Section 724.980(d)(1).
     
    2) A description of how the hazardous waste containing the organic peroxide
    compounds identified pursuant to subsection (i)(1) of this Section are
    managed at the facility in tanks and containers. This description must
    include the following information:
     
    A) For the tanks used at the facility to manage this hazardous waste,
    sufficient information must be provided to describe the following
    for each tank: a facility identification number for the tank, the
    purpose and placement of this tank in the management train of this
    hazardous waste, and the procedures used to ultimately dispose of
    the hazardous waste managed in the tanks.
     
    B) For containers used at the facility to manage this hazardous waste,
    sufficient information must be provided to describe each tank: a
    facility identification number for the container or group of
    containers, the purpose and placement of this container or group of
    containers in the management train of this hazardous waste, and
    the procedures used to ultimately dispose of the hazardous waste
    managed in the containers.
     
    3) An explanation of why managing the hazardous waste containing the
    organic peroxide compounds identified pursuant to subsection (i)(1) of
    this Section in the tanks or containers identified pursuant to subsection
    (i)(2) of this Section would create an undue safety hazard if the air
    emission controls specified in Sections 724.984 through 724.987 were
    installed and operated on these waste management units. This explanation
    must include the following information:
     
    A) For tanks used at the facility to manage this hazardous waste,
    sufficient information must be provided to explain the following:

     
    468
    how use of the required air emission controls on the tanks would
    affect the tank design features and facility operating procedures
    currently used to prevent an undue safety hazard during
    management of this hazardous waste in the tanks; and why
    installation of safety devices on the required air emission controls,
    as allowed under this Subpart CC, would not address those
    situations in which evacuation of tanks equipped with these air
    emission controls is necessary and consistent with good
    engineering and safety practices for handling organic peroxides.
     
    B) For containers used at the facility to manage this hazardous waste,
    sufficient information must be provided to explain the following:
    how use of the required air emission controls on the tanks would
    affect the container design features and handling procedures
    currently used to prevent an undue safety hazard during
    management of this hazardous waste in the containers; and why
    installation of safety devices on the required air emission controls,
    as allowed under this Subpart CC, would not address those
    situations in which evacuation of containers equipped with these
    air emission controls is necessary and consistent with good
    engineering and safety practices for handling organic peroxides.
     
    j) For each hazardous waste management unit not using air emission controls
    specified in Sections 724.984 through 724.987 in accordance with the
    requirements of Section 724.980(b)(7), the owner and operator must record and
    maintain the following information:
     
    1) The certification that the waste management unit is equipped with and
    operating air emission controls in accordance with the requirements of an
    applicable federal Clean Air Act regulation codified under 40 CFR 60, 61,
    or 63.
     
    2) An identification of the specific federal requirements codified under 40
    CFR 60, 61, or 63 with which the waste management unit is in
    compliance.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART DD: CONTAINMENT BUILDINGS
     
    Section 724.1101 Design and Operating Standards
     
    a) All containment buildings must comply with the following design and operating
    standards:
     
    1) The containment building must be completely enclosed with a floor, walls,

     
    469
    and a roof to prevent exposure to the elements (e.g. precipitation, wind,
    run on) and to assure containment of managed wastes.
     
    2) The floor and containment walls of the unit, including the secondary
    containment system if required under subsection (b) of this Section, must
    be designed and constructed of materials of sufficient strength and
    thickness to support themselves, the waste contents, and any personnel
    and heavy equipment that operate within the unit, and to prevent failure
    due to pressure gradients, settlement, compression, or uplift, physical
    contact with the hazardous wastes to which they are exposed; climatic
    conditions; and the stresses of daily operation, including the movement of
    heavy equipment within the unit and contact of such equipment with
    containment walls. The unit must be designed so that it has sufficient
    structural strength to prevent collapse or other failure. All surfaces to be
    in contact with hazardous wastes must be chemically compatible with
    those wastes. The containment building must meet the structural integrity
    requirements established by professional organizations generally
    recognized by the industry such as the American Concrete Institute (ACI)
    and the American Society of Testing Materials (ASTM). If appropriate to
    the nature of the waste management operation to take place in the unit, an
    exception to the structural strength requirement may be made for light-
    weight doors and windows that meet the following criteria:
     
    A) They provide an effective barrier against fugitive dust emissions
    under subsection (c)(1)(C) of this Section; and
     
    B) The unit is designed and operated in a fashion that assures that
    wastes will not actually come in contact with these openings.
     
    3) Incompatible hazardous wastes or treatment reagents must not be placed
    in the unit or its secondary containment system if they could cause the unit
    or secondary containment system to leak, corrode, or otherwise fail.
     
    4) A containment building must have a primary barrier designed to withstand
    the movement of personnel, waste, and handling equipment in the unit
    during the operating life of the unit and appropriate for the physical and
    chemical characteristics of the waste to be managed.
     
    b) For a containment building used to manage hazardous wastes containing free
    liquids or treated with free liquids (the presence of which is determined by the
    paint filter test, a visual examination, or other appropriate means), the owner or
    operator must include the following:
     
    1) A primary barrier designed and constructed of materials to prevent the
    migration of hazardous constituents into the barrier (e.g., a geomembrane
    covered by a concrete wear surface).

     
    470
     
    2) A liquid collection and removal system to minimize the accumulation of
    liquid on the primary barrier of the containment building, as follows:
     
    A) The primary barrier must be sloped to drain liquids to the
    associated collection system; and
     
    B) Liquids and waste must be collected and removed to minimize
    hydraulic head on the containment system at the earliest
    practicable time.
     
    3) A secondary containment system including a secondary barrier designed
    and constructed to prevent migration of hazardous constituents into the
    barrier, and a leak detection system that is capable of detecting failure of
    the primary barrier and collecting accumulated hazardous wastes and
    liquids at the earliest practicable time.
     
    A) The requirements of the leak detection component of the secondary
    containment system are satisfied by installation of a system that is,
    at a minimum, as follows:
     
    i) It is constructed with a bottom slope of 1 percent or more;
    and
     
    ii) It is constructed of a granular drainage material with a
    hydraulic conductivity of 1 x 10
    -2
    cm/sec or more and a
    thickness of 12 inches (30.5 cm) or more, or constructed of
    synthetic or geonet drainage materials with a transmissivity
    of 3 x 10
    -5
    m
    2
    /sec or more.
     
    B) If treatment is to be conducted in the building, an area in which
    such treatment will be conducted must be designed to prevent the
    release of liquids, wet materials, or liquid aerosols to other
    portions of the building.
     
    C) The secondary containment system must be constructed of
    materials that are chemically resistant to the waste and liquids
    managed in the containment building and of sufficient strength and
    thickness to prevent collapse under the pressure exerted by
    overlaying materials and by any equipment used in the
    containment building. (Containment buildings can serve as
    secondary containment systems for tanks placed within the
    building under certain conditions. A containment building can
    serve as an external liner system for a tank, provided it meets the
    requirements of Section 724.193(d)(1). In addition, the
    containment building must meet the requirements of Section

     
    471
    724.193(b) and Sections 724.193(c)(1) and (c)(2) to be an
    acceptable secondary containment system for a tank.)
     
    4) For existing units other than 90-day generator units, USEPA may delay
    the secondary containment requirement for up to two years, based on a
    demonstration by the owner or operator that the unit substantially meets
    the standards of this Subpart DD. In making this demonstration, the
    owner or operator must have done the following:
     
    A) Provided written notice to USEPA of their request by November
    16, 1992. This notification must have described the unit and its
    operating practices with specific reference to the performance of
    existing systems, and specific plans for retrofitting the unit with
    secondary containment;
     
    B) Responded to any comments from USEPA on these plans within
    30 days; and
     
    C) Fulfilled the terms of the revised plans, if such plans are approved
    by USEPA.
     
    c) An owner or operator of a containment building must do the following:
     
    1) Use controls and practice to ensure containment of the hazardous waste
    within the unit, and at a minimum:
     
    A) Maintain the primary barrier to be free of significant cracks, gaps,
    corrosion, or other deterioration that could cause hazardous waste
    to be release from the primary barrier;
     
    B) Maintain the level of the stored or treated hazardous waste within
    the containment walls of the unit so that the height of any
    containment wall is not exceeded;
     
    C) Take measures to prevent the tracking of hazardous waste out of
    the unit by personnel or by equipment used in handling the waste.
    An area must be designated to decontaminate equipment and any
    rinsate must be collected and properly managed; and
     
    D) Take measures to control fugitive dust emissions such that any
    openings (doors, windows, vents, cracks, etc.) exhibit no visible
    emissions (see Method 22 (Visual Determination of Fugitive
    Emissions from Material Sources and Smoke Emissions from
    Flares) in appendix A to 40 CFR 60, appendix A, Method 22 (Test
    Methods) - Visual Determination of Fugitive Emissions from
    Material Sources and Smoke Emissions from Flares), incorporated

     
    472
    by reference in 35 Ill. Adm. Code 720.111(b). In addition, all
    associated particulate collection devices (e.g., fabric filter,
    electrostatic precipitator, etc.) must be operated and maintained
    with sound air pollution control practices (see 40 CFR 60 for
    guidance). This state of no visible emissions must be maintained
    effectively at all times during routine operating and maintenance
    conditions, including when vehicles and personnel are entering and
    exiting the unit.
     
    BOARD NOTE: At 40 CFR 264.1101(c)(1)(iv) (2004), USEPA
    cites “40 CFR part 60, subpart 292.” At 57 Fed. Reg. 37217 (Aug.
    18, 1992), USEPA repeats this citation in the preamble discussion
    of adoption of the rules. No such provision exists in the Code of
    Federal Regulations. The Board has chosen to use the more
    general citation: “40 CFR 60.”
     
    2) Obtain certification by a qualified registered professional engineer (PE)
    that the containment building design meets the requirements of
    subsections (a) through (c) of this Section. For units placed into operation
    prior to February 18, 1993, this certification must have been placed in the
    facility’s operating record (on-site files for generators that are not formally
    required to have operating records) no later than 60 days after the date of
    initial operation of the unit. After February 18, 1993, PE certification has
    been required prior to operation of the unit.
     
    3) Throughout the active life of the containment building, if the owner or
    operator detects a condition that could lead to or has caused a release of
    hazardous waste, must repair the condition promptly. In addition,
    however the following is required:
     
    A) Upon detection of a condition that has caused to a release of
    hazardous wastes (e.g., upon detection of leakage from the primary
    barrier) the owner or operator must do the following:
     
    i) Enter a record of the discovery in the facility operating
    record;
     
    ii) Immediately remove the portion of the containment
    building affected by the condition from service;
     
    iii) Determine what steps must be taken to repair the
    containment building, remove any leakage from the
    secondary collection system, and establish a schedule for
    accomplishing the cleanup and repairs; and
     
    iv) Within seven days after the discovery of the condition,

     
    473
    notify the Agency in writing of the condition, and within 14
    working days, provide a written notice to the Agency with
    a description of the steps taken to repair the containment
    building, and the schedule for accomplishing the work.
     
    B) The Agency must review the information submitted, make a
    determination in accordance with Section 34 of the Act, regarding
    whether the containment building must be removed from service
    completely or partially until repairs and cleanup are complete, and
    notify the owner or operator of the determination and the
    underlying rationale in writing.
     
    C) Upon completing all repairs and cleanup the owner and operator
    must notify the Agency in writing and provide a verification,
    signed by a qualified, registered professional engineer, that the
    repairs and cleanup have been completed according to the written
    plan submitted in accordance with subsection (c)(3)(A)(iv) of this
    Section.
     
    4) Inspect and record in the facility’s operating record, at least once every
    seven days, data gathered from monitoring equipment and leak detection
    equipment, as well as the containment building and the area immediately
    surrounding the containment building, to detect signs of releases of
    hazardous waste.
     
    d) For containment buildings that contain areas both with and without secondary
    containment, the owner or operator must do the following:
     
    1) Design and operate each area in accordance with the requirements
    enumerated in subsections (a) through (c) of this Section;
     
    2) Take measures to prevent the release of liquids or wet materials into areas
    without secondary containment; and
     
    3) Maintain in the facility’s operating log a written description of the
    operating procedures used to maintain the integrity of areas without
    secondary containment.
     
    e) Notwithstanding any other provision of this Subpart DD the Agency must not
    require secondary containment for a permitted containment building where the
    owner operator demonstrates that the only free liquids in the unit are limited
    amounts of dust suppression liquids required to meet occupational health and
    safety requirements, and where containment of managed wastes and liquids can
    be assured without a secondary containment system.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)

     
    474
     
    Section 724.Appendix A Recordkeeping Instructions
     
    See appendix I to 40 CFR 264, Appendix I (Recordkeeping Instructions), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.Appendix D Cochran’s Approximation to the Behrens-Fisher Student’s T-Test
     
    See appendix IV to 40 CFR 264, Appendix IV (Cochran’s Approximation to the Behrens-Fisher
    Students’ T-Test), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.Appendix E Examples of Potentially Incompatible Waste
     
    See appendix V to 40 CFR 264, Appendix V (Examples of Potentially Incompatible Waste),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 724.Appendix I Groundwater Monitoring List
     
    a)
    The regulatory requirements pertain only to the list of substances; the right hand
    columns (Methods and PQL) are given for informational purposes only. See also
    subsections (e) and (f) of this Section.
     
    ba) Common names are those widely used in government regulations, scientific
    publications and commerce; synonyms exist for many chemicals.
     
    cb) “CAS RN” means “Chemical Abstracts Service Registry Number.” Where
    “total” is entered, all species in the groundwater that contain this element are
    included.
     
    dc) CAS index names are those used in the 9th Cumulative index.
     
    e)
    “Suggested Methods” refer to analytical procedure numbers used in “Test
    Methods for Solid Waste,” SW-846, incorporated by reference in 35 Ill. Adm.
    Code 720.111. Analytical details can be found in “Test Methods,” and in
    documentation on file with USEPA. The packed column gas chromatography
    methods 8010, 8020, 8030, 8040, 8060, 8080, 8090, 8110, 8120, 8140, 8150,
    8240, and 8250 were in Update IIB of SW-846. However, in Update III, USEPA
    replaced these methods with “capillary column gas chromatography (GC)
    methods,” as the suggested methods.
     

     
    475
    f)
    Practical Quantitation Limits (“PQLs”) are the lowest concentrations of analytes
    in groundwater that can be reliably determined within specified limits of precision
    and accuracy by the indicated methods under routine laboratory operating
    conditions. The POLs listed are generally stated to one significant figure.
    Caution: The PQL values in many cases are based only on a general estimate for
    the method and not on a determination for individual compounds; PQLs are not a
    part of the regulation.
     
    gd) PCBs (CAS RN 1336-36-3). This category contains congener chemicals,
    including constituents Aroclor-1016 (CAS RN 12674-11-2), Aroclor-1221 (CAS
    RN 11104-28-2), Aroclor-1232 (CAS RN 11141-16-5), Aroclor-1242 (CAS RN
    53469-21-9), Aroclor-1248 (CAS RN 12672-29-6), Aroclor-1254 (CAS RN
    11097-69-1) and Aroclor-1260 (CAS RN 11096-82-5). The PQL shown is an
    average value for PCB congeners.
     
    he) PCDDs. This category includes congener chemicals, including tetrachloro-
    dibenzo-p-dioxins (see also 2,3,7,8-TCDD), pentachlorodibenzo-p-dioxins and
    hexachlorodibenzo-p-dioxins. The PQL shown is an average value for PCDD
    congeners.
     
    if) PCDFs. This category contains congener chemicals, including tetrachloro-
    dibenzofurans, pentachlorodibenzofurans, and hexachlorodibenzofurans. The
    PQL shown is an average for all PCDF congeners.
     
    Common Name CAS RN
    Chemical Abstracts Service
    Index Name
    Suggested
    Methods
    PQL
    (μg/L)
     
    Acenaphthene 83-32-9 Acenaphthylene, 1,2-di-
    hydro-
    8100
    8270
    200.
    10.
     
    Acenaphthylene 208-96-8 Acenaphthylene 8100
    8270
    200.
    10.
     
    Acetone 67-64-1
    2-Propanone 8240 100.
     
    Acetophenone 98-86-2 Ethanone, 1-phenyl- 8270 10.
     
    Acetonitrile; Methyl
    cyanide
    75-05-8 Acetonitrile 8015 100.
     
    2-Acetylaminofluorene; 2-
    AAF
    53-96-3 Acetamide, N-9H-fluoren-
    2-yl-
    8270 10.
     
    Acrolein 107-02-8
    2-Propenal 8030
    8240
    5.
    5.
     

     
    476
    Acrylonitrile 107-13-1
    2-Propenenitrile 8030
    8240
    5.
    5.
     
    Aldrin 309-00-2 1,4:5,8-Dimethano-
    naphthalene, 1,2,3,4,10,10-
    hexachloro-1,4,4a,5,8,8a-
    hexahydro-
    (1
    α
    ,4
    α
    ,4a
    β
    ,5
    α
    ,8
    α
    ,8a
    β
    )-
    8080
    8270
    0.05
    10.
     
    Allyl chloride 107-05-1
    1-Propene, 3-chloro- 8010
    8240
    5.
    100.
     
    4-Aminobiphenyl 92-67-1 [1,1'-Biphenyl]-4-amine 8270 10.
     
    Aniline 62-53-3 Benzenamine 8270 10.
     
    Anthracene 120-12-7 Anthracene 8100
    8270
    200.
    10.
     
    Antimony (Total) Antimony 6010
    7040
    7041
    300.
    2000.
    30.
     
    Aramite 140-57-8 Sulfurous acid, 2-chloro-
    ethyl 2-[4-(1,1-dimethyl-
    ethyl)phenoxy]-1-methyl-
    ethyl ester
    8270 10.
     
    Arsenic (Total) Arsenic 6010
    7060
    7061
    500.
    10.
    20.
     
    Barium (Total) Barium 6010
    7080
    20.
    1000.
     
    Benzene 71-43-2 Benzene 8020
    8240
    2.
    5.
     
    Benzo[a]anthracene; Benz-
    anthracene
    56-55-3 Benz[a]anthracene 8100
    8270
    200.
    10.
     
    Benzo[b]fluoranthene 205-99-2 Benz[e]acephenanthrylene 8100
    8270
    200.
    10.
     

     
    477
    Benzo[k]fluoranthene 207-08-9 Benzo[k]fluoranthene 8100
    8270
    200.
    10.
     
    Benzo[ghi]perylene 191-24-2 Benzo[ghi]perylene 8100
    8270
    200.
    10.
     
    Benzo[a]pyrene 50-32-8 Benzo[a]pyrene 8100
    8270
    200.
    10.
     
    Benzyl alcohol 100-51-6 Benzenemethanol 8270 20.
     
    Beryllium (Total) Beryllium 6010
    7090
    7091
    3.
    50.
    2.
     
    α
    -BHC
    319-84-6 Cyclohexane, 1,2,3,4,5,6-
    hexachloro-,
    (1
    α
    ,2
    α
    ,3
    β
    ,4
    α
    ,5
    β
    ,6
    β
    )-
    8080
    8250
    0.05
    10.
     
    β
    -BHC
    319-85-7 Cyclohexane, 1,2,3,4,5,6-
    hexachloro-,
    (1
    α
    ,2
    β
    ,3
    α
    ,4
    β
    ,5
    α
    ,6
    β
    )-
    8080
    8250
    0.05
    40.
     
    δ
    -BHC
    319-86-8 Cyclohexane, 1,2,3,4,5,6-
    hexachloro-,
    (1
    α
    ,2
    α
    ,3
    α
    ,4
    β
    ,5
    α
    ,6
    β
    )-
    8080
    8250
    0.1
    30.
     
    γ
    -BHC; Lindane
    58-89-9 Cyclohexane, 1,2,3,4,5,6-
    hexachloro-,
    (1
    α
    ,2
    α
    ,3
    β
    ,4
    α
    ,5
    α
    ,6
    β
    )-
    8080
    8250
    0.05
    10.
     
    Bis(2-chloroethoxy)-
    methane
    111-91-1 Ethane, 1,1'-[methylenebis-
    (oxy)]bis[2-chloro-
    8270 10.
     
    Bis(2-chloroethyl)ether 111-44-4 Ethane, 1,1'-oxybis[2-
    chloro-
    8270 10.
     
    Bis(2-chloro-1-methylethyl)
    ether; 2,2'-Dichlorodiiso-
    propyl ether
    108-60-1 Propane, 2,2'-oxybis[1-
    chloro-
    8010
    8270
    100.
    10.
     
    Bis(2-ethylhexyl) phthalate 117-81-7 1,2-Benzenedicarboxylic
    acid, bis(2-ethylhexyl) ester
    8060
    8270
    20.
    10.
     

     
    478
    Bromodichloromethane 75-27-4 Methane, bromodichloro- 8010
    8240
    1.
    5.
     
    Bromoform; Tribromo-
    methane
    75-25-2 Methane, tribromo- 8010
    8240
    2.
    5.
     
    4-Bromophenyl phenyl
    ether
    101-55-3 Benzene, 1-bromo-4-
    phenoxy-
    8270 10.
     
    Butyl benzyl phthalate;
    Benzyl butyl phthalate
    85-68-7 1,2-Benzenedicarboxylic
    acid, butyl phenylmethyl
    ester
    8060
    8270
    5.
    10.
     
    Cadmium Total Cadmium 6010
    7130
    7131
    40.
    50.
    1.
     
    Carbon disulfide 75-15-0 Carbon disulfide 8240 5.
     
    Carbon tetrachloride 56-23-5 Methane, tetrachloro- 8010
    8240
    1.
    5.
     
    Chlordane 57-74-9 4,7-Methano-1H-
    indene,1,2,4,5,6,7,8,8-octa-
    chloro-2,3,3a,4,7,7a-hexa-
    hydro-
    8080
    8250
    0.1
    10.
     
    p-Chloroaniline 106-47-8 Benzeneamine, 4-chloro- 8270 20.
     
    Chlorobenzene 108-90-7 Benzene, chloro- 8010
    8020
    8240
    2.
    2.
    5.
     
    Chlorobenzilate 510-15-6 Benzeneacetic acid, 4-
    chloro-
    α
    -(4-chlorophenyl)-
    α
    -hydroxy-, ethylf ester
    8270 10.
     
    p-Chloro-m-cresol 59-50-7 Phenol, 4-chloro-3-methyl- 8040
    8270
    5.
    20.
     
    Chloroethane; Ethyl
    chloride
    75-00-3 Ethane, chloro- 8010
    8240
    5.
    10.
     
    Chloroform 67-66-3 Methane, trichloro- 8010
    8240
    0.5
    5.
     

     
    479
    2-Chloronapthalene 91-58-7 Naphthalene, 2-chloro- 8120
    8270
    10.
    10.
     
    2-Chlorophenol 95-57-8 Phenol, 2-chloro- 8040
    8270
    5.
    10.
     
    4-Chlorophenyl phenyl
    ether
    7005-72-3 Benzene, 1-chloro-4-
    phenoxy-
    8270 10.
     
    Chloroprene 126-99-8 1,3-Butadiene, 2-chloro- 8010
    8240
    50.
    5.
     
    Chromium (Total) Chromium 6010
    7190
    7191
    70.
    500.
    10.
     
    Chrysene 218-01-9 Chrysene 8100
    8270
    200.
    10.
     
    Cobalt (Total) Cobalt 6010
    7200
    7201
    70.
    500.
    10.
     
    Copper (Total) Copper 6010
    7210
    60.
    200.
     
    m-Cresol 108-39-4 Phenol, 3-methyl- 8270 10.
     
    o-Cresol 95-48-7 Phenol,
    2-methyl- 8270 10.
     
    p-Cresol 106-44-5 Phenol, 4-methyl- 8270 10.
     
    Cyanide 57-12-5 Cyanide 9010 40.
     
    2,4-D; 2,4-Dichloro-
    phenoxyacetic acid
    94-75-7 Acetic acid, (2,4-dichloro-
    phenoxy)-
    8150 10.
     
    4,4'-DDD 72-54-8 Benzene, 1,1'-(2,2-dichloro-
    ethylidene)bis[4-chloro-
    8080
    8270
    0.1
    10.
     
    4,4'-DDE 72-55-9 Benzene, 1,1'-(dichloro-
    ethylidene)bis[4-chloro-
    8080
    8270
    0.05
    10.
     

     
    480
    4,4'-DDT 50-29-3 Benzene, 1,1'-(2,2,2-tri-
    chloroethylidene)bis[4-
    chloro-
    8080
    8270
    0.1
    10.
     
    Diallate 2303-16-4 Carbamothioic acid, bis(1-
    methylethyl)-, S-(2,3-di-
    chloro--2-propenyl) ester
    8270 10.
     
    Dibenz[a,h]anthracene 53-70-3 Dibenz[a,h]anthracene 8100
    8270
    200.
    10.
     
    Dibenzofuran 132-64-9 Dibenzofuran 8270 10.
     
    Dibromochloromethane;
    Chlorodibromomethane
    124-48-1 Methane, dibromochloro- 8010
    8240
    1.
    5.
     
    1,2-Dibromo-3-chloro-
    propane; DBCP
    96-12-8 Propane, 1,2-dibromo-3-
    chloro-
    8010
    8240
    8270
    100.
    5.
    10.
     
    1,2-Dibromoethane;
    Ethylene dibromide
    106-93-4 Ethane, 1,2-dibromo- 8010
    8240
    10.
    5.
     
    Di-n-butyl phthalate 84-74-2 1,2-Benzenedicarboxylic
    acid, dibutyl ester
    8060
    8270
    5.
    10.
     
    o-Dichlorobenzene 95-50-1 Benzene, 1,2-dichloro- 8010
    8020
    8120
    8270
    2.
    5.
    10.
    10.
     
    m-Dichlorobenzene 541-73-1 Benzene, 1,3-dichloro- 8010
    8020
    8120
    8270
    5.
    5.
    10.
    10.
     
    p-Dichlorobenzene 106-46-7 Benzene, 1,4-dichloro- 8010
    8020
    8120
    8270
    2.
    5.
    15.
    10.
     
    3,3'-Dichlorobenzidine 91-94-1 [1,1'-Biphenyl]-4,4'-di-
    amine, 3,3'-dichloro-
    8270 20.
     

     
    481
    trans-1,4-Dichloro-2-butene 110-57-6
    2-Butene, 1,4-dichloro-,
    (E)-
    8240 5.
     
    Dichlorodifluoromethane 75-71-8 Methane, dichlorodifluoro- 8010
    8240
    10.
    5.
     
    1,1-Dichloroethane 75-34-3 Ethane, 1,1-dichloro- 8010
    8240
    1.
    5.
     
    1,2-Dichloroethane;
    Ethylene dichloride
    107-06-2 Ethane, 1,2-dichloro- 8010
    8240
    0.5
    5.
     
    1,1-Dichloroethylene;
    Vinylidene chloride
    75-35-4 Ethene, 1,1-dichloro- 8010
    8240
    1.
    5.
     
    trans-1,2-Dichloroethylene 156-60-5 Ethene, 1,2-dichloro-, (E)- 8010
    8240
    1.
    5.
     
    2,4-Dichlorophenol 120-83-2 Phenol, 2,4-dichloro- 8040
    8270
    5.
    10.
     
    2,6-Dichlorophenol 87-65-0 Phenol, 2,6-dichloro- 8270 10.
     
    1,2-Dichloropropane 78-87-5 Propane, 1,2-dichloro- 8010
    8240
    0.5
    5.
     
    cis-1,3-Dichloropropene 10061-01-5
    1-Propene, 1,3-dichloro-,
    (Z)-
    8010
    8240
    20.
    5.
     
    trans-1,3-Dichloropropene 10061-02-6
    1-Propene, 1,3-dichloro-,
    (E)-
    8010
    8240
    5.
    5.
     
    Dieldrin 60-57-1 2,7:3,6-Dimethanonaphth-
    [2,3-b]oxirene, 3,4,5,6,9,9-
    hexachloro-
    1a,2,2a,3,6,6a,7,7a-octa-
    hydro-
    ,(1a
    α
    ,2
    β
    ,2a
    α
    ,3
    β
    ,6
    β
    ,6a
    α
    ,7
    β
    ,
    7a
    α
    )-
    8080
    8270
    0.05
    10.
     
    Diethyl phthalate 84-66-2 1,2-Benzenedicarboxylic
    acid, diethyl ester
    8060
    8270
    5.
    10.
     

     
    482
    O,O-Diethyl O-2-pyrazinyl
    phosphorothioate;
    Thionazin
    297-97-2 Phosphorothioic acid, O,O-
    diethyl O-pyrazinyl ester
    8270 10.
     
    Dimethoate 60-51-5 Phosphorodithioic acid,
    O,O-dimethyl S-[2-(methyl-
    amino)-2-oxoethyl] ester
    8270 10.
     
    p-(Dimethylamino)-
    azobenzene
    60-11-7 Benzenamine, N,N-di-
    methyl-4-(phenylazo)-
    8270 10.
     
    7,12-Dimethylbenz[a]-
    anthracene
    57-97-6 Benz[a]anthracene,7,12-di-
    methyl-
    8270 10.
     
    3,3'-Dimethylbenzidine 119-93-7 [1,1'-Biphenyl]-4,4'-di-
    amine, 3,3'-dimethyl-
    8270 10.
     
    α
    ,
    α
    -Dimethylphenethyl-
    amine
    122-09-8
    Benzeneethanamine,
    α
    ,
    α
    -
    dimethyl-
    8270 10.
     
    2,4-Dimethylphenol 105-67-9 Phenol, 2,4-dimethyl- 8040
    8270
    5.
    10.
     
    Dimethyl phthalate 131-11-3 1,2-Benzenedicarboxylic
    acid, dimethyl ester
    8060
    8270
    5.
    10.
     
    m-Dinitrobenzene 99-65-0 Benzene, 1,3-dinitro- 8270 10.
     
    4,6-Dinitro-o-cresol 534-52-1 Phenol, 2-methyl-4,6-di-
    nitro-
    8040
    8270
    150.
    50.
     
    2,4-Dinitrophenol 51-28-5 Phenol, 2,4-dinitro- 8040
    8270
    150.
    50.
     
    2,4-Dinitrotoluene 121-14-2 Benzene, 1-methyl-2,4-di-
    nitro-
    8090
    8270
    0.2
    10.
     
    2,6-Dinitrotoluene 606-20-2 Benzene, 2-methyl-1,3-di-
    nitro-
    8090
    8270
    0.1
    10.
     
    Dinoseb; DNBP; 2-sec-
    Butyl-4,6-dinitrophenol
    88-85-7 Phenol, 2-(1-methylpropyl)-
    4,6-dinitro-
    8150
    8270
    1.
    10.
     
    Di-n-octyl phthalate 117-84-0 1,2-Benzenedicarboxylic
    acid, dioctyl ester
    8060
    8270
    30.
    10.
     

     
    483
    1,4-Dioxane 123-91-1 1,4-Dioxane 8015 150.
     
    Diphenylamine 122-39-4 Benzeneamine, N-phenyl- 8270 10.
     
    Disulfoton 298-04-4 Phosphorodithioic acid,
    O,O-diethyl S-[2-(ethyl-
    thio)ethyl] ester
    8140
    8270
    2.
    10.
     
    Endosulfan I 959-98-8 6,9-Methano-2,4,3-benzodi-
    oxathiepin,6,7,8,9,10,10-
    hexachloro-1,5,5a,6,9,9a-
    hexahydro-, 3-oxide,
    (3
    α
    ,5a
    β
    ,6
    α
    ,9
    α
    ,9a
    β
    )-
    8080
    8250
    0.1
    10.
     
    Endosulfan II 33213-65-9
    6,9-Methano-2,4,3-benzodi-
    oxathiepin,6,7,8,9,10,10-
    hexachloro-1,5,5a,6,9,9a-
    hexahydro-, 3-oxide,
    (3
    α
    ,5a
    α
    ,6
    β
    ,9
    β
    ,9a
    α
    )-
    8080 0.05
     
    Endosulfan sulfate 1031-07-8 6,9-Methano-2,4,3-benzodi-
    oxathiepin,6,7,8,9,10,10-
    hexachloro-1,5,5a,6,9,9a-
    hexahydro-,3,3-dioxide
    8080
    8270
    0.5
    10.
     
    Endrin 72-20-8 2,7:3,6-Dimethanonaphth-
    [2,3-b]oxirene, 3,4,5,6,9,9-
    hexachloro-
    1a,2,2a,3,6,6a,7,7a-octa-
    hydro-,
    (1a
    α
    ,2
    β
    ,2a
    β
    ,3
    α
    ,6
    α
    ,6a
    β
    ,7
    β
    ,
    7a
    α
    )-
    8080
    8250
    0.1
    10.
     
    Endrin aldehyde 7421-93-4 1,2,4-Methanocyclopenta-
    [cd]pentalene-5-carbox-
    aldehyde, 2,2a,3,3,4,7-hexa-
    chlorodecahydro-,
    (1
    α
    ,2
    β
    ,2a
    β
    ,4
    β
    ,4a
    β
    ,5
    β
    ,6a
    β
    ,6
    b
    β
    ,7R)-
    8080
    8270
    0.2
    10.
     
    Ethylbenzene 100-41-4 Benzene, ethyl- 8020
    8240
    2.
    5.
     

     
    484
    Ethyl methacrylate 97-63-2
    2-Propenoic acid, 2-methyl-
    , ethyl ester
    8015
    8240
    8270
    10.
    5.
    10.
     
    Ethyl methanesulfonate 62-50-0 Methanesulfonic acid, ethyl
    ester
    8270 10.
     
    Famphur 52-85-7 Phosphorothioic acid, O-[4-
    [(dimethylamino)sulfonyl]-
    phenyl]-O,O-dimethyl ester
    8270 10.
     
    Fluoranthene 206-44-0 Fluoranthene 8100
    8270
    200.
    10.
     
    Fluorene 86-73-7 9H-Fluorene 8100
    8270
    200.
    10.
     
    Heptachlor 76-44-8 4,7-Methano-1H-indene,
    1,4,5,6,7,8,8-heptachloro-
    3a,4,7,7a-tetrahydro-
    8080
    8270
    0.05
    10.
     
    Heptachlor epoxide 1024-57-3 2,5-Methano-2H-indeno-
    [1,2-b]oxirene,
    2,3,4,5,6,7,7-heptachloro-
    1a,1b,5,5a,6,6a-hexahydro-,
    (1a
    α
    ,1b
    β
    ,2
    α
    ,5
    α
    ,5a
    β
    ,6
    β
    ,6a
    α
    )-
    8080
    8270
    1.
    10.
     
    Hexachlorobenzene 118-74-1 Benzene, hexachloro- 8120
    8270
    0.5
    10.
     
    Hexachlorobutadiene 87-68-3 1,3-Butadiene, 1,1,2,3,4,4-
    hexachloro-
    8120
    8270
    5.
    10.
     
    Hexachlorocyclopentadiene 77-47-4 1,3-Cyclopentadiene,
    1,2,3,4,5,5-hexachloro-
    8120
    8270
    5.
    10.
     
    Hexachloroethane 67-72-1 Ethane, hexachloro- 8120
    8270
    0.5
    10.
     
    Hexachlorophene 70-30-4 Phenol, 2,2'-methylenebis-
    [3,4,6-trichloro-
    8270 10.
     
    Hexachloropropene 1888-71-7
    1-Propene, 1,1,2,3,3,3-
    hexachloro-
    8270 10.
     

     
    485
    2-Hexanone 591-78-6
    2-Hexanone 8240 50.
     
    Indeno(1,2,3-cd)pyrene 193-39-5 Indeno[1,2,3-cd]pyrene 8100
    8270
    200.
    10.
     
    Isobutyl alcohol 78-83-1
    1-Propanol, 2-methyl- 8015 50.
     
    Isodrin 465-73-6 1,4,5,8-Dimethano-
    naphthalene, 1,2,3,4,10,10-
    hexachloro-1,4,4a,5,8,8a-
    hexahydro-
    (1
    α
    ,4
    α
    ,4a
    β
    ,5
    β
    ,8
    β
    ,8a
    β
    )-
    8270 10.
     
    Isophorone 78-59-1
    2-Cyclohexen-1-one, 3,5,5-
    trimethyl-
    8090
    8270
    60.
    10.
     
    Isosafrole 120-58-1 1,3-Benzodioxole, 5-(1-
    propenyl)-
    8270 10.
     
    Kepone 143-50-0 1,3,4-Metheno-2H-cyclo-
    buta-[c,d]pentalen-2-one,
    1,1a,3,3a,4,5,5,5a,5b,6-
    decachlorooctahydro-
    8270 10.
     
    Lead (Total) Lead 6010
    7420
    7421
    40.
    1000.
    10.
     
    Mercury (Total) Mercury 7470 2.
     
    Methacrylonitrile 126-96-7
    2-Propenenitrile, 2-methyl- 8015
    8240
    5.
    5.
     
    Methapyrilene 91-80-5 1,2-Ethanediamine, N,N-di-
    methyl-N'-2-pyridinyl-N'-
    (2-thienylmethyl)-
    8270 10.
     
    Methoxychlor 72-43-5 Benzene, 1,1'-(2,2,2-tri-
    chloroethylidene)bis[4-
    methoxy-
    8080
    8270
    2.
    10.
     
    Methyl bromide; Bromo-
    methane
    74-83-9 Methane, bromo- 8010
    8240
    20.
    10.
     

     
    486
    Methyl chloride; Chloro-
    methane
    74-87-3 Methane, chloro- 8010
    8240
    1.
    10.
     
    3-Methylcholanthrene 56-49-5 Benz[j]aceanthrylene, 1,2-
    dihydro-3-methyl-
    8270 10.
     
    Methylene bromide; Di-
    bromomethane
    74-95-3 Methane, dibromo- 8010
    8240
    15.
    5.
     
    Methylene chloride; Di-
    chloromethane
    75-09-2 Methane, dichloro- 8010
    8240
    5.
    5.
     
    Methyl ethyl ketone; MEK 78-93-3
    2-Butanone 8015
    8240
    10.
    100.
     
    Methyl iodide; Iodomethane 74-88-4 Methane, iodo- 8010
    8240
    40.
    5.
     
    Methyl methacrylate 80-62-6
    2-Propenoic acid, 2-methyl-
    , methyl ester
    8015
    8240
    2.
    5.
     
    Methyl methanesulfonate 66-27-3 Methanesulfonic acid,
    methyl ester
    8270 10.
     
    2-Methylnaphthalene 91-57-6 Naphthylene, 2-methyl- 8270 10.
     
    Methyl parathion; Parathion
    methyl
    298-00-0 Phosphorothioic acid, O,O-
    dimethyl O-(4-nitrophenyl)
    ester
    8140
    8270
    0.5
    10.
     
    4-Methyl-2-pentanone;
    Methyl isobutyl ketone
    108-10-1
    2-Pentanone, 4-methyl- 8015
    8240
    5.
    50.
     
    Naphthalene 91-20-3 Naphthalene 8100
    8270
    200.
    10.
     
    1,4-Naphthoquinone 130-15-4 1,4-Naphthalenedione 8270 10.
     
    1-Naphthylamine 134-32-7
    1-Naphthalenamine 8270 10.
     
    2-Naphthylamine 91-59-8
    2-Naphthalenamine 8270 10.
     
    Nickel (Total) Nickel 6010
    7520
    50.
    400.
     

     
    487
    o-Nitroaniline 88-74-4 Benzenamine, 2-nitro- 8270 50.
     
    m-Nitroaniline 99-09-2 Benzenamine, 3-nitro- 8270 50.
     
    p-Nitroaniline 100-01-6 Benzenamine, 4-nitro- 8270 50.
     
    Nitrobenzene 98-95-3 Benzene, nitro- 8090
    8270
    40.
    10.
     
    o-Nitrophenol 88-75-5 Phenol, 2-nitro- 8040
    8270
    5.
    10.
     
    p-Nitrophenol 100-02-7 Phenol, 4-nitro- 8040
    8270
    10.
    50.
     
    4-Nitroquinoline 1-oxide 56-57-5 Quinoline, 4-nitro-, 1-oxide 8270 10.
     
    N-Nitrosodi-n-butylamine 924-16-3
    1-Butanamine, N-butyl-N-
    nitroso-
    8270 10.
     
    N-Nitrosodiethylamine 55-18-5 Ethanamine, N-ethyl-N-
    nitroso-
    8270 10.
     
    N-Nitrosodimethylamine 62-75-9 Methanamine, N-methyl-N-
    nitroso-
    8270 10.
     
    N-Nitrosodiphenylamine 86-30-6 Benzenamine, N-nitroso-N-
    phenyl-
    8270 10.
     
    N-Nitrosodipropylamine;
    Di-n-propylnitrosamine
    621-64-7
    1-Propanamine, N-nitroso-
    N-propyl-
    8270 10.
     
    N-Nitrosomethylethylamine 10595-95-6
    Ethanamine, N-methyl-N-
    nitroso-
    8270 10.
     
    N-Nitrosomorpholine 59-89-2 Morpholine, 4-nitroso- 8270 10.
     
    N-Nitrosopiperidene 100-75-4 Piperidene, 1-nitroso- 8270 10.
     
    N-Nitrosopyrrolidine 930-55-2 Pyrrolidine, 1-nitroso- 8270 10.
     
    5-Nitro-o-toluidine 99-55-8 Benzenamine, 2-methyl-5-
    nitro-
    8270 10.
     

     
    488
    Parathion 56-38-2 Phosphorothioic acid, O,O-
    diethyl-O-(4-nitrophenyl)
    ester
    8270 10.
     
    Polychlorinated biphenyls;
    PCBs
    See (g) 1,1'-Biphenyl, chloro
    derivatives
    8080
    8250
    50.
    100.
     
    Polychlorinated dibenzo-p-
    dioxins; PCDDs
    See (h) Dibenzo[b,e][1,4]dioxin,
    chloro derivatives
    8280 0.01
     
    Polychlorinated di-
    benzofurans; PCDFs
    See (i) Bibenzofuran, chloro
    derivatives
    8280 0.01
     
    Pentachlorobenzene 608-93-5 Benzene, pentachloro- 8270 10.
     
    Pentachloroethane 76-01-7 Ethane, pentachloro- 8240
    8270
    5.
    10.
     
    Pentachloronitrobenzene 82-68-8 Benzene, pentachloronitro- 8270 10.
     
    Pentachlorophenol 87-86-5 Phenol, pentachloro- 8040
    8270
    5.
    50.
     
    Phenacetin 62-44-2 Acetamide, N-(4-ethoxy-
    phenyl)
    8270 10.
     
    Phenanthrene 85-01-8 Phenanthrene 8100
    8270
    200.
    10.
     
    Phenol 108-95-2 Phenol 8040
    8270
    1.
    10.
     
    p-Phenylenediamine 106-50-3 1,4-Benzenediamine 8270 10.
     
    Phorate 298-02-2 Phosphorodithioic acid,
    O,O-diethyl S-[(ethylthio)-
    methyl] ester
    8140
    8270
    2.
    10.
     
    2-Picoline 109-06-8 Pyridine, 2-methyl- 8240
    8270
    5.
    10.
     
    Pronamide 23950-58-5
    Benzamide, 3,5-dichloro-N-
    (1,1-dimethyl-2-propenyl)-
    8270 10.
     

     
    489
    Propionitrile; Ethyl cyanide 107-12-0 Propanenitrile 8015
    8240
    60.
    5.
     
    Pyrene 129-00-0 Pyrene 8100
    8270
    200.
    10.
     
    Pyridine 110-86-1 Pyridine 8240
    8270
    5.
    10.
     
    Safrole 94-59-7 1,3-Benzodioxole, 5-(2-
    propenyl)-
    8270 10.
     
    Selenium (Total) Selenium 6010
    7740
    7741
    750.
    20.
    20.
     
    Silver (Total) Silver 6010
    7760
    70.
    100.
     
    Silvex; 2,4,5-TP 93-72-1 Propanoic acid, 2-(2,4,5-tri-
    chlorophenoxy)-
    8150 2.
     
    Styrene 100-42-5 Benzene, ethenyl- 8020
    8240
    1.
    5.
     
    Sulfide 18496-25-8
    Sulfide 9030 10000.
     
    2,4,5-T; 2,4,5-Trichloro-
    phenoxyacetic acid
    93-76-5 Acetic acid, (2,4,5-tri-
    chlorophenoxy)-
    8150 2.
     
    2,3,7,8-TCDD; 2,3,7,8-
    Tetrachlorodibenzo-p-
    dioxin
    1746-01-8 Dibenzo[b,e][1,4]dioxin,
    2,3,7,8-tetrachloro-
    8280 0.005
     
    1,2,4,5-Tetrachlorobenzene 95-94-3 Benzene, 1,2,4,5-tetra-
    chloro-
    8270 10.
     
    1,1,1,2-Tetrachloroethane 630-20-6 Ethane, 1,1,1,2-tetrachloro- 8010
    8240
    5.
    5.
     
    1,1,2,2,-Tetrachloroethane 79-34-5 Ethane, 1,1,2,2-tetrachloro- 8010
    8240
    0.5
    5.
     

     
    490
    Tetrachloroethylene;
    Perchloroethylene; Tetra-
    chloroethene
    127-18-4 Ethene, tetrachloro- 8010
    8240
    0.5
    5.
     
    2,3,4,6-Tetrachlorophenol 58-90-2 Phenol, 2,3,4,6-tetrachloro- 8270 10.
     
    Tetraethyl dithiopyro-
    phosphate; Sulfotepp
    3689-24-5 Thiodiphosphoric acid
    ([(HO)2P(S)]2O), tetraethyl
    ester
    8270 10.
     
    Thallium (Total) Thallium 6010
    7840
    7841
    400.
    1000.
    10.
     
    Tin (Total) Tin 7870 8000.
     
    Toluene 108-88-3 Benzene, methyl- 8020
    8240
    2.
    5.
     
    o-Toluidine 95-53-4 Benzenamine, 2-methyl- 8270 10.
     
    Toxaphene 8001-35-2 Toxaphene 8080
    8250
    2.
    10.
     
    1,2,4-Trichlorobenzene 120-82-1 Benzene, 1,2,4-trichloro- 8270 10.
     
    1,1,1-Trichloroethane;
    Methyl chloroform
    71-55-6 Ethane, 1,1,1-trichloro- 8240 5.
     
    1,1,2-Trichloroethane 79-00-5 Ethane, 1,1,2-trichloro- 8010
    8240
    0.2
    5.
     
    Trichloroethylene; Tri-
    chloroethene
    79-01-6 Ethene, trichloro- 8010
    8240
    1.
    5.
     
    Trichlorofluoromethane 75-69-4 Methane, trichlorofluoro- 8010
    8240
    10.
    5.
     
    2,4,5-Trichlorophenol 95-96-4 Phenol, 2,4,5-trichloro- 8270 10.
     
    2,4,6-Trichlorophenol 88-06-2 Phenol, 2,4,6-trichloro- 8040
    8270
    5.
    10.
     
    1,2,3-Trichloropropane 96-18-4 Propane, 1,2,3-trichloro- 8010
    8240
    10.
    5.
     

     
    491
    O,O,O-Triethyl
    phosphorothioate
    126-68-1 Phosphorothioic acid,
    O,O,O-triethyl ester
    8270 10.
     
    sym-Trinitrobenzene 99-35-4 Benzene, 1,3,5-trinitro- 8270 10.
     
    Vanadium (Total) Vanadium 6010
    7910
    7911
    80.
    2000.
    40.
     
    Vinyl acetate 108-05-4 Acetic acid, ethenyl ester 8240 5.
     
    Vinyl chloride 75-01-4 Ethene, chloro- 8010
    8240
    2.
    10.
     
    Xylene (total) 1330-20-7 Benzene, dimethyl- 8020
    8240
    5.
    5.
     
    Zinc (Total) Zinc 6010
    7950
    20.
    50.
     
    Common Name CAS RN Chemical Abstracts Service Index Name
    Acenaphthene 83-32-9 Acenaphthylene, 1,2-dihydro-
    Acenaphthylene 208-96-8 Acenaphthylene
    Acetone 67-64-1 2-Propanone
    Acetophenone 98-86-2 Ethanone, 1-phenyl-
    Acetonitrile; Methyl
    cyanide
    75-05-8 Acetonitrile
    2-Acetylaminofluorene; 2-
    AAF
    53-96-3 Acetamide, N-9H-fluoren-2-yl-
    Acrolein 107-02-8 2-Propenal
    Acrylonitrile 107-13-1 2-Propenenitrile
    Aldrin 309-00-2 1,4:5,8-Dimethanonaphthalene,
    1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-
    hexahydro- (1
    α
    ,4
    α
    ,4a
    β
    ,5
    α
    ,8
    α
    ,8a
    β
    )-
    Allyl chloride 107-05-1 1-Propene, 3-chloro-
    4-Aminobiphenyl 92-67-1 (1,1'-Biphenyl)-4-amine
    Aniline 62-53-3 Benzenamine
    Anthracene 120-12-7 Anthracene
    Antimony (Total) Antimony
    Aramite 140-57-8 Sulfurous acid, 2-chloroethyl 2-(4-(1,1-
    dimethylethyl)phenoxy)-1-methylethyl
    ester
    Arsenic (Total) Arsenic
    Barium (Total) Barium
    Benzene 71-43-2 Benzene

     
    492
    Benzo(a)anthracene; Benz-
    anthracene
    56-55-3 Benz(a)anthracene
    Benzo(b)fluoranthene 205-99-2 Benz(e)acephenanthrylene
    Benzo(k)fluoranthene 207-08-9 Benzo(k)fluoranthene
    Benzo(ghi)perylene 191-24-2 Benzo(ghi)perylene
    Benzo(a)pyrene 50-32-8 Benzo(a)pyrene
    Benzyl alcohol 100-51-6 Benzenemethanol
    Beryllium (Total) Beryllium
    α
    -BHC
    319-84-6 Cyclohexane, 1,2,3,4,5,6-hexachloro-,
    (1
    α
    ,2
    α
    ,3
    β
    ,4
    α
    ,5
    β
    ,6
    β
    )-
    β
    -BHC
    319-85-7 Cyclohexane, 1,2,3,4,5,6-hexachloro-,
    (1
    α
    ,2
    β
    ,3
    α
    ,4
    β
    ,5
    α
    ,6
    β
    )-
    δ
    -BHC
    319-86-8 Cyclohexane, 1,2,3,4,5,6-hexachloro-,
    (1
    α
    ,2
    α
    ,3
    α
    ,4
    β
    ,5
    α
    ,6
    β
    )-
    γ
    -BHC; Lindane
    58-89-9 Cyclohexane, 1,2,3,4,5,6-hexachloro-,
    (1
    α
    ,2
    α
    ,3
    β
    ,4
    α
    ,5
    α
    ,6
    β
    )-
    Bis(2-chloroethoxy)-
    methane
    111-91-1 Ethane, 1,1'-(methylenebis(oxy))bis(2-
    chloro-
    Bis(2-chloroethyl) ether 111-44-4 Ethane, 1,1'-oxybis(2-chloro-
    Bis(2-chloro-1-methylethyl)
    ether; 2,2'-Dichlorodiiso-
    propyl ether
    108-60-1 Propane, 2,2'-oxybis(1-chloro-
    Bis(2-ethylhexyl) phthalate 117-81-7 1,2-Benzenedicarboxylic acid, bis(2-ethyl-
    hexyl) ester
    Bromodichloromethane 75-27-4 Methane, bromodichloro-
    Bromoform; Tribromo-
    methane
    75-25-2 Methane, tribromo-
    4-Bromophenyl phenyl
    ether
    101-55-3 Benzene, 1-bromo-4-phenoxy-
    Butyl benzyl phthalate;
    Benzyl butyl phthalate
    85-68-7 1,2-Benzenedicarboxylic acid, butyl
    phenylmethyl ester
    Cadmium Total Cadmium
    Carbon disulfide 75-15-0 Carbon disulfide
    Carbon tetrachloride 56-23-5 Methane, tetrachloro-
    Chlordane 57-74-9 4,7-Methano-1H-indene,1,2,4,5,6,7,8,8-
    octachloro-2,3,3a,4,7,7a-hexahydro-
    p-Chloroaniline 106-47-8 Benzeneamine, 4-chloro-
    Chlorobenzene 108-90-7 Benzene, chloro-
    Chlorobenzilate 510-15-6
    Benzeneacetic acid, 4-chloro-
    α
    -(4-chloro-
    phenyl)-
    α
    -hydroxy-, ethylf ester
    p-Chloro-m-cresol 59-50-7 Phenol, 4-chloro-3-methyl-
    Chloroethane; Ethyl
    chloride
    75-00-3 Ethane, chloro-
    Chloroform 67-66-3 Methane, trichloro-
    2-Chloronapthalene 91-58-7 Naphthalene, 2-chloro-
    2-Chlorophenol 95-57-8 Phenol, 2-chloro-

     
    493
    4-Chlorophenyl phenyl
    ether
    7005-72-3 Benzene, 1-chloro-4-phenoxy-
    Chloroprene 126-99-8 1,3-Butadiene, 2-chloro-
    Chromium (Total) Chromium
    Chrysene 218-01-9 Chrysene
    Cobalt (Total) Cobalt
    Copper (Total) Copper
    m-Cresol 108-39-4 Phenol, 3-methyl-
    o-Cresol 95-48-7 Phenol, 2-methyl-
    p-Cresol 106-44-5 Phenol, 4-methyl-
    Cyanide 57-12-5 Cyanide
    2,4-D; 2,4-Dichloro-
    phenoxyacetic acid
    94-75-7 Acetic acid, (2,4-dichlorophenoxy)-
    4,4'-DDD 72-54-8 Benzene, 1,1'-(2,2-dichloroethylidene)bis-
    (4-chloro-
    4,4'-DDE 72-55-9 Benzene, 1,1'-(dichloroethylidene)bis(4-
    chloro-
    4,4'-DDT 50-29-3 Benzene, 1,1'-(2,2,2-trichloroethylidene)-
    bis(4-chloro-
    Diallate 2303-16-4 Carbamothioic acid, bis(1-methylethyl)-,
    S-(2,3-dichloro--2-propenyl) ester
    Dibenz(a,h)anthracene 53-70-3 Dibenz(a,h)anthracene
    Dibenzofuran 132-64-9 Dibenzofuran
    Dibromochloromethane;
    Chlorodibromomethane
    124-48-1 Methane, dibromochloro-
    1,2-Dibromo-3-chloro-
    propane; DBCP
    96-12-8 Propane, 1,2-dibromo-3-chloro-
    1,2-Dibromoethane;
    Ethylene dibromide
    106-93-4 Ethane, 1,2-dibromo-
    Di-n-butyl phthalate 84-74-2 1,2-Benzenedicarboxylic acid, dibutyl
    ester
    o-Dichlorobenzene 95-50-1 Benzene, 1,2-dichloro-
    m-Dichlorobenzene 541-73-1 Benzene, 1,3-dichloro-
    p-Dichlorobenzene 106-46-7 Benzene, 1,4-dichloro-
    3,3'-Dichlorobenzidine 91-94-1 (1,1'-Biphenyl)-4,4'-diamine, 3,3'-dichloro-
    trans-1,4-Dichloro-2-butene 110-57-6 2-Butene, 1,4-dichloro-, (E)-
    Dichlorodifluoromethane 75-71-8 Methane, dichlorodifluoro-
    1,1-Dichloroethane 75-34-3 Ethane, 1,1-dichloro-
    1,2-Dichloroethane;
    Ethylene dichloride
    107-06-2 Ethane, 1,2-dichloro-
    1,1-Dichloroethylene;
    Vinylidene chloride
    75-35-4 Ethene, 1,1-dichloro-
    trans-1,2-Dichloroethylene 156-60-5 Ethene, 1,2-dichloro-, (E)-
    2,4-Dichlorophenol 120-83-2 Phenol, 2,4-dichloro-
    2,6-Dichlorophenol 87-65-0 Phenol, 2,6-dichloro-
    1,2-Dichloropropane 78-87-5 Propane, 1,2-dichloro-

     
    494
    cis-1,3-Dichloropropene 10061-01-5 1-Propene, 1,3-dichloro-, (Z)-
    trans-1,3-Dichloropropene 10061-02-6 1-Propene, 1,3-dichloro-, (E)-
    Dieldrin 60-57-1 2,7:3,6-Dimethanonaphth(2,3-b)oxirene,
    3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-
    octahydro-
    ,(1a
    α
    ,2
    β
    ,2a
    α
    ,3
    β
    ,6
    β
    ,6a
    α
    ,7
    β
    ,7a
    α
    )-
    Diethyl phthalate 84-66-2 1,2-Benzenedicarboxylic acid, diethyl ester
    O,O-Diethyl O-2-pyrazinyl
    phosphorothioate;
    Thionazin
    297-97-2 Phosphorothioic acid, O,O-diethyl O-pyra-
    zinyl ester
    Dimethoate 60-51-5 Phosphorodithioic acid, O,O-dimethyl S-
    (2-(methylamino)-2-oxoethyl) ester
    p-(Dimethylamino)-
    azobenzene
    60-11-7 Benzenamine, N,N-dimethyl-4-(phenyl-
    azo)-
    7,12-Dimethylbenz(a)-
    anthracene
    57-97-6 Benz(a)anthracene,7,12-dimethyl-
    3,3'-Dimethylbenzidine 119-93-7 (1,1'-Biphenyl)-4,4'-diamine, 3,3'-
    dimethyl-
    α
    ,
    α
    -Dimethylphenethyl-
    amine
    122-09-8
    Benzeneethanamine,
    α
    ,
    α
    -dimethyl-
    2,4-Dimethylphenol 105-67-9 Phenol, 2,4-dimethyl-
    Dimethyl phthalate 131-11-3 1,2-Benzenedicarboxylic acid, dimethyl
    ester
    m-Dinitrobenzene 99-65-0 Benzene, 1,3-dinitro-
    4,6-Dinitro-o-cresol 534-52-1 Phenol, 2-methyl-4,6-dinitro-
    2,4-Dinitrophenol 51-28-5 Phenol, 2,4-dinitro-
    2,4-Dinitrotoluene 121-14-2 Benzene, 1-methyl-2,4-dinitro-
    2,6-Dinitrotoluene 606-20-2 Benzene, 2-methyl-1,3-dinitro-
    Dinoseb; DNBP; 2-sec-
    Butyl-4,6-dinitrophenol
    88-85-7 Phenol, 2-(1-methylpropyl)-4,6-dinitro-
    Di-n-octyl phthalate 117-84-0 1,2-Benzenedicarboxylic acid, dioctyl ester
    1,4-Dioxane 123-91-1 1,4-Dioxane
    Diphenylamine 122-39-4 Benzeneamine, N-phenyl-
    Disulfoton 298-04-4 Phosphorodithioic acid, O,O-diethyl S-(2-
    (ethylthio)ethyl) ester
    Endosulfan I 959-98-8 6,9-Methano-2,4,3-
    benzodioxathiepin,6,7,8,9,10,10-hexa-
    chloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide,
    (3
    α
    ,5a
    β
    ,6
    α
    ,9
    α
    ,9a
    β
    )-
    Endosulfan II 33213-65-9 6,9-Methano-2,4,3-
    benzodioxathiepin,6,7,8,9,10,10-hexa-
    chloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide,
    (3
    α
    ,5a
    α
    ,6
    β
    ,9
    β
    ,9a
    α
    )-

     
    495
    Endosulfan sulfate 1031-07-8 6,9-Methano-2,4,3-
    benzodioxathiepin,6,7,8,9,10,10-hexa-
    chloro-1,5,5a,6,9,9a-hexahydro-,3,3-
    dioxide
    Endrin 72-20-8 2,7:3,6-Dimethanonaphth(2,3-b)oxirene,
    3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-
    octahydro-,
    (1a
    α
    ,2
    β
    ,2a
    β
    ,3
    α
    ,6
    α
    ,6a
    β
    ,7
    β
    ,7a
    α
    )-
    Endrin aldehyde 7421-93-4 1,2,4-Methanocyclopenta(cd)pentalene-5-
    carboxaldehyde, 2,2a,3,3,4,7-hexachloro-
    decahydro-,
    (1
    α
    ,2
    β
    ,2a
    β
    ,4
    β
    ,4a
    β
    ,5
    β
    ,6a
    β
    ,6b
    β
    ,7R)-
    Ethylbenzene 100-41-4 Benzene, ethyl-
    Ethyl methacrylate 97-63-2 2-Propenoic acid, 2-methyl-, ethyl ester
    Ethyl methanesulfonate 62-50-0 Methanesulfonic acid, ethyl ester
    Famphur 52-85-7 Phosphorothioic acid, O-(4-((dimethyl-
    amino)sulfonyl)phenyl)-O,O-dimethyl
    ester
    Fluoranthene 206-44-0 Fluoranthene
    Fluorene 86-73-7 9H-Fluorene
    Heptachlor 76-44-8 4,7-Methano-1H-indene, 1,4,5,6,7,8,8-
    heptachloro-3a,4,7,7a-tetrahydro-
    Heptachlor epoxide 1024-57-3 2,5-Methano-2H-indeno(1,2-b)oxirene,
    2,3,4,5,6,7,7-heptachloro-1a,1b,5,5a,6,6a-
    hexahydro-, (1a
    α
    ,1b
    β
    ,2
    α
    ,5
    α
    ,5a
    β
    ,6
    β
    ,6a
    α
    )-
    Hexachlorobenzene 118-74-1 Benzene, hexachloro-
    Hexachlorobutadiene 87-68-3 1,3-Butadiene, 1,1,2,3,4,4-hexachloro-
    Hexachlorocyclopentadiene 77-47-4 1,3-Cyclopentadiene, 1,2,3,4,5,5-hexa-
    chloro-
    Hexachloroethane 67-72-1 Ethane, hexachloro-
    Hexachlorophene 70-30-4 Phenol, 2,2'-methylenebis(3,4,6-trichloro-
    Hexachloropropene 1888-71-7 1-Propene, 1,1,2,3,3,3-hexachloro-
    2-Hexanone 591-78-6 2-Hexanone
    Indeno(1,2,3-cd)pyrene 193-39-5 Indeno(1,2,3-cd)pyrene
    Isobutyl alcohol 78-83-1 1-Propanol, 2-methyl-
    Isodrin 465-73-6 1,4,5,8-Dimethanonaphthalene,
    1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-
    hexahydro-(1
    α
    ,4
    α
    ,4a
    β
    ,5
    β
    ,8
    β
    ,8a
    β
    )-
    Isophorone 78-59-1 2-Cyclohexen-1-one, 3,5,5-trimethyl-
    Isosafrole 120-58-1 1,3-Benzodioxole, 5-(1-propenyl)-
    Kepone 143-50-0 1,3,4-Metheno-2H-cyclobuta-(c,d)penta-
    len-2-one, 1,1a,3,3a,4,5,5,5a,5b,6-deca-
    chlorooctahydro-
    Lead (Total) Lead
    Mercury (Total) Mercury
    Methacrylonitrile 126-96-7 2-Propenenitrile, 2-methyl-

     
    496
    Methapyrilene 91-80-5 1,2-Ethanediamine, N,N-dimethyl-N'-2-
    pyridinyl-N'-(2-thienylmethyl)-
    Methoxychlor 72-43-5 Benzene, 1,1'-(2,2,2-trichloroethylidene)-
    bis(4-methoxy-
    Methyl bromide; Bromo-
    methane
    74-83-9 Methane, bromo-
    Methyl chloride; Chloro-
    methane
    74-87-3 Methane, chloro-
    3-Methylcholanthrene 56-49-5 Benz(j)aceanthrylene, 1,2-dihydro-3-
    methyl-
    Methylene bromide;
    Dibromomethane
    74-95-3 Methane, dibromo-
    Methylene chloride;
    Dichloromethane
    75-09-2 Methane, dichloro-
    Methyl ethyl ketone; MEK 78-93-3 2-Butanone
    Methyl iodide; Iodomethane 74-88-4 Methane, iodo-
    Methyl methacrylate 80-62-6 2-Propenoic acid, 2-methyl-, methyl ester
    Methyl methanesulfonate 66-27-3 Methanesulfonic acid, methyl ester
    2-Methylnaphthalene 91-57-6 Naphthylene, 2-methyl-
    Methyl parathion; Parathion
    methyl
    298-00-0 Phosphorothioic acid, O,O-dimethyl O-(4-
    nitrophenyl) ester
    4-Methyl-2-pentanone;
    Methyl isobutyl ketone
    108-10-1 2-Pentanone, 4-methyl-
    Naphthalene 91-20-3 Naphthalene
    1,4-Naphthoquinone 130-15-4 1,4-Naphthalenedione
    1-Naphthylamine 134-32-7 1-Naphthalenamine
    2-Naphthylamine 91-59-8 2-Naphthalenamine
    Nickel (Total) Nickel
    o-Nitroaniline 88-74-4 Benzenamine, 2-nitro-
    m-Nitroaniline 99-09-2 Benzenamine, 3-nitro-
    p-Nitroaniline 100-01-6 Benzenamine, 4-nitro-
    Nitrobenzene 98-95-3 Benzene, nitro-
    o-Nitrophenol 88-75-5 Phenol, 2-nitro-
    p-Nitrophenol 100-02-7 Phenol, 4-nitro-
    4-Nitroquinoline 1-oxide 56-57-5 Quinoline, 4-nitro-, 1-oxide
    N-Nitrosodi-n-butylamine 924-16-3 1-Butanamine, N-butyl-N-nitroso-
    N-Nitrosodiethylamine 55-18-5 Ethanamine, N-ethyl-N-nitroso-
    N-Nitrosodimethylamine 62-75-9 Methanamine, N-methyl-N-nitroso-
    N-Nitrosodiphenylamine 86-30-6 Benzenamine, N-nitroso-N-phenyl-
    N-Nitrosodipropylamine;
    Di-n-propylnitrosamine
    621-64-7 1-Propanamine, N-nitroso-N-propyl-
    N-Nitrosomethylethylamine 10595-95-6 Ethanamine, N-methyl-N-nitroso-
    N-Nitrosomorpholine 59-89-2 Morpholine, 4-nitroso-
    N-Nitrosopiperidene 100-75-4 Piperidene, 1-nitroso-
    N-Nitrosopyrrolidine 930-55-2 Pyrrolidine, 1-nitroso-
    5-Nitro-o-toluidine 99-55-8 Benzenamine, 2-methyl-5-nitro-

     
    497
    Parathion 56-38-2 Phosphorothioic acid, O,O-diethyl-O-(4-
    nitrophenyl) ester
    Polychlorinated biphenyls;
    PCBs
    See (g) 1,1'-Biphenyl, chloro derivatives
    Polychlorinated dibenzo-p-
    dioxins; PCDDs
    See (h) Dibenzo(b,e)(1,4)dioxin, chloro
    derivatives
    Polychlorinated
    dibenzofurans; PCDFs
    See (i) Bibenzofuran, chloro derivatives
    Pentachlorobenzene 608-93-5 Benzene, pentachloro-
    Pentachloroethane 76-01-7 Ethane, pentachloro-
    Pentachloronitrobenzene 82-68-8 Benzene, pentachloronitro-
    Pentachlorophenol 87-86-5 Phenol, pentachloro-
    Phenacetin 62-44-2 Acetamide, N-(4-ethoxyphenyl)
    Phenanthrene 85-01-8 Phenanthrene
    Phenol 108-95-2 Phenol
    p-Phenylenediamine 106-50-3 1,4-Benzenediamine
    Phorate 298-02-2 Phosphorodithioic acid, O,O-diethyl S-
    ((ethylthio)methyl) ester
    2-Picoline 109-06-8 Pyridine, 2-methyl-
    Pronamide 23950-58-5 Benzamide, 3,5-dichloro-N-(1,1-dimethyl-
    2-propenyl)-
    Propionitrile; Ethyl cyanide 107-12-0 Propanenitrile
    Pyrene 129-00-0 Pyrene
    Pyridine 110-86-1 Pyridine
    Safrole 94-59-7 1,3-Benzodioxole, 5-(2-propenyl)-
    Selenium (Total) Selenium
    Silver (Total) Silver
    Silvex; 2,4,5-TP 93-72-1 Propanoic acid, 2-(2,4,5-trichloro-
    phenoxy)-
    Styrene 100-42-5 Benzene, ethenyl-
    Sulfide 18496-25-8 Sulfide
    2,4,5-T; 2,4,5-Trichloro-
    phenoxyacetic acid
    93-76-5 Acetic acid, (2,4,5-trichlorophenoxy)-
    2,3,7,8-TCDD; 2,3,7,8-
    Tetrachlorodibenzo-p-
    dioxin
    1746-01-8 Dibenzo(b,e)(1,4)dioxin, 2,3,7,8-tetra-
    chloro-
    1,2,4,5-Tetrachlorobenzene 95-94-3 Benzene, 1,2,4,5-tetrachloro-
    1,1,1,2-Tetrachloroethane 630-20-6 Ethane, 1,1,1,2-tetrachloro-
    1,1,2,2,-Tetrachloroethane 79-34-5 Ethane, 1,1,2,2-tetrachloro-
    Tetrachloroethylene;
    Perchloroethylene; Tetra-
    chloroethene
    127-18-4 Ethene, tetrachloro-
    2,3,4,6-Tetrachlorophenol 58-90-2 Phenol, 2,3,4,6-tetrachloro-
    Tetraethyl dithiopyro-
    phosphate; Sulfotepp
    3689-24-5 Thiodiphosphoric acid (((HO)2P(S))2O),
    tetraethyl ester
    Thallium (Total) Thallium

     
    498
    Tin (Total) Tin
    Toluene 108-88-3 Benzene, methyl-
    o-Toluidine 95-53-4 Benzenamine, 2-methyl-
    Toxaphene 8001-35-2 Toxaphene
    1,2,4-Trichlorobenzene 120-82-1 Benzene, 1,2,4-trichloro-
    1,1,1-Trichloroethane;
    Methyl chloroform
    71-55-6 Ethane, 1,1,1-trichloro-
    1,1,2-Trichloroethane 79-00-5 Ethane, 1,1,2-trichloro-
    Trichloroethylene; Tri-
    chloroethene
    79-01-6 Ethene, trichloro-
    Trichlorofluoromethane 75-69-4 Methane, trichlorofluoro-
    2,4,5-Trichlorophenol 95-96-4 Phenol, 2,4,5-trichloro-
    2,4,6-Trichlorophenol 88-06-2 Phenol, 2,4,6-trichloro-
    1,2,3-Trichloropropane 96-18-4 Propane, 1,2,3-trichloro-
    O,O,O-Triethyl phosphoro-
    thioate
    126-68-1 Phosphorothioic acid, O,O,O-triethyl ester
    sym-Trinitrobenzene 99-35-4 Benzene, 1,3,5-trinitro-
    Vanadium (Total) Vanadium
    Vinyl acetate 108-05-4 Acetic acid, ethenyl ester
    Vinyl chloride 75-01-4 Ethene, chloro-
    Xylene (total) 1330-20-7 Benzene, dimethyl-
    Zinc (Total) Zinc
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
     
    PART 725
    INTERIM STATUS STANDARDS FOR OWNERS AND OPERATORS OF
    HAZARDOUS WASTE TREATMENT, STORAGE, AND DISPOSAL
    FACILITIES
     
    SUBPART A: GENERAL PROVISIONS
    Section
    725.101 Purpose, Scope, and Applicability
    725.104 Imminent Hazard Action
     
    SUBPART B: GENERAL FACILITY STANDARDS
    Section
    725.110 Applicability
    725.111 USEPA Identification Number
    725.112 Required Notices
    725.113 General Waste Analysis

     
    499
    725.114 Security
    725.115 General Inspection Requirements
    725.116 Personnel Training
    725.117 General Requirements for Ignitable, Reactive, or Incompatible Wastes
    725.118 Location Standards
    725.119 Construction Quality Assurance Program
     
    SUBPART C: PREPAREDNESS AND PREVENTION
    Section
    725.130 Applicability
    725.131 Maintenance and Operation of Facility
    725.132 Required Equipment
    725.133 Testing and Maintenance of Equipment
    725.134 Access to Communications or Alarm System
    725.135 Required Aisle Space
    725.137 Arrangements with Local Authorities
     
    SUBPART D: CONTINGENCY PLAN AND EMERGENCY PROCEDURES
    Section
    725.150 Applicability
    725.151 Purpose and Implementation of Contingency Plan
    725.152 Content of Contingency Plan
    725.153 Copies of Contingency Plan
    725.154 Amendment of Contingency Plan
    725.155 Emergency Coordinator
    725.156 Emergency Procedures
     
    SUBPART E: MANIFEST SYSTEM, RECORDKEEPING, AND REPORTING
    Section
    725.170 Applicability
    725.171 Use of Manifest System
    725.172 Manifest Discrepancies
    725.173 Operating Record
    725.174 Availability, Retention, and Disposition of Records
    725.175 Annual Report
    725.176 Unmanifested Waste Report
    725.177 Additional Reports
     
    SUBPART F: GROUNDWATER MONITORING
    Section
    725.190 Applicability
    725.191 Groundwater Monitoring System
    725.192 Sampling and Analysis
    725.193 Preparation, Evaluation, and Response
    725.194 Recordkeeping and Reporting
     

     
    500
    SUBPART G: CLOSURE AND POST-CLOSURE CARE
    Section
    725.210 Applicability
    725.211 Closure Performance Standard
    725.212 Closure Plan; Amendment of Plan
    725.213 Closure; Time Allowed for Closure
    725.214 Disposal or Decontamination of Equipment, Structures, and Soils
    725.215 Certification of Closure
    725.216 Survey Plat
    725.217 Post-Closure Care and Use of Property
    725.218 Post-Closure Care Plan; Amendment of Plan
    725.219 Post-Closure Notices
    725.220 Certification of Completion of Post-Closure Care
    725.221 Alternative Post-Closure Care Requirements
     
    SUBPART H: FINANCIAL REQUIREMENTS
    Section
    725.240 Applicability
    725.241 Definitions of Terms as Used in this Subpart H
    725.242 Cost Estimate for Closure
    725.243 Financial Assurance for Closure
    725.244 Cost Estimate for Post-Closure Care
    725.245 Financial Assurance for Post-Closure Monitoring and Maintenance
    725.246 Use of a Mechanism for Financial Assurance of Both Closure and Post-Closure
    Care
    725.247 Liability Requirements
    725.248 Incapacity of Owners or Operators, Guarantors, or Financial Institutions
    725.251 Promulgation of Forms (Repealed)
     
    SUBPART I: USE AND MANAGEMENT OF CONTAINERS
    Section
    725.270 Applicability
    725.271 Condition of Containers
    725.272 Compatibility of Waste with Containers
    725.273 Management of Containers
    725.274 Inspections
    725.276 Special Requirements for Ignitable or Reactive Wastes
    725.277 Special Requirements for Incompatible Wastes
    725.278 Air Emission Standards
     
    SUBPART J: TANK SYSTEMS
    Section
    725.290 Applicability
    725.291 Assessment of Existing Tank System Integrity
    725.292 Design and Installation of New Tank Systems or Components
    725.293 Containment and Detection of Releases

     
    501
    725.294 General Operating Requirements
    725.295 Inspections
    725.296 Response to Leaks or Spills and Disposition of Tank Systems
    725.297 Closure and Post-Closure Care
    725.298 Special Requirements for Ignitable or Reactive Wastes
    725.299 Special Requirements for Incompatible Wastes
    725.300 Waste Analysis and Trial Tests
    725.301 Generators of 100 to 1,000 Kilograms of Hazardous Waste Per Month
    725.302 Air Emission Standards
     
    SUBPART K: SURFACE IMPOUNDMENTS
    Section
    725.320 Applicability
    725.321 Design and Operating Requirements
    725.322 Action Leakage Rate
    725.323 Response Actions
    725.324 Containment System
    725.325 Waste Analysis and Trial Tests
    725.326 Monitoring and Inspections
    725.328 Closure and Post-Closure Care
    725.329 Special Requirements for Ignitable or Reactive Wastes
    725.330 Special Requirements for Incompatible Wastes
    725.331 Air Emission Standards
     
    SUBPART L: WASTE PILES
    Section
    725.350 Applicability
    725.351 Protection from Wind
    725.352 Waste Analysis
    725.353 Containment
    725.354 Design and Operating Requirements
    725.355 Action Leakage Rates
    725.356 Special Requirements for Ignitable or Reactive Wastes
    725.357 Special Requirements for Incompatible Wastes
    725.358 Closure and Post-Closure Care
    725.359 Response Actions
    725.360 Monitoring and Inspections
     
    SUBPART M: LAND TREATMENT
    Section
    725.370 Applicability
    725.372 General Operating Requirements
    725.373 Waste Analysis
    725.376 Food Chain Crops
    725.378 Unsaturated Zone (Zone of Aeration) Monitoring
    725.379 Recordkeeping

     
    502
    725.380 Closure and Post-Closure Care
    725.381 Special Requirements for Ignitable or Reactive Wastes
    725.382 Special Requirements for Incompatible Wastes
     
    SUBPART N: LANDFILLS
    Section
    725.400 Applicability
    725.401 Design Requirements
    725.402 Action Leakage Rate
    725.403 Response Actions
    725.404 Monitoring and Inspections
    725.409 Surveying and Recordkeeping
    725.410 Closure and Post-Closure Care
    725.412 Special Requirements for Ignitable or Reactive Wastes
    725.413 Special Requirements for Incompatible Wastes
    725.414 Special Requirements for Liquid Wastes
    725.415 Special Requirements for Containers
    725.416 Disposal of Small Containers of Hazardous Waste in Overpacked Drums (Lab
    Packs)
     
    SUBPART O: INCINERATORS
    Section
    725.440 Applicability
    725.441 Waste Analysis
    725.445 General Operating Requirements
    725.447 Monitoring and Inspections
    725.451 Closure
    725.452 Interim Status Incinerators Burning Particular Hazardous Wastes
     
    SUBPART P: THERMAL TREATMENT
    Section
    725.470 Other Thermal Treatment
    725.473 General Operating Requirements
    725.475 Waste Analysis
    725.477 Monitoring and Inspections
    725.481 Closure
    725.482 Open Burning; Waste Explosives
    725.483 Interim Status Thermal Treatment Devices Burning Particular Hazardous Wastes
     
    SUBPART Q: CHEMICAL, PHYSICAL, AND BIOLOGICAL TREATMENT
    Section
    725.500 Applicability
    725.501 General Operating Requirements
    725.502 Waste Analysis and Trial Tests
    725.503 Inspections
    725.504 Closure

     
    503
    725.505 Special Requirements for Ignitable or Reactive Wastes
    725.506 Special Requirements for Incompatible Wastes
     
    SUBPART R: UNDERGROUND INJECTION
    Section
    725.530 Applicability
     
    SUBPART W: DRIP PADS
    Section
    725.540 Applicability
    725.541 Assessment of Existing Drip Pad Integrity
    725.542 Design and Installation of New Drip Pads
    725.543 Design and Operating Requirements
    725.544 Inspections
    725.545 Closure
     
    SUBPART AA: AIR EMISSION STANDARDS FOR PROCESS VENTS
    Section
    725.930 Applicability
    725.931 Definitions
    725.932 Standards: Process Vents
    725.933 Standards: Closed-Vent Systems and Control Devices
    725.934 Test Methods and Procedures
    725.935 Recordkeeping Requirements
     
    SUBPART BB: AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS
    Section
    725.950 Applicability
    725.951 Definitions
    725.952 Standards: Pumps in Light Liquid Service
    725.953 Standards: Compressors
    725.954 Standards: Pressure Relief Devices in Gas/Vapor Service
    725.955 Standards: Sampling Connecting Systems
    725.956 Standards: Open-Ended Valves or Lines
    725.957 Standards: Valves in Gas/Vapor or Light Liquid Service
    725.958 Standards: Pumps, Valves, Pressure Relief Devices, Flanges, and Other
    Connectors
    725.959 Standards: Delay of Repair
    725.960 Standards: Closed-Vent Systems and Control Devices
    725.961 Percent Leakage Alternative for Valves
    725.962 Skip Period Alternative for Valves
    725.963 Test Methods and Procedures
    725.964 Recordkeeping Requirements
     

     
    504
    SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE
    IMPOUNDMENTS, AND CONTAINERS
    Section
    725.980 Applicability
    725.981 Definitions
    725.982 Schedule for Implementation of Air Emission Standards
    725.983 Standards: General
    725.984 Waste Determination Procedures
    725.985 Standards: Tanks
    725.986 Standards: Surface Impoundments
    725.987 Standards: Containers
    725.988 Standards: Closed-Vent Systems and Control Devices
    725.989 Inspection and Monitoring Requirements
    725.990 Recordkeeping Requirements
    725.991 Alternative Tank Emission Control Requirements (Repealed)
     
    SUBPART DD: CONTAINMENT BUILDINGS
    Section
    725.1100 Applicability
    725.1101 Design and Operating Standards
    725.1102 Closure and Post-Closure Care
     
    SUBPART EE: HAZARDOUS WASTE MUNITIONS AND EXPLOSIVES
    STORAGE
    Section
    725.1200 Applicability
    725.1201 Design and Operating Standards
    725.1202 Closure and Post-Closure Care
     
    725.Appendix A Recordkeeping Instructions
    725.Appendix B EPA Report Form and Instructions (Repealed)
    725.Appendix C USEPA Interim Primary Drinking Water Standards
    725.Appendix D Tests for Significance
    725.Appendix E Examples of Potentially Incompatible Wastes
    725.Appendix F Compounds with Henry’s Law Constant Less Than 0.1 Y/X (at 25°C)
     
    AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the
    Environmental Protection Act [415 ILCS 5/7.2, 22.4, and 27].
     
    SOURCE: Adopted in R81-22 at 5 Ill. Reg. 9781, effective May 17, 1982; amended and
    codified in R81-22 at 6 Ill. Reg. 4828, effective May 17, 1982; amended in R82-18 at 7 Ill. Reg.
    2518, effective February 22, 1983; amended in R82-19 at 7 Ill. Reg. 14034, effective October 12,
    1983; amended in R84-9 at 9 Ill. Reg. 11869, effective July 24, 1985; amended in R85-22 at 10
    Ill. Reg. 1085, effective January 2, 1986; amended in R86-1 at 10 Ill. Reg. 14069, effective
    August 12, 1986; amended in R86-28 at 11 Ill. Reg. 6044, effective March 24, 1987; amended in
    R86-46 at 11 Ill. Reg. 13489, effective August 4, 1987; amended in R87-5 at 11 Ill. Reg. 19338,

     
    505
    effective November 10, 1987; amended in R87-26 at 12 Ill. Reg. 2485, effective January 15,
    1988; amended in R87-39 at 12 Ill. Reg. 13027, effective July 29, 1988; amended in R88-16 at
    13 Ill. Reg. 437, effective December 28, 1988; amended in R89-1 at 13 Ill. Reg. 18354, effective
    November 13, 1989; amended in R90-2 at 14 Ill. Reg. 14447, effective August 22, 1990;
    amended in R90-10 at 14 Ill. Reg. 16498, effective September 25, 1990; amended in R90-11 at
    15 Ill. Reg. 9398, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14534, effective
    October 1, 1991; amended in R91-13 at 16 Ill. Reg. 9578, effective June 9, 1992; amended in
    R92-1 at 16 Ill. Reg. 17672, effective November 6, 1992; amended in R92-10 at 17 Ill. Reg.
    5681, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20620, effective November 22,
    1993; amended in R93-16 at 18 Ill. Reg. 6771, effective April 26, 1994; amended in R94-7 at 18
    Ill. Reg. 12190, effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17548, effective
    November 23, 1994; amended in R95-6 at 19 Ill. Reg. 9566, effective June 27, 1995; amended in
    R95-20 at 20 Ill. Reg. 11078, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22
    Ill. Reg. 369, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7620, effective
    April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17620, effective September 28,
    1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1850, effective January 19, 1999;
    amended in R99-15 at 23 Ill. Reg. 9168, effective July 26, 1999; amended in R00-5 at 24 Ill.
    Reg. 1076, effective January 6, 2000; amended in R00-13 at 24 Ill. Reg. 9575, effective June 20,
    2000; amended in R03-7 at 27 Ill. Reg. 4187, effective February 14, 2003; amended in R05-2 at
    29 Ill. Reg. 6389, effective April 22, 2005; amended in R06-5/R06-6/R06-7 at 30 Ill. Reg.
    ________, effective ______________________.
     
    SUBPART A: GENERAL PROVISIONS
     
    Section 725.101 Purpose, Scope, and Applicability
     
    a) The purpose of this Part is to establish minimum standards that define the
    acceptable management of hazardous waste during the period of interim status and
    until certification of final closure or, if the facility is subject to post-closure care
    requirements, until post-closure care responsibilities are fulfilled.
     
    b) Except as provided in Section 725.980(b), the standards in this Part and 35 Ill. Adm.
    Code 724.652 through 724.654 apply to owners and operators of facilities that
    treat, store, or dispose of hazardous waste and which have fully complied with the
    requirements for interim status under Section 3005(e) of the Resource Conservation
    and Recovery Act (RCRA) (42 USC 6925(e)) and 35 Ill. Adm. Code 703, until
    either a permit is issued under Section 3005 of the Resource Conservation and
    Recovery Act (42 USC 6905) or Section 21(f) of the Environmental Protection Act
    [415 ILCS 5/21(f)], or until applicable closure and post-closure care responsibilities
    under this Part are fulfilled, and to those owners and operators of facilities in
    existence on November 19, 1980, that have failed to provide timely notification as
    required by Section 3010(a) of RCRA (42 USC 6910(a)) or that have failed to file
    Part A of the Permit Application, as required by federal 40 CFR 270.10(e) and (g)
    or 35 Ill. Adm. Code 703.150 and 703.152. These standards apply to all treatment,
    storage, or disposal of hazardous waste at these facilities after November 19, 1980,
    except as specifically provided otherwise in this Part or in 35 Ill. Adm. Code 721.

     
    506
     
    BOARD NOTE: As stated in Section 3005(a) of RCRA (42 USC 6905(a)), after
    the effective date of regulations under that Section (i.e., 40 CFR 270 and 124) the
    treatment, storage, or disposal of hazardous waste is prohibited except in
    accordance with a permit. Section 3005(e) of RCRA (42 USC 6905(e)) provides
    for the continued operation of an existing facility that meets certain conditions until
    final administrative disposition of the owner’s and operator’s permit application is
    made.
     
    c) The requirements of this Part do not apply to any of the following:
     
    1) A person disposing of hazardous waste by means of ocean disposal subject
    to a permit issued under the federal Marine Protection, Research and
    Sanctuaries Act (33 USC 1401 et seq.);
     
    BOARD NOTE: This Part applies to the treatment or storage of hazardous
    waste before it is loaded into an ocean vessel for incineration or disposal at
    sea, as provided in subsection (b) of this Section.
     
    2) This subsection (c)(2) corresponds with 40 CFR 265.1(c)(2), marked
    “reserved” by USEPA. This statement maintains structural consistency
    with USEPA rules;
     
    3) The owner or operator of a POTW (publicly owned treatment works) that
    treats, stores, or disposes of hazardous waste;
     
    BOARD NOTE: The owner or operator of a facility under subsections
    (c)(1) and (c)(3) is subject to the requirements of 35 Ill. Adm. Code 724 to
    the extent they are included in a permit by rule granted to such a person
    under 35 Ill. Adm. Code 702 and 703 or are required by Subpart F of 35 Ill.
    Adm. Code 704.
     
    4) This subsection (c)(4) corresponds with 40 CFR 265.1(c)(4), which
    pertains exclusively to the applicability of the federal regulations in
    authorized states. There is no need for a parallel provision in the Illinois
    regulations. This statement maintains structural consistency with USEPA
    rules;
     
    5) The owner or operator of a facility permitted, licensed, or registered by
    Illinois to manage municipal or industrial solid waste, if the only hazardous
    waste the facility treats, stores, or disposes of is excluded from regulation
    under this Part by 35 Ill. Adm. Code 721.105;
     
    6) The owner or operator of a facility managing recyclable materials described
    in 35 Ill. Adm. Code 721.106(a)(2) through (a)(4), except to the extent that
    requirements of this Part are referred to in Subpart C, F, G, or H of 35 Ill.

     
    507
    Adm. Code 726 or 35 Ill. Adm. Code 739;
     
    7) A generator accumulating waste on-site in compliance with 35 Ill. Adm.
    Code 722.134, except to the extent the requirements are included in 35 Ill.
    Adm. Code 722.134;
     
    8) A farmer disposing of waste pesticides from the farmer’s own use in
    compliance with 35 Ill. Adm. Code 722.170;
     
    9) The owner or operator of a totally enclosed treatment facility, as defined in
    35 Ill. Adm. Code 720.110;
     
    10) The owner or operator of an elementary neutralization unit or a wastewater
    treatment unit, as defined in 35 Ill. Adm. Code 720.110, provided that if the
    owner or operator is diluting hazardous ignitable (D001) wastes (other than
    the D001 High TOC Subcategory defined in Table T of 35 Ill. Adm. Code
    728) or reactive (D003) waste in order to remove the characteristic before
    land disposal, the owner or operator must comply with the requirements set
    forth in Section 725.117(b);
     
    11) Immediate response.
     
    A) Except as provided in subsection (c)(11)(B) of this Section, a person
    engaged in treatment or containment activities during immediate
    response to any of the following situations:
     
    i) A discharge of a hazardous waste;
     
    ii) An imminent and substantial threat of a discharge of a
    hazardous waste;
     
    iii) A discharge of a material that becomes a hazardous waste
    when discharged; or
     
    iv) An immediate threat to human health, public safety,
    property, or the environment from the known or suspected
    presence of military munitions, other explosive material, or
    an explosive device, as determined by an explosives or
    munitions emergency response specialist as defined in 35
    Ill. Adm. Code 720.110.
     
    B) An owner or operator of a facility otherwise regulated by this Part
    must comply with all applicable requirements of Subparts C and D
    of this Part.
     
    C) Any person that is covered by subsection (c)(11)(A) of this Section

     
    508
    that continues or initiates hazardous waste treatment or containment
    activities after the immediate response is over is subject to all
    applicable requirements of this Part and 35 Ill. Adm. Code 702, 703,
    and 705 for those activities;
     
    D) In the case of an explosives or munitions emergency response, if a
    federal, state, or local official acting within the scope of his or her
    official responsibilities or an explosives or munitions emergency
    response specialist determines that immediate removal of the
    material or waste is necessary to protect human health or the
    environment, that official or specialist may authorize the removal
    of the material or waste by transporters that do not have USEPA
    identification numbers and without the preparation of a manifest.
    In the case of emergencies involving military munitions, the
    responding military emergency response specialist’s organizational
    unit must retain records for three years identifying the dates of the
    response, the responsible persons responding, the type and
    description of material addressed, and its disposition;
     
    12) A transporter storing manifested shipments of hazardous waste in containers
    meeting the requirements of 35 Ill. Adm. Code 722.130 at a transfer facility
    for a period of ten days or less;
     
    13) The addition of absorbent material to waste in a container (as defined in 35
    Ill. Adm. Code 720.110) or the addition of waste to the absorbent material in
    a container, provided that these actions occur at the time that the waste is
    first placed in the containers and Sections 725.117(b), 725.271, and 725.272
    are complied with;
     
    14) A universal waste handler or universal waste transporter (as defined in 35
    Ill. Adm. Code 720.110) that handles any of the wastes listed below is
    subject to regulation under 35 Ill. Adm. Code 733 when handling the
    following universal wastes:
     
    A) Batteries, as described in 35 Ill. Adm. Code 733.102;
     
    B) Pesticides, as described in 35 Ill. Adm. Code 733.103;
     
    C) Thermostats, as described in 35 Ill. Adm. Code 733.104;
     
    D) Lamps, as described in 35 Ill. Adm. Code 733.105; and
     
    E) Mercury-containing equipment as described in 35 Ill. Adm. Code
    733.106.
    BOARD NOTE: Subsection (c)(14)(E) of this Section was added
    pursuant to Sections 3.283, 3.284, and 22.23b of the Act [415

     
    509
    ILCS 5/3.283, 3.284, and 22.23b] (See P.A. 93-964, effective
    August 20, 2004).
     
    d) The following hazardous wastes must not be managed at facilities subject to
    regulation under this Part: hazardous waste numbers F020, F021, F022, F023,
    F026, or F027, unless the following conditions are fulfilled:
     
    1) The wastewater treatment sludge is generated in a surface impoundment as
    part of the plant’s wastewater treatment system;
     
    2) The waste is stored in tanks or containers;
     
    3) The waste is stored or treated in waste piles that meet the requirements of 35
    Ill. Adm. Code 724.350(c) and all other applicable requirements of Subpart
    L of this Part;
     
    4) The waste is burned in incinerators that are certified pursuant to the
    standards and procedures in Section 725.452; or
     
    5) The waste is burned in facilities that thermally treat the waste in a device
    other than an incinerator and that are certified pursuant to the standards and
    procedures in Section 725.483.
     
    e) This Part applies to owners and operators of facilities that treat, store, or dispose of
    hazardous wastes referred to in 35 Ill. Adm. Code 728, and the 35 Ill. Adm. Code
    728 standards are considered material conditions or requirements of the interim
    status standards of this Part.
     
    f) 35 Ill. Adm. Code 726.505 identifies when the requirements of this Part apply to
    the storage of military munitions classified as solid waste under 35 Ill. Adm. Code
    726.302. The treatment and disposal of hazardous waste military munitions are
    subject to the applicable permitting, procedural, and technical standards in 35 Ill.
    Adm. Code 702, 703, 705, 720 through 726, and 728.
     
    g) Other bodies of regulations may apply to a person, facility, or activity, such as 35
    Ill. Adm. Code 809 (special waste hauling), 35 Ill. Adm. Code 807 or 810 through
    817 (solid waste landfills), 35 Ill. Adm. Code 848 or 849 (used and scrap tires), or
    35 Ill. Adm. Code 1420 through 1422 (potentially infectious medical waste),
    depending on the provisions of those other regulations.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    510
    SUBPART D: CONTINGENCY PLAN AND EMERGENCY PROCEDURES
     
    Section 725.156 Emergency Procedures
     
    a) Whenever there is an imminent or actual emergency situation, the emergency
    coordinator (or his designee when the emergency coordinator is on call) must
    immediately do the following:
     
    1) Activate
    He or she must activate internal facility alarms or communication
    systems, where applicable, to notify all facility personnel; and
     
    2) Notify
    He or she must notify appropriate State or local agencies with
    designated response roles if their help is needed.
     
    b) Whenever there is a release, fire, or explosion, the emergency coordinator must
    immediately identify the character, exact source, amount, and a real extent of any
    released materials. He or she may do this by observation or review of facility
    records or manifests and, if necessary, by chemical analysis.
     
    c) Concurrently, the emergency coordinator must assess possible hazards to human
    health or the environment that may result from the release, fire, or explosion.
    This assessment must consider both direct and indirect effects of the release, fire,
    or explosion (e.g., the effects of any toxic, irritating, or asphyxiating gases that
    are generated, or the effects of any hazardous surface water runoffs from water or
    chemical agents used to control fire and heat-induced explosions).
     
    d) If the emergency coordinator determines that the facility has had a release, fire, or
    explosion that could threaten human health or the environment outside the
    facility, he or she must report his findings as follows:
     
    1) If his assessment indicates that evacuation of local areas may be advisable,
    the emergency coordinator must immediately notify appropriate local
    authorities. He or she must be available to help appropriate officials
    decide whether local areas should be evacuated; and
     
    2) The emergency coordinator must immediately notify either the
    government official designated as the on-scene coordinator for that
    geographical area (in the applicable regional contingency plan under
    federal 40 CFR 300), or the National Response Center (using their 24-
    hour toll free number 800-424-8802). The report must include the
    following:
     
    A) The name and telephone number of reporter;
     
    B) The name and address of facility;
     

     
    511
    C) The time and type of incident (e.g., release, fire, etc.);
     
    D) The name and quantity of materials involved, to the extent known;
     
    E) The extent of injuries, if any; and
     
    F) The possible hazards to human health or the environment outside
    the facility.
     
    e) During an emergency the emergency coordinator must take all reasonable
    measures necessary to ensure that fires, explosions, and releases do not occur,
    recur, or spread to other hazardous waste at the facility. These measures must
    include, where applicable, stopping processes and operations, collecting and
    containing released waste, and removing or isolating containers.
     
    f) If the facility stops operations in response to a fire, explosion or release, the
    emergency coordinator must monitor for leaks, pressure buildup, gas generation,
    or ruptures in valves, pipes, or other equipment, wherever this is appropriate.
     
    g) Immediately after an emergency, the emergency coordinator must provide for
    treating, storing, or disposing of recovered waste, contaminated soil, or surface
    water, or any other material that results from a release, fire, or explosion at the
    facility.
     
    BOARD NOTE: Unless the owner or operator can demonstrate in accordance
    with 35 Ill. Adm. Code 721.103(d) or (e) that the recovered material is not a
    hazardous waste, the owner or operator becomes a generator of hazardous waste
    and must manage it in accordance with all applicable requirements of 35 Ill. Adm.
    Code 722, 723, and 725.
     
    h) The emergency coordinator must ensure that, in the affected areas of the facility,
    the following occur:
     
    1) No waste that may be incompatible with the released material is treated,
    stored, or disposed of until cleanup procedures are completed; and
     
    2) All emergency equipment listed in the contingency plan is cleaned and fit
    for its intended use before operations are resumed.
     
    i) The owner or operator must notify the Agency and other appropriate State and
    local authorities that the facility is in compliance with subsection (h) of this
    Section before operations are resumed in the affected areas of the facility.
     
    j) The owner or operator must note in the operating record the time, date, and details
    of any incident that requires implementing the contingency plan. Within 15 days
    after the incident, it must submit a written report on the incident to the Agency.

     
    512
    The report must include the following information:
     
    1) The name, address, and telephone number of the owner or operator;
     
    2) The name, address, and telephone number of the facility;
     
    3) The date, time, and type of incident (e.g., fire, explosion, etc.);
     
    4) The name and quantity of materials involved;
     
    5) The extent of injuries, if any;
     
    6) An assessment of actual or potential hazards to human health or the
    environment, where this is applicable; and
     
    7) The estimated quantity and disposition of recovered material that resulted
    from the incident.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART E: MANIFEST SYSTEM, RECORDKEEPING, AND REPORTING
     
    Section 725.170 Applicability
     
    The regulations in this Subpart E apply to owners and operators of both on-site and off-site
    facilities, except as Section 725.101 provides otherwise. Sections 725.171, 725.172, and
    725.176 do not apply to owners and operators of on-site facilities that do not receive any
    hazardous waste from off-site sources, nor do they apply to owners and operators of off-site
    facilities with respect to waste military munitions exempted from manifest requirements under
    35 Ill. Adm. Code 726.303(a).
     
    BOARD NOTE: This Section corresponds with 40 CFR 265.70(a) (2005), effective September
    5, 2006. The Board omitted 40 CFR 265.70(b), as added at 70 Fed. Reg. 10776 (March 4, 2005),
    since that provision only stated the September 5, 2006 effective date for the newer manifest
    requirements.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.171 Use of Manifest System
     
    a) Receipt of manifested hazardous waste.
     
    a1) The following requirements apply until September 5, 2006: If a facility
    receives hazardous waste accompanied by a manifest, the owner or
    operator or its agent must do each of the following:
     

     
    513
    1A) Sign
    It must sign and date each copy of the manifest to certify that
    the hazardous waste covered by the manifest was received;
     
    2B) Note
    It must note any significant discrepancies in the manifest, as
    defined in Section 725.172(a), on each copy of the manifest;
     
    BOARD NOTE: An owner or operator of a facility whose
    procedures under Section 725.113(c) include waste analysis need
    not perform that analysis before signing the manifest and giving it
    to the transporter. Section 725.172(b), however, requires the
    owner or operator to report any unreconciled discrepancy
    discovered during later analysis.
     
    3C) Immediately
    It must immediately give the transporter at least one
    copy of the signed manifest;
     
    4D) Send
    It must send a copy of the manifest to the generator and the
    Agency within 30 days of the date of delivery; and
     
    5E) Retain
    It must retain at the facility a copy of each manifest for at
    least three years from after the date of delivery.
     
    2) The following requirements apply effective September 5, 2006:
     
    A) If a facility receives hazardous waste accompanied by a manifest,
    the owner, operator, or its agent must sign and date the manifest, as
    indicated in subsection (a)(2)(B) of this Section to certify that the
    hazardous waste covered by the manifest was received, that the
    hazardous waste was received except as noted in the discrepancy
    space of the manifest, or that the hazardous waste was rejected as
    noted in the manifest discrepancy space.
     
    B) If a facility receives a hazardous waste shipment accompanied by a
    manifest, the owner, operator, or its agent must do the following:
     
    i) It must sign and date, by hand, each copy of the manifest;
     
    ii) It must note any discrepancies (as defined in Section
    725.172(b)) on each copy of the manifest;
     
    iii) It must immediately give the transporter at least one copy
    of the manifest;
     
    iv) It must send a copy of the manifest to the generator within
    30 days after delivery; and
     

     
    514
    v) It must retain at the facility a copy of each manifest for at
    least three years after the date of delivery.
     
    C) If a facility receives hazardous waste imported from a foreign
    source, the receiving facility must mail a copy of the manifest to
    the following address within 30 days after delivery: International
    Compliance Assurance Division, OFA/ OECA (2254A), U.S.
    Environmental Protection Agency, Ariel Rios Building, 1200
    Pennsylvania Avenue, NW., Washington, DC 20460.
     
    BOARD NOTE: Subsection (a)(1) of this Section corresponds with 40 CFR
    265.71(a) (2004), effective until September 5, 2006. Subsection (a)(2) of this
    Section corresponds with 40 CFR 265.71(a) (2005), effective September 5, 2006.
     
    b) If a facility receives from a rail or water (bulk shipment) transporter hazardous
    waste that is accompanied by a shipping paper containing all the information
    required on the manifest (excluding the USEPA identification numbers, generator
    certification, and signatures), the owner or operator or its agent must do each of
    the following:
     
    1) Sign
    It must sign and date each copy of the manifest or shipping paper (if
    the manifest has not been received) to certify that the hazardous waste
    covered by the manifest or shipping paper was received;
     
    2) Note
    It must note any significant discrepancies, as defined in Section
    725.172(a), in the manifest or shipping paper (if the manifest has not been
    received) on each copy of the manifest or shipping paper;
     
    BOARD NOTE: The owner or operator of a facility whose procedures
    under Section 725.113(c) include waste analysis need not perform that
    analysis before signing the shipping paper and giving it to the transporter.
    Section 725.172(b), however, requires reporting an unreconciled
    discrepancy discovered during later analysis.
     
    3) Immediately
    It must immediately give the rail or water (bulk shipment)
    transporter at least one copy of the manifest or shipping paper (if the
    manifest has not been received);
     
    4) Forwarding copies of the manifest.
     
    4A) Until September 5, 2006: The facility owner or operator must send
    a copy of the signed and dated manifest to the generator and to the
    Agency within 30 days after the delivery; however, if the manifest
    has not been received within 30 days after delivery, the owner or
    operator, or its agent, must send a copy of the shipping paper
    signed and dated to the generator; and or

     
    515
     
    B) Effective September 5, 2006: The owner or operator must send a
    copy of the signed and dated manifest or a signed and dated copy
    of the shipping paper (if the manifest has not been received within
    30 days after delivery) to the generator within 30 days after the
    delivery; and
     
    BOARD NOTE: 35 Ill. Adm. Code 722.123(c) requires the generator to
    send three copies of the manifest to the facility when hazardous waste is
    sent by rail or water (bulk shipment). Subsection (b)(4)(A) is derived
    from 40 CFR 265.74(b)(4) (2004), effective until September 5, 2006.
    Subsection (b)(4)(B) is derived from 40 CFR 265.74(b)(4) (2005),
    effective September 5, 2006.
     
    5) Retain at the facility a copy of the manifest and shipping paper (if signed
    in lieu of the manifest at the time of delivery) for at least three years from
    the date of delivery.
     
    c) Whenever a shipment of hazardous waste is initiated from a facility, the owner or
    operator of that facility must comply with the requirements of 35 Ill. Adm. Code
    722.
     
    BOARD NOTE: The provisions of 35 Ill. Adm. Code 722.134 are applicable to
    the on-site accumulation of hazardous wastes by generators. Therefore, the
    provisions of 35 Ill. Adm. Code 722.134 apply only to owners or operators that
    are shipping hazardous waste which they generated at that facility.
     
    d) Within three working days of the receipt of a shipment subject to Subpart H of 35
    Ill. Adm. Code 722, the owner or operator of the facility must provide a copy of
    the tracking document bearing all required signatures to the notifier; to the Office
    of Enforcement and Compliance Assurance, Office of Compliance, Enforcement
    Planning, Targeting and Data Division (2222A), Environmental Protection
    Agency, 401 M St., SW, Washington, DC 20460; to the Bureau of Land, Division
    of Land Pollution Control, Illinois Environmental Protection Agency, P.O. Box
    19276, Springfield, IL 62794-9276; and to competent authorities of all other
    concerned countries. The original copy of the tracking document must be
    maintained at the facility for at least three years from the date of signature.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.172 Manifest Discrepancies
     
    a) The following requirements apply until September 5, 2005:
     
    a1) Manifest discrepancies are differences between the quantity or type of
    hazardous waste designated on the manifest or shipping paper and the

     
    516
    quantity or type of hazardous waste a facility actually receives.
     
    b2) Significant discrepancies in quantity are defined as follows:
     
    1A) For bulk waste, variations greater than 10 percent in weight, and
     
    2B) For batch waste, any variation in piece count, such as a
    discrepancy of one drum in a truckload.
     
    c3) Significant discrepancies in type are obvious differences that can be
    discovered by inspection or waste analysis, such as waste solvent
    substituted for waste acid or toxic constituents not reported on the
    manifest or shipping paper.
     
    d4) Upon discovering a significant discrepancy, the owner or operator must
    attempt to reconcile the discrepancy with the waste generator or
    transporter (e.g., with telephone conversations). If the discrepancy is not
    resolved within 15 days after receiving the waste, the owner or operator
    must immediately submit to the Agency a letter describing the discrepancy
    and attempts to reconcile it and a copy of the manifest or shipping paper at
    issue.
     
    b) The following requirements apply effective September 5, 2005:
     
    1) “Manifest discrepancies” are defined as any one of the following:
     
    A) Significant differences (as defined by subsection (b)(2) of this
    Section) between the quantity or type of hazardous waste
    designated on the manifest or shipping paper, and the quantity and
    type of hazardous waste a facility actually receives;
     
    B) Rejected wastes, which may be a full or partial shipment of
    hazardous waste that the treatment, storage, or disposal facility
    cannot accept; or
     
    C) Container residues, which are residues that exceed the quantity
    limits for empty containers set forth in 35 Ill. Adm. Code
    721.107(b).
     
    2) “Significant differences in quantity” are defined as the appropriate of the
    following: for bulk waste, variations greater than 10 percent in weight; or,
    for batch waste, any variation in piece count, such as a discrepancy of one
    drum in a truckload. “Significant differences in type” are defined as
    obvious differences that can be discovered by inspection or waste
    analysis, such as waste solvent substituted for waste acid, or as toxic
    constituents not reported on the manifest or shipping paper.

     
    517
     
    3) Upon discovering a significant difference in quantity or type, the owner or
    operator must attempt to reconcile the discrepancy with the waste
    generator or transporter (
    e.g.,
    with telephone conversations). If the
    discrepancy is not resolved within 15 days after receiving the waste, the
    owner or operator must immediately submit to the Agency a letter
    describing the discrepancy and attempts to reconcile it, and a copy of the
    manifest or shipping paper at issue.
     
    4) Rejection of hazardous waste.
     
    A) Upon rejecting waste or identifying a container residue that
    exceeds the quantity limits for empty containers set forth in 35 Ill.
    Adm. Code 721.107(b), the facility must consult with the generator
    prior to forwarding the waste to another facility that can manage
    the waste. If it is impossible to locate an alternative facility that
    can receive the waste, the facility may return the rejected waste or
    residue to the generator. The facility must send the waste to the
    alternative facility or to the generator within 60 days of the
    rejection or the container residue identification.
     
    B) While the facility is making arrangements for forwarding rejected
    wastes or residues to another facility under this Section, it must
    ensure that either the delivering transporter retains custody of the
    waste, or the facility must provide for secure, temporary custody of
    the waste, pending delivery of the waste to the first transporter
    designated on the manifest prepared under subsection (b)(5) or
    (b)(6) of this Section.
     
    5) Except as provided in subsection (b)(5)(G) of this Section, for full or
    partial load rejections and residues that are to be sent off-site to an
    alternate facility, the facility is required to prepare a new manifest in
    accordance with 35 Ill. Adm. Code 722.120(a) and the following
    instructions:
     
    A) Write the generator’s USEPA identification number in Item 1 of
    the new manifest. Write the generator’s name and mailing address
    in Item 5 of the new manifest. If the mailing address is different
    from the generator’s site address, then write the generator’s site
    address in the designated space in Item 5.
     
    B) Write the name of the alternate designated facility and the
    facility’s USEPA identification number in the designated facility
    block (Item 8) of the new manifest.
     
    C) Copy the manifest tracking number found in Item 4 of the old

     
    518
    manifest to the Special Handling and Additional Information
    Block of the new manifest, and indicate that the shipment is a
    residue or rejected waste from the previous shipment.
     
    D) Copy the manifest tracking number found in Item 4 of the new
    manifest to the manifest reference number line in the Discrepancy
    Block of the old manifest (Item 18a).
     
    E) Write the USDOT description for the rejected load or the residue
    in Item 9 (U.S. DOT Description) of the new manifest and write
    the container types, quantity, and volumes of waste.
     
    F) Sign the Generator’s/Offeror’s Certification to certify, as the
    offeror of the shipment, that the waste has been properly packaged,
    marked and labeled and is in proper condition for transportation.
     
    G) For full load rejections that are made while the transporter remains
    present at the facility, the facility may forward the rejected
    shipment to the alternate facility by completing Item 18b of the
    original manifest and supplying the information on the next
    destination facility in the Alternate Facility space. The facility
    must retain a copy of this manifest for its records, and then give
    the remaining copies of the manifest to the transporter to
    accompany the shipment. If the original manifest is not used, then
    the facility must use a new manifest and comply with subsections
    (b)(5)(A) through (b)(5)(F) of this Section.
     
    6) Except as provided in subsection (b)(6)(G) of this Section, for rejected
    wastes and residues that must be sent back to the generator, the facility is
    required to prepare a new manifest in accordance with 35 Ill. Adm. Code
    722.120(a) and the following instructions:
     
    A) Write the facility’s USEPA identification number in Item 1 of the
    new manifest. Write the generator’s name and mailing address in
    Item 5 of the new manifest. If the mailing address is different from
    the generator’s site address, then write the generator’s site address
    in the designated space for Item 5.
     
    B) Write the name of the initial generator and the generator’s USEPA
    identification number in the designated facility block (Item 8) of
    the new manifest.
     
    C) Copy the manifest tracking number found in Item 4 of the old
    manifest to the Special Handling and Additional Information
    Block of the new manifest, and indicate that the shipment is a
    residue or rejected waste from the previous shipment.

     
    519
     
    D) Copy the manifest tracking number found in Item 4 of the new
    manifest to the manifest reference number line in the Discrepancy
    Block of the old manifest (Item 18a).
     
    E) Write the USDOT description for the rejected load or the residue
    in Item 9 (U.S. DOT Description) of the new manifest and write
    the container types, quantity, and volumes of waste.
     
    F) Sign the Generator’s/Offeror’s Certification to certify, as offeror of
    the shipment, that the waste has been properly packaged, marked
    and labeled and is in proper condition for transportation.
     
    G) For full load rejections that are made while the transporter remains
    at the facility, the facility may return the shipment to the generator
    with the original manifest by completing Item 18b of the manifest
    and supplying the generator’s information in the Alternate Facility
    space. The facility must retain a copy for its records and then give
    the remaining copies of the manifest to the transporter to
    accompany the shipment. If the original manifest is not used, then
    the facility must use a new manifest and comply with subsections
    (b)(6)(A) through (b)(6)(F) of this Section.
     
    7) If a facility rejects a waste or identifies a container residue that exceeds
    the quantity limits for empty containers set forth in 35 Ill. Adm. Code
    721.107(b) after it has signed, dated, and returned a copy of the manifest
    to the delivering transporter or to the generator, the facility must amend its
    copy of the manifest to indicate the rejected wastes or residues in the
    discrepancy space of the amended manifest. The facility must also copy
    the manifest tracking number from Item 4 of the new manifest to the
    Discrepancy space of the amended manifest, and must re-sign and date the
    manifest to certify to the information as amended. The facility must retain
    the amended manifest for at least three years from the date of amendment,
    and must within 30 days, send a copy of the amended manifest to the
    transporter and generator that received copies prior to their being
    amended.
     
    BOARD NOTE: Subsection (a) is derived from 40 CFR 265.72 (2004), effective until
    September 5, 2006. Subsection (b) is derived from 40 CFR 265.72 (2005), effective September
    5, 2006.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.176 Unmanifested Waste Report
     
    a) The following requirements apply until September 5, 2005: If a facility accepts

     
    520
    for treatment, storage, or disposal any hazardous waste from an off-site source
    without an accompanying manifest or without an accompanying shipping paper,
    as described in 35 Ill. Adm. Code 723.120(e)(2), and, if the waste is not excluded
    from the manifest requirement by 35 Ill. Adm. Code 721.105, then the owner or
    operator must prepare and submit a single copy of a report to the Agency within
    15 days after receiving the waste. The unmanifested waste report must be
    submitted on USEPA form 8700-13B. Such report must be designated
    “Unmanifested Waste Report” and must include the following information:
     
    a1) The USEPA identification number, name, and address of the facility;
     
    b2) The date the facility received the waste;
     
    c3) The USEPA identification number, name, and address of the generator
    and the transporter, if available;
     
    d4) A description and the quantity of each unmanifested hazardous waste the
    facility received;
     
    e5) The method of treatment, storage, or disposal for each hazardous waste;
     
    f6) The certification signed by the owner or operator of the facility or its
    authorized representative; and
     
    g7) A brief explanation of why the waste was unmanifested, if known.
     
    b) The following requirements apply effective September 5, 2005: If a facility
    accepts for treatment, storage, or disposal any hazardous waste from an off-site
    source without an accompanying manifest, or without an accompanying shipping
    paper, as described by 35 Ill. Adm. Code 723.120(e), and if the waste is not
    excluded from the manifest requirement by 35 Ill. Adm. Code 260 through 265,
    then the owner or operator must prepare and submit a letter to the Agency within
    fifteen days after receiving the waste. The unmanifested waste report must
    contain the following information:
     
    1) The USEPA identification number, name, and address of the facility;
     
    2) The date the facility received the waste;
     
    3) The USEPA identification number, name, and address of the generator
    and the transporter, if available;
     
    4) A description and the quantity of each unmanifested hazardous waste the
    facility received;
     
    5) The method of treatment, storage, or disposal for each hazardous waste;

     
    521
     
    6) The certification signed by the owner or operator of the facility or its
    authorized representative; and
     
    7) A brief explanation of why the waste was unmanifested, if known.
     
    (BOARD NOTE: Small quantities of hazardous waste are excluded from regulation under this
    Part and do not require a manifest. Where a facility received unmanifested hazardous waste, the
    Board suggests USEPA has suggested that the owner or operator obtain from each generator a
    certification that the waste qualifies for exclusion. Otherwise, the Board suggests USEPA has
    suggested that the owner or operator file an unmanifested waste report for the hazardous waste
    movement. Subsection (a) is derived from 40 CFR 265.76 (2004), effective until September 5,
    2006. Subsection (b) is derived from 40 CFR 265.76 (2005), effective September 5, 2006.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART F: GROUNDWATER MONITORING
     
    Section 725.190 Applicability
     
    a) The owner or operator of a surface impoundment, landfill, or land treatment
    facility that is used to manage hazardous waste must implement a groundwater
    monitoring program capable of determining the facility’s impact on the quality of
    groundwater in the uppermost aquifer underlying the facility, except as Section
    725.101 and subsection (c) of this Section provide otherwise.
     
    b) Except as subsections (c) and (d) of this Section provide otherwise, the owner or
    operator must install, operate, and maintain a groundwater monitoring system that
    meets the requirements of Section 725.191 and must comply with Sections
    725.192 through 725.194. This groundwater monitoring program must be carried
    out during the active life of the facility and for disposal facilities during the post-
    closure care period as well.
     
    c) All or part of the groundwater monitoring requirements of this Subpart F may be
    waived if the owner or operator can demonstrate that there is a low potential for
    migration of hazardous waste or hazardous waste constituents from the facility via
    the uppermost aquifer to water supply wells (domestic, industrial, or agricultural)
    or to surface water. This demonstration must be in writing and must be kept at
    the facility. This demonstration must be certified by a qualified geologist or
    geotechnical engineer and must establish the following:
     
    1) The potential for migration of hazardous waste or hazardous waste
    constituents from the facility to the uppermost aquifer by an evaluation of
    the following information:
     
    A) A water balance of precipitation, evapotranspiration, runoff, and

     
    522
    infiltration; and
     
    B) Unsaturated zone characteristics (i.e., geologic materials, physical
    properties, and depth to ground water); and
     
    2) The potential for hazardous waste or hazardous waste constituents that
    enter the uppermost aquifer to migrate to a water supply well or surface
    water by an evaluation of the following information:
     
    A) Saturated zone characteristics (i.e., geologic materials, physical
    properties, and rate of groundwater flow); and
     
    B) The proximity of the facility to water supply wells or surface
    water.
     
    d) If an owner or operator assumes (or knows) that groundwater monitoring of
    indicator parameters in accordance with Sections 725.191 and 725.192 would
    show statistically significant increases (or decreases in the case of pH) when
    evaluated under Section 725.193(b), it may install, operate, and maintain an
    alternate groundwater monitoring system (other than the one described in
    Sections 725.191 and 725.192). If the owner or operator decides to use an
    alternate groundwater monitoring system it must have done as follows:
     
    1) By November 19, 1981, the owner or operator must have submitted to the
    USEPA Region 5 a specific plan, certified by a qualified geologist or
    geotechnical engineer, that satisfies the requirements of federal 40 CFR
    265.93(d)(3) for an alternate groundwater monitoring system;
     
    2) By November 19, 1981, the owner or operator must have initiated the
    determinations specified in federal 40 CFR 265.93(d)(4);
     
    3) The owner or operator must have prepared and submitted a written report
    in accordance with Section 725.193(d)(5);
     
    4) The owner or operator must continue to make the determinations specified
    in Section 725.193(d)(4) on a quarterly basis until final closure of the
    facility; and
     
    5) The owner or operator must comply with the recordkeeping and reporting
    requirements in Section 725.194(b).
     
    e) The groundwater monitoring requirements of this Subpart F may be waived with
    respect to any surface impoundment of which the following is true:
     
    1) The impoundment is used to neutralize wastes that are hazardous solely
    because they exhibit the corrosivity characteristic under 35 Ill. Adm. Code

     
    523
    721.122 or which are listed as hazardous wastes in Subpart D of 35 Ill.
    Adm. Code 721 only for this reason; and
     
    2) The impoundment contains no other hazardous wastes, if the owner or
    operator can demonstrate that there is no potential for migration of
    hazardous wastes from the impoundment. The demonstration must
    establish, based upon consideration of the characteristics of the wastes and
    the impoundment, that the corrosive wastes will be neutralized to the
    extent that they no longer meet the corrosivity characteristic before they
    can migrate out of the impoundment. The demonstration must be in
    writing and must be certified by a qualified professional.
     
    f) A permit or enforceable document can contain alternative requirements for
    groundwater monitoring that replace all or part of the requirements of this Subpart F
    applicable to a regulated unit (as defined in 35 Ill. Adm. Code 724.190), as provided
    under 35 Ill. Adm. Code 703.161, where the Board has determined by an adjusted
    standard granted pursuant to Section 28.1 of the Act [415 ILCS 5/28.1] and
    Subpart D of 35 Ill. Adm. Code 104 the following:
     
    1) The regulated unit is situated among solid waste management units (or areas
    of concern), a release has occurred, and both the regulated unit and one or
    more solid waste management units (or areas of concern) are likely to have
    contributed to the release; and
     
    2) It is not necessary to apply the groundwater monitoring requirements of this
    Subpart F because the alternative requirements will protect human health
    and the environment. The alternative standards for the regulated unit must
    meet the requirements of 35 Ill. Adm. Code 724.201(a).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.192 Sampling and Analysis
     
    a) The owner or operator must obtain and analyze samples from the installed
    groundwater monitoring system. The owner or operator must develop and follow
    a groundwater sampling and analysis plan. The owner or operator must keep this
    plan at the facility. The plan must include procedures and techniques for each of
    the following:
     
    1) Sample collection;
     
    2) Sample preservation and shipment;
     
    3) Analytical procedures; and
     
    4) Chain of custody control.

     
    524
     
    BOARD NOTE: See “Procedures Manual For Groundwater Ground Water
    Monitoring At Solid Waste Disposal Facilities,” USEPA document number EPA-
    530/SW-611, and “Methods for Chemical Analysis of Water and Wastes,”
    USEPA document number EPA-600/4-79-020, incorporated by reference in 35
    Ill. Adm. Code 720.111(a), for discussions of sampling and analysis procedures.
     
    b) The owner or operator must determine the concentration or value of the following
    parameters in groundwater samples in accordance with subsections (c) and (d) of
    this Section:
     
    1) Parameters characterizing the suitability of the groundwater as a drinking
    water supply, as specified in Appendix C to this Part.
     
    2) The following parameters establishing groundwater quality:
     
    A) Chloride,
     
    B) Iron,
     
    C) Manganese,
     
    D) Phenols,
     
    E) Sodium, and
     
    F) Sulfate.
     
    BOARD NOTE: These parameters are to be used as a basis for
    comparison in the event a groundwater quality assessment is
    required under Section 725.193(d).
     
    3) The following parameters used as indicators of groundwater
    contamination:
     
    A) pH,
     
    B) Specific Conductance,
     
    C) Total Organic Carbon, and
     
    D) Total Organic Halogen.
     
    c) Establishing background concentrations.
     
    1) For all monitoring wells, the owner or operator must establish initial

     
    525
    background concentrations or values of all parameters specified in
    subsection (b) of this Section. The owner or operator must do this
    quarterly for one year.
     
    2) For each of the indicator parameters specified in subsection (b)(3) of this
    Section, the owner or operator must obtain at least four replicate
    measurements for each sample and determine the initial background
    arithmetic mean and variance by pooling the replicate measurements for
    the respective parameter concentrations or values in samples obtained
    from upgradient wells during the first year.
     
    d) After the first year, the owner or operator must sample all monitoring wells and
    analyze the samples with the following frequencies:
     
    1) Samples collected to establish groundwater quality must be obtained and
    analyzed for the parameters specified in subsection (b)(2) of this Section
    at least annually.
     
    2) Samples collected to indicate groundwater contamination must be
    obtained and analyzed for the parameters specified in subsection (b)(3) of
    this Section at least semi-annually.
     
    e) The owner or operator must determine the elevation of the groundwater surface at
    each monitoring well each time a sample is obtained.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART H: FINANCIAL REQUIREMENTS
     
    Section 725.243 Financial Assurance for Closure
     
    An owner or operator of each facility must establish financial assurance for closure of the
    facility. The owner or operator must choose from the options specified in subsections (a)
    through (e) of this Section.
     
    a) Closure trust fund.
     
    1) An owner or operator may satisfy the requirements of this Section by
    establishing a closure trust fund that conforms to the requirements of this
    subsection and submitting an original, signed duplicate of the trust
    agreement to the Agency. The trustee must be an entity that has the
    authority to act as a trustee and whose trust operations are regulated and
    examined by a federal or State agency.
     
    2) The wording of the trust agreement must be as specified in 35 Ill. Adm.
    Code 724.251 and the trust agreement must be accompanied by a formal

     
    526
    certification of acknowledgment as specified in 35 Ill. Adm. Code
    724.251. Schedule A of the trust agreement must be updated within 60
    days after a change in the amount of the current closure cost estimate
    covered by the agreement.
     
    3) Payments into the trust fund must be made annually by the owner or
    operator over the 20 years beginning May 19, 1981, or over the remaining
    operating life of the facility as estimated in the closure plan, whichever
    period is shorter; this period is hereafter referred to as the “pay-in period.”
    The payments into the closure trust fund must be made as follows:
     
    A) The first payment must be made before May 19, 1981, except as
    provided in subsection (a)(5) of this Section. The first payment
    must be at least equal to the current closure cost estimate, except
    as provided in subsection (f) of this Section, divided by the number
    of years in the pay-in period.
     
    B) Subsequent payments must be made no later than 30 days after
    each anniversary date of the first payment. The amount of each
    subsequent payment must be determined by this formula:
     
    Y
    CV
    CE
    nt
    Next Payme
    =
      
     
    Where:
     
    CE is the current closure cost estimate,
    CV is the current value of the trust fund, and
    Y is the number of years remaining in the pay-in period.
     
    4) The owner or operator may accelerate payments into the trust fund or may
    deposit the full amount of the current closure cost estimate at the time the
    fund is established. However, the owner or operator must maintain the
    value of the fund at no less than the value that the fund would have if
    annual payments were made as specified in subsection (a)(3) of this
    Section.
     
    5) If the owner or operator establishes a closure trust fund after having used
    one or more alternate mechanisms specified in this Section, the owner or
    operator’s first payment must be in at least the amount that the fund would
    contain if the trust fund were established initially and annual payments
    made as specified in subsection (a)(3) of this Section.
     
    6) After the pay-in period is completed, whenever the current closure cost
    estimate changes, the owner or operator must compare the new estimate
    with the trustee’s most recent annual valuation of the trust fund. If the

     
    527
    value of the fund is less than the amount of the new estimate, the owner or
    operator, within 60 days after the change in the cost estimate, must either
    deposit an amount into the fund so that its value after this deposit at least
    equals the amount of the current closure cost estimate, or obtain other
    financial assurance, as specified in this Section, to cover the difference.
     
    7) If the value of the trust fund is greater than the total amount of the current
    closure cost estimate, the owner or operator may submit a written request
    to the Agency for release of the amount in excess of the current closure
    cost estimate.
     
    8) If an owner or operator substitutes other financial assurance, as specified
    in this Section, for all or part of the trust fund, the owner or operator may
    submit a written request to the Agency for release of the amount in excess
    of the current closure cost estimate covered by the trust fund.
     
    9) Within 60 days after receiving a request from the owner or operator for
    release of funds as specified in subsection (a)(7) or (a)(8) of this Section,
    the Agency must instruct the trustee to release to the owner or operator
    such funds as the Agency specifies in writing.
     
    10) After beginning partial or final closure, an owner or operator or another
    person authorized to conduct partial or final closure may request
    reimbursement for closure expenditures by submitting itemized bills to the
    Agency. The owner or operator may request reimbursement for partial
    closure only if sufficient funds are remaining in the trust fund to cover the
    maximum costs of closing the facility over its remaining operating life.
    Within 60 days after receiving bills for partial or final closure activities,
    the Agency must instruct the trustee to make reimbursement in those
    amounts as the Agency specifies in writing if the Agency determines that
    the partial or final closure expenditures are in accordance with the
    approved closure plan, or otherwise justified. If the Agency determines
    that the maximum cost of closure over the remaining life of the facility
    will be significantly greater than the value of the trust fund, it must
    withhold reimbursement of such amounts as it deems prudent until it
    determines, in accordance with subsection (h) of this Section, that the
    owner or operator is no longer required to maintain financial assurance for
    final closure of the facility. If the Agency does not instruct the trustee to
    make such reimbursements, the Agency must provide the owner or
    operator a detailed written statement of reasons.
     
    11) The Agency must agree to termination of the trust when either of the
    following occurs:
     
    A) An owner or operator substitutes alternate financial assurance, as
    specified in this Section; or

     
    528
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (h) of this Section.
     
    b) Surety bond guaranteeing payment into a closure trust fund.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining a surety bond that conforms to the requirements of this
    subsection (b) and submitting the bond to the Agency. The surety
    company issuing the bond must, at a minimum, be among those listed as
    acceptable sureties on federal bonds in Circular 570 of the U.S.
    Department of the Treasury.
     
    2) The wording of the surety bond must be as specified in 35 Ill. Adm. Code
    724.251.
     
    3) The owner or operator that uses a surety bond to satisfy the requirements
    of this Section must also establish a standby trust fund. Under the terms
    of the bond, all payments made thereunder will be deposited by the surety
    directly into the standby trust fund in accordance with instructions from
    the Agency. This standby trust fund must meet the requirements specified
    in subsection (a) of this Section, except as follows:
     
    A) An original, signed duplicate of the trust agreement must be
    submitted to the Agency with the surety bond; and
     
    B) Until the standby trust fund is funded pursuant to the requirements
    of this Section, the following are not required by these regulations:
     
    i) Payments into the trust fund, as specified in subsection (a);
     
    ii) Updating of Schedule A of the trust agreement (see 40 CFR
    264.251(a)) 35 Ill. Adm. Code 724.251(a)) to show current
    closure cost estimates;
     
    iii) Annual valuations, as required by the trust agreement; and
     
    iv) Notices of nonpayment, as required by the trust agreement.
     
    4) The bond must guarantee that the owner or operator will:
     
    A) Fund the standby trust fund in an amount equal to the penal sum of
    the bond before the beginning of final closure of the facility;
     
    B) Fund the standby trust fund in an amount equal to the penal sum
    within 15 days after an order to begin final closure is issued by the

     
    529
    Board or a court of competent jurisdiction; or
     
    C) Provide alternate financial assurance, as specified in this Section,
    and obtain the Agency’s written approval of the assurance
    provided, within 90 days after receipt by both the owner or
    operator and the Agency of a notice of cancellation of the bond
    from the surety.
     
    5) Under the terms of the bond, the surety will become liable on the bond
    obligation when the owner or operator fails to perform as guaranteed by
    the bond.
     
    6) The penal sum of the bond must be in an amount at least equal to the
    current closure cost estimate, except as provided in subsection (f) of this
    Section.
     
    7) Whenever the current closure cost estimate increases to an amount greater
    than the penal sum, the owner or operator, within 60 days after the
    increase, must either cause the penal sum to be increased to an amount at
    least equal to the current closure cost estimate and submit evidence of
    such increase to the Agency, or obtain other financial assurance, as
    specified in this Section, to cover the increase. Whenever the current
    closure cost estimate decreases, the penal sum may be reduced to the
    amount of the current closure cost estimate following written approval by
    the Agency.
     
    8) Under the terms of the bond, the surety may cancel the bond by sending
    notice of cancellation by certified mail to the owner or operator and to the
    Agency. Cancellation may not occur, however, during the 120 days
    beginning on the date of receipt of the notice of cancellation by both the
    owner or operator and the Agency, as evidenced by the return receipts.
     
    9) The owner or operator may cancel the bond if the Agency has given prior
    written consent based on its receipt of evidence of alternate financial
    assurance, as specified in this Section.
     
    c) Closure letter of credit.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining an irrevocable standby letter of credit that conforms to the
    requirements of this subsection (c) and submitting the letter to the Agency.
    The issuing institution must be an entity that has the authority to issue
    letters of credit and whose letter-of-credit operations are regulated and
    examined by a federal or State agency.
     
    2) The wording of the letter of credit must be as specified in 35 Ill. Adm.

     
    530
    Code 724.251.
     
    3) An owner or operator that uses a letter of credit to satisfy the requirements
    of this Section must also establish a standby trust fund. Under the terms
    of the letter of credit, all amounts paid pursuant to a draft by the Agency
    must be deposited by the issuing institution directly into the standby trust
    fund in accordance with instructions from the Agency. This standby trust
    fund must meet the requirements of the trust fund specified in subsection
    (a) of this Section, except as follows:
     
    A) An original, signed duplicate of the trust agreement must be
    submitted to the Agency with the letter of credit; and
     
    B) Unless the standby trust fund is funded pursuant to the
    requirements of this Section, the following are not required by
    these regulations:
     
    i) Payments into the trust fund, as specified in subsection (a)
    of this Section;
     
    ii) Updating of Schedule A of the trust agreement (as specified
    in 35 Ill. Adm. Code 724.251) to show current closure cost
    estimates;
     
    iii) Annual valuations, as required by the trust agreement; and
     
    iv) Notices of nonpayment as required by the trust agreement.
     
    4) The letter of credit must be accompanied by a letter from the owner or
    operator referring to the letter of credit by number, issuing institution, and
    date and providing the following information: the USEPA identification
    number, name, and address of the facility, and the amount of funds
    assured for closure of the facility by the letter of credit.
     
    5) The letter of credit must be irrevocable and issued for a period of at least
    one year. The letter of credit must provide that the expiration date will be
    automatically extended for a period of at least one year unless, at least 120
    days before the current expiration date, the issuing institution notifies both
    the owner or operator and the Agency by certified mail of a decision not to
    extend the expiration date. Under the terms of the letter of credit, the 120
    days will begin on the date when both the owner or operator and the
    Agency have received the notice, as evidenced by the return receipts.
     
    6) The letter of credit must be issued in an amount at least equal to the
    current closure cost estimate, except as provided in subsection (f) of this
    Section.

     
    531
     
    7) Whenever the current closure cost estimate increases to an amount greater
    than the amount of the credit, the owner or operator, within 60 days after
    the increase, must either cause the amount of the credit to be increased so
    that it at least equals the current closure cost estimate and submit evidence
    of such increase to the Agency, or obtain other financial assurance, as
    specified in this Section, to cover the increase. Whenever the current
    closure cost estimate decreases, the amount of the credit may be reduced
    to the amount of the current closure cost estimate following written
    approval by the Agency.
     
    8) Following a final judicial determination or Board order finding that the
    owner or operator has failed to perform final closure in accordance with
    the approved closure plan when required to do so, the Agency may draw
    on the letter of credit.
     
    9) If the owner or operator does not establish alternate financial assurance, as
    specified in this Section, and obtain written approval of such alternate
    assurance from the Agency within 90 days after receipt by both the owner
    or operator and the Agency of a notice from issuing institution that it has
    decided not to extend the letter of credit beyond the current expiration
    date, the Agency must draw on the letter of credit. The Agency may delay
    the drawing if the issuing institution grants an extension of the term of the
    credit. During the last 30 days of any such extension the Agency must
    draw on the letter of credit if the owner or operator has failed to provide
    alternate financial assurance, as specified in this Section, and obtain
    written approval of such assurance from the Agency.
     
    10) The Agency must return the letter of credit to the issuing institution for
    termination when one of the following occurs:
     
    A) An owner or operator substitutes alternate financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (h) of this Section.
     
    d) Closure insurance.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining closure insurance that conforms to the requirements of this
    subsection and submitting a certificate of such insurance to the Agency.
    At a minimum, the insurer must be licensed to transact the business of
    insurance, or eligible to provide insurance as an excess or surplus lines
    insurer, in one or more States.
     

     
    532
    2) The wording of the certificate of insurance must be as specified in 35 Ill.
    Adm. Code 724.251.
     
    3) The closure insurance policy must be issued for a face amount at least
    equal to the current closure cost estimate, except as provided in subsection
    (f) of this Section. The term “face amount” means the total amount the
    insurer is obligated to pay under the policy. Actual payments by the
    insurer will not change the face amount, although the insurer’s future
    liability will be lowered by the amount of the payments.
     
    4) The closure insurance policy must guarantee that funds will be available
    to close the facility whenever final closure occurs. The policy must also
    guarantee that, once final closure begins, the insurer will be responsible
    for paying out funds, up to an amount equal to the face amount of the
    policy, upon the direction of the Agency to such party or parties as the
    Agency specifies.
     
    5) After beginning partial or final closure, an owner or operator or any other
    person authorized to conduct closure may request reimbursement for
    closure expenditures by submitting itemized bills to the Agency. The
    owner or operator may request reimbursement for partial closure only if
    the remaining value of the policy is sufficient to cover the maximum costs
    of closing the facility over its remaining operating life. Within 60 days
    after receiving bills for closure activities, the Agency must instruct the
    insurer to make reimbursement in such amounts as the Agency specifies in
    writing if the Agency determines that the partial or final closure
    expenditures are in accordance with the approved closure plan or
    otherwise justified. If the Agency determines that the maximum cost of
    closure over the remaining life of the facility will be significantly greater
    than the face amount of the policy, it must withhold reimbursement of
    such amounts as it deems prudent until it determines, in accordance with
    subsection (h) of this Section, that the owner or operator is no longer
    required to maintain financial assurance for final closure of the particular
    facility. If the Agency does not instruct the insurer to make such
    reimbursements, the Agency must provide the owner or operator with a
    detailed written statement of reasons.
     
    6) The owner or operator must maintain the policy in full force and effect
    until the Agency consents to termination of the policy by the owner or
    operator as specified in subsection (d)(10) of this Section. Failure to pay
    the premium, without substitution of alternate financial assurance as
    specified in this Section, will constitute a significant violation of these
    regulations, warranting such remedy as the Board may impose pursuant to
    the Environmental Protection Act. Such violation will be deemed to begin
    upon receipt by the Agency of a notice of future cancellation, termination,
    or failure to renew due to nonpayment of the premium, rather than upon

     
    533
    the date of expiration.
     
    7) Each policy must contain a provision allowing assignment of the policy to
    a successor owner or operator. Such assignment may be conditional upon
    consent of the insurer, provided such consent is not unreasonably refused.
     
    8) The policy must provide that the insurer may not cancel, terminate, or fail
    to renew the policy except for failure to pay the premium. The automatic
    renewal of the policy must, at a minimum, provide the insured with the
    option of renewal at the face amount of the expiring policy. If there is a
    failure to pay the premium, the insurer may elect to cancel, terminate, or
    fail to renew the policy by sending notice by certified mail to the owner or
    operator and the Agency. Cancellation, termination, or failure to renew
    may not occur, however, during the 120 days beginning with the date of
    receipt of the notice by both the Agency and the owner or operator, as
    evidenced by the return receipts. Cancellation, termination, or failure to
    renew may not occur and the policy will remain in full force and effect in
    the event that, on or before the date of expiration, one of the following
    occurs:
     
    A) The Agency deems the facility abandoned;
     
    B) Interim status is terminated or revoked;
     
    C) Closure is ordered by the Board or a court of competent
    jurisdiction;
     
    D) The owner or operator is named as debtor in a voluntary or
    involuntary proceeding under 11 U.S.C. (Bankruptcy); or
     
    E) The premium due is paid.
     
    9) Whenever the current closure cost estimate increases to an amount greater
    than the face amount of the policy, the owner or operator, within 60 days
    after the increase, must either cause the face amount to be increased to an
    amount at least equal to the current closure cost estimate and submit
    evidence of such increase to the Agency, or obtain other financial
    assurance as specified in this Section to cover the increase. Whenever the
    current closure cost estimate decreases, the face amount may be reduced
    to the amount of the current closure cost estimate following written
    approval by the Agency.
     
    10) The Agency must give written consent to the owner or operator that the
    owner or operator may terminate the insurance policy when either of the
    following occurs:
     

     
    534
    A) An owner or operator substitutes alternate financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (h) of this Section.
     
    e) Financial test and corporate guarantee for closure.
     
    1) An owner or operator may satisfy the requirements of this Section by
    demonstrating that the owner or operator passes a financial test as
    specified in this subsection. To pass this test the owner or operator must
    meet the criteria of either subsection (e)(1)(A) or (e)(1)(B) of this Section:
     
    A) The owner or operator must have all of the following:
     
    i) Two of the following three ratios: a ratio of total liabilities
    to net worth less than 2.0; a ratio of the sum of net income
    plus depreciation, depletion and amortization to total
    liabilities greater than 0.1; and a ratio of current assets to
    current liabilities greater than 1.5;
     
    ii) Net working capital and tangible net worth each at least six
    times the sum of the current closure and post-closure cost
    estimates and the current plugging and abandonment cost
    estimates;
     
    iii) Tangible net worth of at least $10 million; and
     
    iv) Assets located in the United States amounting to at least 90
    percent of total assets or at least six times the sum of the
    current closure and post-closure cost estimates and the
    current plugging and abandonment cost estimates.
     
    B) The owner or operator must have all of the following:
     
    i) A current rating for its most recent bond issuance of AAA,
    AA, A, or BBB, as issued by Standard and Poor’s, or Aaa,
    Aa, A, or Baa, as issued by Moody’s;
     
    ii) Tangible net worth at least six times the sum of the current
    closure and post-closure cost estimates and the current
    plugging and abandonment cost estimates;
     
    iii) Tangible net worth of at least $10 million; and
     
    iv) Assets located in the United States amounting to at least 90

     
    535
    percent of total assets or at least six times the sum of the
    current closure and post-closure cost estimates and the
    current plugging and abandonment cost estimates.
     
    2) The phrase “current closure and post-closure cost estimates,” as used in
    subsection (e)(1) of this Section, refers to the cost estimates required to be
    shown in subsections 1 through 4 of the letter from the owner’s or
    operator’s chief financial officer (40 CFR 264.151(f)) (incorporated by
    reference in see 35 Ill. Adm. Code 724.251). The phrase “current
    plugging and abandonment cost estimates,” as used in subsection (e)(1) of
    this Section, refers to the cost estimates required to be shown in
    subsections 1 through 4 of the letter from the owner’s or operator’s chief
    financial officer (40 CFR 144.70(f)), incorporated by reference in see 35
    Ill. Adm. Code 704.240).
     
    3) To demonstrate that the owner or operator meets this test, the owner or
    operator must submit each of the following items to the Agency:
     
    A) A letter signed by the owner’s or operator’s chief financial officer
    and worded as specified in 35 Ill. Adm. Code 724.251;
     
    B) A copy of the independent certified public accountant’s report on
    examination of the owner’s or operator’s financial statements for
    the latest completed fiscal year; and
     
    C) A special report from the owner’s or operator’s independent
    certified public accountant to the owner or operator stating the
    following:
     
    i) That the accountant has compared the data that the letter
    from the chief financial officer specifies as having been
    derived from the independently audited, year-end financial
    statements for the latest fiscal year with the amounts in
    such financial statements; and
     
    ii) In connection with that procedure, that no matters came to
    the accountant’s attention which caused the accountant to
    believe that the specified data should be adjusted.
     
    4) This subsection (e)(4) corresponds with 40 CFR 265.143(e)(4), a federal
    provision relating to an extension of the time to file the proofs of financial
    assurance required by this subsection (e) granted by USEPA. This
    statement maintains structural consistency with the corresponding federal
    regulations.
     
    5) After the initial submission of items specified in subsection (e)(3) of this

     
    536
    Section, the owner or operator must send updated information to the
    Agency within 90 days after the close of each succeeding fiscal year. This
    information must consist of all three items specified in subsection (e)(3) of
    this Section.
     
    6) If the owner or operator no longer meets the requirements of subsection
    (e)(1) of this Section, the owner or operator must send notice to the
    Agency of intent to establish alternate financial assurance as specified in
    this Section. The notice must be sent by certified mail within 90 days
    after the end of the fiscal year for which the year-end financial data show
    that the owner or operator no longer meets the requirements. The owner
    or operator must provide the alternate financial assurance within 120 days
    after the end of such fiscal year.
     
    7) The Agency may, based on a reasonable belief that the owner or operator
    may no longer meet the requirements of subsection (e)(1) of this Section,
    require reports of financial condition at any time from the owner or
    operator in addition to those specified in subsection (e)(3) of this Section.
    If the Agency finds, on the basis of such reports or other information, that
    the owner or operator no longer meets the requirements of subsection
    (e)(1) of this Section, the owner or operator must provide alternate
    financial assurance as specified in this Section within 30 days after
    notification of such a finding.
     
    8) The Agency may disallow use of this test on the basis of qualifications in
    the opinion expressed by the independent certified public accountant in
    the accountant’s report on examination of the owner’s or operator’s
    financial statements (see subsection (e)(3)(B) of this Section). An adverse
    opinion or a disclaimer of opinion will be cause for disallowance. The
    Agency must evaluate other qualifications on an individual basis. The
    owner or operator must provide alternate financial assurance as specified
    in this Section within 30 days after notification of the disallowance.
     
    9) The owner or operator is no longer required to submit the items specified
    in subsection (e)(3) of this Section when either of the following occurs:
     
    A) An owner or operator substitutes alternate financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (h) of this Section.
     
    10) An owner or operator may meet the requirements of this Section by
    obtaining a written guarantee, hereafter referred to as “corporate
    guarantee.” The guarantor must be the direct or higher-tier parent
    corporation of the owner or operator, a firm whose parent corporation is

     
    537
    also the parent corporation of the owner or operator, or a firm with a
    “substantial business relationship” with the owner or operator. The
    guarantor must meet the requirements for owners or operators in
    subsections (e)(1) through (e)(8) of this Section, and must comply with the
    terms of the corporate guarantee. The wording of the corporate guarantee
    must be identical to the wording specified in 35 Ill. Adm. Code 724.251.
    The corporate guarantee must accompany the items sent to the Agency as
    specified in subsection (e)(3) of this Section. One of these items must be
    the letter from the guarantor’s chief financial officer. If the guarantor’s
    parent corporation is also the parent corporation of the owner or operator,
    the letter must describe the value received in consideration of the
    guarantee. If the guarantor is a firm with a “substantial business
    relationship” with the owner or operator, this letter must describe this
    substantial business relationship” and the value received in consideration
    of the guarantee. The terms of the corporate guarantee must provide the
    following:
     
    A) That, if the owner or operator fails to perform final closure of a
    facility covered by the corporate guarantee in accordance with the
    closure plan and other interim status requirements whenever
    required to do so, the guarantor will do so or establish a trust fund
    as specified in subsection (a) of this Section, in the name of the
    owner or operator.
     
    B) That the corporate guarantee will remain in force unless the
    guarantor sends notice of cancellation by certified mail to the
    owner or operator and to the Agency. Cancellation may not occur,
    however, during the 120 days beginning on the date of receipt of
    the notice of cancellation by both the owner or operator and the
    Agency, as evidenced by the return receipts.
     
    C) That, if the owner or operator fails to provide alternate financial
    assurance as specified in this Section and obtain the written
    approval of such alternate assurance from the Agency within 90
    days after receipt by both the owner or operator and the Agency of
    a notice of cancellation of the corporate guarantee from the
    guarantor, the guarantor will provide such alternate financial
    assurance in the name of the owner or operator.
     
    f) Use of multiple financial mechanisms. An owner or operator may satisfy the
    requirements of this Section by establishing more than one financial mechanism
    per facility. These mechanisms are limited to trust funds, surety bonds, letters of
    credit, and insurance. The mechanisms must be as specified in subsections (a)
    through (d) of this Section, respectively, except that it is the combination of
    mechanisms, rather than the single mechanism, that must provide financial
    assurance for an amount at least equal to the current closure cost estimate. If an

     
    538
    owner or operator uses a trust fund in combination with a surety bond or a letter
    of credit, the owner or operator may use the trust fund as the standby trust fund
    for the other mechanisms. A single standby trust fund may be established for two
    or more mechanisms. The Agency may use any or all of the mechanisms to
    provide for closure of the facility.
     
    g) Use of a financial mechanism for multiple facilities. An owner or operator may
    use a financial assurance mechanism specified in this Section to meet the
    requirements of this Section for more than one facility. Evidence of financial
    assurance submitted to the Agency must include a list showing, for each facility,
    the USEPA identification number, name, address, and the amount of funds for
    closure assured by the mechanism. The amount of funds available through the
    mechanism must be no less than the sum of funds that would be available if a
    separate mechanism had been established and maintained for each facility. The
    amount of funds available to the Agency must be sufficient to close all of the
    owner or operator’s facilities. In directing funds available through the mechanism
    for closure of any of the facilities covered by the mechanism, the Agency may
    direct only the amount of funds designated for that facility, unless the owner or
    operator agrees to the use of additional funds available under the mechanism.
     
    h) Release of the owner or operator from the requirements of this Section. Within
    60 days after receiving certifications from the owner or operator and an
    independent registered professional engineer that final closure has been
    completed in accordance with the approved closure plan, the Agency must notify
    the owner or operator in writing that the owner or operator is no longer required
    by this Section to maintain financial assurance for closure of the facility, unless
    the Agency determines that closure has not been in accordance with the approved
    closure plan. The Agency must provide the owner or operator a detailed written
    statement of any such determination that closure has not been in accordance with
    the approved closure plan.
     
    i) Appeal. The following Agency actions are deemed to be permit modifications or
    refusals to modify for purposes of appeal to the Board (35 Ill. Adm. Code
    702.184(e)(3)):
     
    1) An increase in, or a refusal to decrease the amount of, a bond, letter of
    credit, or insurance; or
     
    2) Requiring alternate assurance upon a finding that an owner or operator or
    parent corporation no longer meets a financial test.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.245 Financial Assurance for Post-Closure Monitoring and Maintenance
     
    An owner or operator of a facility with a hazardous waste disposal unit must establish financial

     
    539
    assurance for post-closure care of the disposal units. The owner or operator must choose from
    the following options:
     
    a) Post-closure trust fund.
     
    1) An owner or operator may satisfy the requirements of this Section by
    establishing a post-closure trust fund that conforms to the requirements of
    this subsection and submitting an original, signed duplicate of the trust
    agreement to the Agency. The trustee must be an entity that has the
    authority to act as a trustee and whose trust operations are regulated and
    examined by a federal or State agency.
     
    2) The wording of the trust agreement must be as specified in 35 Ill. Adm.
    Code 724.251 and the trust agreement must be accompanied by a formal
    certification of acknowledgment (as specified in 35 Ill. Adm. Code
    724.251). Schedule A of the trust agreement must be updated within 60
    days after a change in the amount of the current post-closure cost estimate
    covered by the agreement.
     
    3) Payments into the trust fund must be made annually by the owner or
    operator over the 20 years beginning May 19, 1981, or over the remaining
    operating life of the facility as estimated in the closure plan, whichever
    period is shorter; this period is hereafter referred to as the “pay-in period.”
    The payments into the post-closure trust fund must be made as follows:
     
    A) The first payment must have been made before May 19, 1981,
    except as provided in subsection (a)(5) of this Section. The first
    payment must be at least equal to the current post-closure cost
    estimate, except as provided in subsection (f) of this Section,
    divided by the number of years in the pay-in period.
     
    B) Subsequent payments must be made no later than 30 days after
    each anniversary date of the first payment. The amount of each
    subsequent payment must be determined by this formula:
     
    Y
    CV
    CE
    nt
    Next Payme
    =
      
     
    Where:
     
    CE is the current closure cost estimate,
    CV is the current value of the trust fund, and
    Y is the number of years remaining in the pay-in period.
     
    4) The owner or operator may accelerate payments into the trust fund or may
    deposit the full amount of the current post-closure cost estimate at the time

     
    540
    the fund is established. However, the owner or operator must maintain the
    value of the fund at no less than the value that the fund would have if
    annual payments were made as specified in subsection (a)(3) of this
    Section.
     
    5) If the owner or operator establishes a post-closure trust fund after having
    used one or more alternate mechanisms specified in this Section, the
    owner or operator’s first payment must be in at least the amount that the
    fund would contain if the trust fund were established initially and annual
    payments made as specified in subsection (a)(3) of this Section.
     
    6) After the pay-in period is completed, whenever the current post-closure
    cost estimate changes during the operating life of the facility, the owner or
    operator must compare the new estimate with the trustee’s most recent
    annual valuation of the trust fund. If the value of the fund is less than the
    amount of the new estimate, the owner or operator, within 60 days after
    the change in the cost estimate, must either deposit an amount into the
    fund so that its value after this deposit at least equals the amount of the
    current post-closure cost estimate, or obtain other financial assurance as
    specified in this Section to cover the difference.
     
    7) During the operating life of the facility, if the value of the trust fund is
    greater than the total amount of the current post-closure cost estimate, the
    owner or operator may submit a written request to the Agency for release
    of the amount in excess of the current post-closure cost estimate.
     
    8) If an owner or operator substitutes other financial assurance as specified in
    this Section for all or part of the trust fund, owner or operator may submit
    a written request to the Agency for release of the amount in excess of the
    current post-closure cost estimate covered by the trust fund.
     
    9) Within 60 days after receiving a request from the owner or operator for
    release of funds as specified in subsection (a)(7) or (a)(8) of this Section,
    the Agency must instruct the trustee to release to the owner or operator
    such funds as the Agency specifies in writing.
     
    10) During the period of post-closure care, the Agency must approve a release
    of funds if the owner or operator demonstrates to the Agency that the
    value of the trust fund exceeds the remaining cost of post-closure care.
     
    11) An owner or operator or any other person authorized to perform post-
    closure care may request reimbursement for post-closure care
    expenditures by submitting itemized bills to the Agency. Within 60 days
    after receiving bills for post-closure activities, the Agency must instruct
    the trustee to make reimbursement in those amounts as the Agency
    specifies in writing if the Agency determines that the post-closure care

     
    541
    expenditures are in accordance with the approved post-closure plan or
    otherwise justified. If the Agency does not instruct the trustee to make
    such reimbursements, the Agency must provide the owner or operator with
    a detailed written statement of reasons.
     
    12) The Agency must agree to termination of a trust when either of the
    following occurs:
     
    A) An owner or operator substitutes alternate financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (h) of this Section.
     
    b) Surety bond guaranteeing payment into a post-closure trust fund.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining a surety bond that conforms to the requirements of this
    subsection (b) and submitting the bond to the Agency. The surety
    company issuing the bond must, at a minimum, be among those listed as
    acceptable sureties on Federal federal bonds in Circular 570 of the U.S.
    Department of the Treasury.
     
    2) The wording of the surety bond must be as specified in 35 Ill. Adm. Code
    724.251.
     
    3) The owner or operator that uses a surety bond to satisfy the requirements
    of this Section must also establish a standby trust fund. Under the terms
    of the bond, all payments made thereunder will be deposited by the surety
    directly into the standby trust fund in accordance with instructions from
    the Agency. This standby trust fund must meet the requirements specified
    in subsection (a) of this Section, except as follows:
     
    A) An original, signed duplicate of the trust agreement must be
    submitted to the Agency with the surety bond; and
     
    B) Until the standby trust fund is funded pursuant to the requirements
    of this Section, the following are not required by these regulations:
     
    i) Payments into the trust fund, as specified in subsection (a)
    of this Section;
     
    ii) Updating of Schedule A of the trust agreement (as specified
    in 35 Ill. Adm. Code 724.251) to show current post-closure
    cost estimates;
     

     
    542
    iii) Annual valuations, as required by the trust agreement; and
     
    iv) Notices of nonpayment, as required by the trust agreement.
     
    4) The bond must guarantee that the owner or operator will perform the
    following acts:
     
    A) Fund the standby trust fund in an amount equal to the penal sum of
    the bond before the beginning of final closure of the facility; or
     
    B) Fund the standby trust fund in an amount equal to the penal sum
    within 15 days after an order to begin closure is issued by the
    Board or a court of competent jurisdiction; or
     
    C) Provide alternate financial assurance, as specified in this Section,
    and obtain the Agency’s written approval of the assurance
    provided, within 90 days after receipt by both the owner or
    operator and the Agency of a notice of cancellation of the bond
    from the surety.
     
    5) Under the terms of the bond, the surety will become liable on the bond
    obligation when the owner or operator fails to perform as guaranteed by
    the bond.
     
    6) The penal sum of the bond must be in an amount at least equal to the
    current post-closure cost estimate, except as provided in subsection (f) of
    this Section.
     
    7) Whenever the current post-closure cost estimate increases to an amount
    greater than the penal sum, the owner or operator, within 60 days after the
    increase, must either cause the penal sum to be increased to an amount at
    least equal to the current post-closure cost estimate and submit evidence
    of such increase to the Agency or obtain other financial assurance as
    specified in this Section to cover the increase. Whenever the current post-
    closure cost estimate decreases, the penal sum may be reduced to the
    amount of the current post-closure cost estimate following written
    approval by the Agency.
     
    8) Under the terms of the bond, the surety may cancel the bond by sending
    notice of cancellation by certified mail to the owner or operator and to the
    Agency. Cancellation may not occur, however, during the 120 days
    beginning on the date of receipt of the notice of cancellation by both the
    owner or operator and the Agency, as evidenced by the return receipts.
     
    9) The owner or operator may cancel the bond if the Agency has given prior
    written consent based on its receipt of evidence of alternate financial

     
    543
    assurance as specified in this Section.
     
    c) Post-closure letter of credit.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining an irrevocable standby letter of credit that conforms to the
    requirements of this subsection (c) and submitting the letter to the Agency.
    The issuing institution must be an entity that has the authority to issue
    letters of credit and whose letter-of-credit operations are regulated and
    examined by a federal or State agency.
     
    2) The wording of the letter of credit must be as specified in 35 Ill. Adm.
    Code 724.251.
     
    3) An owner or operator that uses a letter of credit to satisfy the requirements
    of this Section must also establish a standby trust fund. Under the terms
    of the letter of credit, all amounts paid pursuant to a draft by the Agency
    must be deposited by the issuing institution directly into the standby trust
    fund in accordance with instructions from the Agency. This standby trust
    fund must meet the requirements of the trust fund specified in subsection
    (a) of this Section, except as follows:
     
    A) An original, signed duplicate of the trust agreement must be
    submitted to the Agency with the letter of credit; and
     
    B) Unless the standby trust fund is funded pursuant to the
    requirements of this Section, the following are not required by
    these regulations:
     
    i) Payments into the trust fund, as specified in subsection (a)
    of this Section;
     
    ii) Updating of Schedule A of the trust agreement (as specified
    in 35 Ill. Adm. Code 724.151) to show current post-closure
    cost estimates;
     
    iii) Annual valuations, as required by the trust agreement; and
     
    iv) Notices of nonpayment, as required by the trust agreement.
     
    4) The letter of credit must be accompanied by a letter from the owner or
    operator referring to the letter of credit by number, issuing institution, and
    date and providing the following information: the USEPA identification
    number, name, and address of the facility, and the amount of funds
    assured for post-closure care of the facility by the letter of credit.
     

     
    544
    5) The letter of credit must be irrevocable and issued for a period of at least
    one year. The letter of credit must provide that the expiration date will be
    automatically extended for a period of at least one year unless, at least 120
    days before the current expiration date, the issuing institution notifies both
    the owner or operator and the Agency by certified mail of a decision not to
    extend the expiration date. Under the terms of the letter of credit, the 120
    days will begin on the date when both the owner or operator and the
    Agency have received the notice, as evidenced by the return receipts.
     
    6) The letter of credit must be issued in an amount at least equal to the
    current post-closure cost estimate, except as provided in subsection (f) of
    this Section.
     
    7) Whenever the current post-closure cost estimate increases to an amount
    greater than the amount of the credit during the operating life of the
    facility, the owner or operator, within 60 days after the increase, must
    either cause the amount of the credit to be increased so that it at least
    equals the current post-closure cost estimate and submit evidence of such
    increase to the Agency, or obtain other financial assurance, as specified in
    this Section, to cover the increase. Whenever the current cost estimate
    decreases during the operating life of the facility, the amount of the credit
    may be reduced to the amount of the current post-closure cost estimate
    following written approval by the Agency.
     
    8) During the period of post-closure care, the Agency must approve a
    decrease in the amount of the letter of credit if the owner or operator
    demonstrates to the Agency that the amount exceeds the remaining cost of
    post-closure care.
     
    9) Following a final judicial determination or Board order finding that the
    owner or operator has failed to perform post-closure care in accordance
    with the approved post-closure plan and other interim status requirements,
    the Agency may draw on the letter of credit.
     
    10) If the owner or operator does not establish alternate financial assurance, as
    specified in this Section, and obtain written approval of such alternate
    assurance from the Agency within 90 days after receipt by both the owner
    or operator and the Agency of a notice from the issuing institution that it
    has decided not to extend the letter of credit beyond the current expiration
    date, the Agency must draw on the letter of credit. The Agency may delay
    the drawing if the issuing institution grants an extension of the term of the
    credit. During the last 30 days after any such extension the Agency must
    draw on the letter of credit if the owner or operator has failed to provide
    alternate financial assurance, as specified in this Section, and obtain
    written approval of such assurance from the Agency.
     

     
    545
    11) The Agency must return the letter of credit to the issuing institution for
    termination when either of the following occurs:
     
    A) An owner or operator substitutes alternate financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (h) of this Section.
     
    d) Post-closure insurance.
     
    1) An owner or operator may satisfy the requirements of this Section by
    obtaining post-closure insurance that conforms to the requirements of this
    subsection and submitting a certificate of such insurance to the Agency.
    At a minimum, the insurer must be licensed to transact the business of
    insurance, or eligible to provide insurance as an excess or surplus lines
    insurer, in one or more states.
     
    2) The wording of the certificate of insurance must be as specified in 35 Ill.
    Adm. Code 724.251.
     
    3) The post-closure insurance policy must be issued for a face amount at
    least equal to the current post-closure estimate, except as provided in
    subsection (f) of this Section. The term “face amount” means the total
    amount the insurer is obligated to pay under the policy. Actual payments
    by the insurer’s will not change the face amount, although the insurer’s
    future liability will be lowered by the amount of the payments.
     
    4) The post-closure insurance policy must guarantee that funds will be
    available to provide post-closure care of facility whenever the post-closure
    period begins. The policy must also guarantee that, once post-closure care
    begins, the insurer will be responsible for paying out funds, up to an
    amount equal to the face amount of the policy, upon the direction of the
    Agency, to such party or parties as the Agency specifies.
     
    5) An owner or operator or any other person authorized to perform post-
    closure care may request reimbursement for post-closure care
    expenditures by submitting itemized bills to the Agency. Within 60 days
    after receiving bills for post-closure activities, the Agency must instruct
    the insurer to make reimbursement in such amounts as the Agency
    specifies in writing, if the Agency determines that the post-closure care
    expenditures are in accordance with the approved post-closure plan or
    otherwise justified. If the Agency does not instruct the insurer to make
    such reimbursements, the Agency must provide the owner or operator with
    a detailed written statement of reasons.
     

     
    546
    6) The owner or operator must maintain the policy in full force and effect
    until the Agency consents to termination of the policy by the owner or
    operator, as specified in subsection (d)(11) of this Section. Failure to pay
    the premium, without substitution of alternate financial assurance, as
    specified in this Section, will constitute a significant violation of these
    regulations, warranting such remedy as the Board may impose pursuant to
    the Environmental Protection Act. Such violation will be deemed to begin
    upon receipt by the Agency of a notice of future cancellation, termination,
    or failure to renew due to nonpayment of the premium, rather than upon
    the date of expiration.
     
    7) Each policy must contain a provision allowing assignment of the policy to
    a successor owner or operator. Such assignment may be conditional upon
    consent of the insurer, provided such consent is not unreasonably refused.
     
    8) The policy must provide that the insurer may not cancel, terminate, or fail
    to renew the policy except for failure to pay the premium. The automatic
    renewal of the policy must, at a minimum, provide the insured with the
    option of renewal at the face amount of the expiring policy. If there is a
    failure to pay the premium, the insurer may elect to cancel, terminate, or
    fail to renew the policy by sending notice by certified mail to the owner or
    operator and the Agency. Cancellation, termination, or failure to renew
    may not occur, however, during the 120 days beginning with the date of
    receipt of the notice by both the Agency and the owner or operator, as
    evidenced by the return receipts. Cancellation, termination, or failure to
    renew may not occur, and the policy will remain in full force and effect in
    the event that, on or before the date of expiration, one of the following
    occurs:
     
    A) The Agency deems the facility abandoned;
     
    B) Interim status is terminated or revoked;
     
    C) Closure is ordered by the Board or a court of competent
    jurisdiction;
     
    D) The owner or operator is named as debtor in a voluntary or
    involuntary proceeding under 11 USC (Bankruptcy); or
     
    E) The premium due is paid.
     
    9) Whenever the current post-closure cost estimate increases to an amount
    greater than the face amount of the policy during the operating life of the
    facility, the owner or operator, within 60 days after the increase, must
    either cause the face amount to be increased to an amount at least equal to
    the current post-closure cost estimate and submit evidence of such

     
    547
    increase to the Agency, or obtain other financial assurance, as specified in
    this Section, to cover the increase. Whenever the current post-closure cost
    estimate decreases during the operating life of the facility, the face amount
    may be reduced to the amount of the current post-closure cost estimate
    following written approval by the Agency.
     
    10) Commencing on the date that liability to make payments pursuant to the
    policy accrues, the insurer must thereafter annually increase the face
    amount of the policy. Such increase must be equivalent to the face
    amount of the policy, less any payments made, multiplied by an amount
    equivalent to 85 percent of the most recent investment rate or of the
    equivalent coupon-issue yield announced by the U.S. Treasury for 26-
    week Treasury securities.
     
    11) The Agency must give written consent to the owner or operator that the
    owner or operator may terminate the insurance policy when either of the
    following occurs:
     
    A) An owner or operator substitutes alternate financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (h) of this Section.
     
    e) Financial test and corporate guarantee for post-closure care.
     
    1) An owner or operator may satisfy the requirements of this Section by
    demonstrating that the owner or operator passes a financial test, as
    specified in this subsection (e). To pass this test the owner or operator
    must meet the criteria of either subsection (e)(1)(A) or (e)(1)(B) of this
    Section:
     
    A) The owner or operator must have each of the following:
     
    i) Two of the following three ratios: a ratio of total liabilities
    to net worth less than 2.0; a ratio of the sum of net income
    plus depreciation, depletion and amortization to total
    liabilities greater than 0.1; and a ratio of current assets to
    current liabilities greater than 1.5;
     
    ii) Net working capital and tangible net worth each at least six
    times the sum of the current closure and post-closure cost
    estimates and the current plugging and abandonment cost
    estimates;
     
    iii) Tangible new worth of at least $10 million; and

     
    548
     
    iv) Assets in the United States amounting to at least 90 percent
    of total assets or at least six times the sum of the current
    closure and post-closure cost estimates and the plugging
    and abandonment cost estimates.
     
    B) The owner or operator must have each of the following:
     
    i) A current rating for its most recent bond issuance of AAA,
    AA, A, or BBB, as issued by Standard and Poor’s, or Aaa,
    Aa, A, or Baa, as issued by Moody’s;
     
    ii) Tangible net worth at least six times the sum of the current
    closure and post-closure cost estimates and the current
    plugging and abandonment cost estimates;
     
    iii) Tangible net worth of at least $10 million; and
     
    iv) Assets located in the United States amounting to at least 90
    percent of its total assets or at least six times the sum of the
    current closure and post-closure cost estimates and the
    current plugging and abandonment cost estimates.
     
    2) The phrase “current closure and post-closure cost estimates,” as used in
    subsection (e)(1) of this Section, refers to the cost estimates required to be
    shown in subsections 1 through 4 of the letter from the owner’s or
    operator’s chief financial officer (40 CFR 264.151(f)) (incorporated by
    reference in see 35 Ill. Adm. Code 724.251). The phrases “current
    plugging and abandonment cost estimates,” as used in subsection (e)(1) of
    this Section, refers to the cost estimates required to be shown in
    subsections 1 through 4 of the letter from the owner’s or operator’s chief
    financial officer 40 CFR 144.70(f)), incorporated by reference in (see 35
    Ill. Adm. Code 704.240).
     
    3) To demonstrate that it meets this test, the owner or operator must submit
    each of the following items to the Agency:
     
    A) A letter signed by the owner’s or operator’s chief financial officer
    and worded as specified in 35 Ill. Adm. Code 724.251;
     
    B) A copy of the independent certified public accountant’s report on
    examination of the owner’s or operator’s financial statements for
    the latest completed fiscal year; and
     
    C) A special report from the owner’s or operator’s independent
    certified public accountant to the owner or operator stating both of

     
    549
    the following:
     
    i) That the accountant has compared the data that the letter
    from the chief financial officer specifies as having been
    derived from the independently audited, year-end financial
    statements for the latest fiscal year with the amounts in
    such financial statements; and
     
    ii) In connection with that procedure, that no matters came to
    the accountant’s attention that caused the accountant to
    believe that the specified data should be adjusted.
     
    4) This subsection (e)(4) corresponds with 40 CFR 265.143(e)(4), a federal
    provision relating to an extension of the time to file the proofs of financial
    assurance required by this subsection (e) granted by USEPA. This
    statement maintains structural consistency with the corresponding federal
    regulations.
     
    5) After the initial submission of items specified in subsection (e)(3) of this
    Section, the owner or operator must send updated information to the
    Agency within 90 days after the close of each succeeding fiscal year. This
    information must consist of all three items specified in subsection (e)(3) of
    this Section.
     
    6) If the owner or operator no longer meets the requirements of subsection
    (e)(1) of this Section, the owner or operator must send notice to the
    Agency of intent to establish alternate financial assurance, as specified in
    this Section. The notice must be sent by certified mail within 90 days
    after the end of the fiscal year for which the year-end financial data show
    that the owner or operator no longer meets the requirements. The owner
    or operator must provide the alternate financial assurance within 120 days
    after the end of such fiscal year.
     
    7) The Agency may, based on a reasonable belief that the owner or operator
    may no longer meet the requirements of subsection (e)(1) of this Section,
    require reports of financial condition at any time from the owner or
    operator in addition to those specified in subsection (e)(3) of this Section.
    If the Agency finds, on the basis of such reports or other information, that
    the owner or operator no longer meets the requirements of subsection
    (e)(1) of this Section, the owner or operator must provide alternate
    financial assurance, as specified in this Section, within 30 days after
    notification of such a finding.
     
    8) The Agency may disallow use of this test on the basis of qualifications in
    the opinion expressed by the independent certified public accountant in
    the accountant’s report on examination of the owner’s or operator’s

     
    550
    financial statements (see subsection (e)(3)(B) of this Section). An adverse
    opinion or a disclaimer of opinion will be cause for disallowance. The
    Agency must evaluate other qualifications on an individual basis. The
    owner or operator must provide alternate financial assurance, as specified
    in this Section, within 30 days after notification of the disallowance.
     
    9) During the period of post-closure care, the Agency must approve a
    decrease in the current post-closure cost estimate for which this test
    demonstrates financial assurance if the owner or operator demonstrates to
    the Agency that the amount of the cost estimate exceeds the remaining
    cost of post-closure care.
     
    10) The owner or operator is no longer required to submit the items specified
    in subsection (e)(3) of this Section when either of the following occurs:
     
    A) An owner or operator substitutes alternate financial assurance, as
    specified in this Section; or
     
    B) The Agency releases the owner or operator from the requirements
    of this Section in accordance with subsection (h) of this Section.
     
    11) An owner or operator may meet the requirements of this Section by
    obtaining a written guarantee, hereafter referred to as “corporate
    guarantee.” The guarantor must be the direct or higher-tier parent
    corporation of the owner or operator, a firm whose parent corporation is
    also the parent corporation of the owner or operator, or a firm with a
    “substantial business relationship” with the owner or operator. The
    guarantor must meet the requirements for owners or operators in
    subsections (e)(1) through (e)(9) of this Section, and must comply with the
    terms of the corporate guarantee. The wording of the corporate guarantee
    must be identical to the wording specified in 35 Ill. Adm. Code 724.251.
    The corporate guarantee must accompany the items sent to the Agency as
    specified in subsection (e)(3) of this Section. One of these items must be
    the letter from the guarantor’s chief financial officer. If the guarantor’s
    parent corporation is also the parent corporation of the owner or operator,
    the letter must describe the value received in consideration of the
    guarantee. If the guarantor is a firm with a “substantial business
    relationship” with the owner or operator, this letter must describe this
    substantial business relationship” and the value received in consideration
    of the guarantee. The terms of the corporate guarantee must provide as
    follows:
     
    A) That, if the owner or operator fails to perform post-closure care of
    a facility covered by the corporate guarantee in accordance with
    the post-closure plan and other interim status requirements
    whenever required to do so, the guarantor will do so or establish a

     
    551
    trust fund as specified in subsection (a) of this Section, in the name
    of the owner or operator.
     
    B) That the corporate guarantee will remain in force unless the
    guarantor sends notice of cancellation by certified mail to the
    owner or operator and to the Agency. Cancellation may not occur,
    however, during the 120 days beginning on the date of receipt of
    the notice of cancellation by both the owner or operator and the
    Agency, as evidenced by the return receipts.
     
    C) That, if the owner or operator fails to provide alternate financial
    assurance, as specified in this Section, and obtain the written
    approval of such alternate assurance from the Agency within 90
    days after receipt by both the owner or operator and the Agency of
    a notice of cancellation of the corporate guarantee from the
    guarantor, the guarantor will provide such alternate financial
    assurance in the name of the owner or operator.
     
    f) Use of multiple financial mechanisms. An owner or operator may satisfy the
    requirements of this Section by establishing more than one financial mechanism
    per facility. These mechanisms are limited to trust funds, surety bonds, letters of
    credit, and insurance. The mechanisms must be as specified in subsections (a)
    through (d) of this Section, respectively, except that it is the combination of
    mechanisms, rather than the single mechanism, that must provide financial
    assurance for an amount at least equal to the current post-closure cost estimate. If
    an owner or operator uses a trust fund in combination with a surety bond or a
    letter of credit, it may use the trust fund as the standby trust fund for the other
    mechanisms. A single standby trust fund may be established for two or more
    mechanisms. The Agency may use any or all of the mechanisms to provide for
    post-closure care of the facility.
     
    g) Use of a financial mechanism for multiple facilities. An owner or operator may
    use a financial assurance mechanism specified in this Section to meet the
    requirements of this Section for more than one facility. Evidence of financial
    assurance submitted to the Agency must include a list showing, for each facility,
    the USEPA Identification Number, name, address, and the amount of funds for
    post-closure care assured by the mechanism. The amount of funds available
    through the mechanism must be no less than the sum of funds that would be
    available if a separate mechanism had been established and maintained for each
    facility. The amount of funds available to the Agency must be sufficient to
    provide post-closure care for all of the owner or operator’s facilities. In directing
    funds available through the mechanism for post-closure care of any of the
    facilities covered by the mechanism, the Agency may direct only the amount of
    funds designated for that facility, unless the owner or operator agrees to the use of
    additional funds available under the mechanism.
     

     
    552
    h) Release of the owner or operator from the requirements of this Section. Within
    60 days after receiving certifications from the owner or operator and an
    independent registered professional engineer that the post-closure care period has
    been completed in accordance with the approved post-closure plan, the Agency
    must notify the owner or operator in writing that the owner or operator is no
    longer required by this Section to maintain financial assurance for post-closure
    care of that unit, unless the Agency determines that post-closure care has not been
    in accordance with the approved post-closure plan. The Agency must provide the
    owner or operator a detailed written statement of any such determination that
    post-closure care has not been in accordance with the approved post-closure plan.
     
    i) Appeal. The following Agency actions are deemed to be permit modifications or
    refusals to modify for purposes of appeal to the Board (35 Ill. Adm. Code
    702.184(e)(3)):
     
    1) An increase in, or a refusal to decrease the amount of, a bond, letter of
    credit, or insurance; or
     
    2) Requiring alternate assurance upon a finding that an owner or operator or
    parent corporation no longer meets a financial test.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.248 Incapacity of Owners or Operators, Guarantors, or Financial Institutions
     
    a) An owner or operator must notify the Agency by certified mail of the
    commencement of a voluntary or involuntary proceeding under 11 USC
    (Bankruptcy) naming the owner or operator as debtor, within 10 days after
    commencement of the proceeding. A guarantor of a corporate guarantee as
    specified in Sections 725.243(e) and 725.245(e) must make such a notification if
    the guarantor is named as a debtor, as required under the terms of the corporate
    guarantee (see 35 Ill. Adm. Code 724.251).
     
    b) An owner or operator that fulfills the requirements of Sections 725.243, 725.245
    or 725.247 by obtaining a trust fund, surety bond, letter of credit, or insurance
    policy will be deemed to be without the required financial assurance or liability
    coverage in the event of bankruptcy of the trustee or issuing institution, or a
    suspension or revocation of the authority of the trustee institution to act as trustee
    or of the institution issuing the surety bond, letter of credit, or insurance policy to
    issue such instruments. The owner or operator must establish other financial
    assurance or liability coverage within 60 days after such an event.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    553
    SUBPART I: USE AND MANAGEMENT OF CONTAINERS
     
    Section 725.273 Management of Containers
     
    a) A container holding hazardous waste must always be closed during storage,
    except when it is necessary to add or remove waste.
     
    b) A container holding hazardous waste must not be opened, handled, or stored in a
    manner that may rupture the container or cause it to leak.
     
    BOARD NOTE: Re-use of containers in transportation is governed by U.S. Department of
    Transportation USDOT regulations, including those set forth in 49 CFR 173.28 (Reuse,
    Reconditioning, and Remanufacture of Packagings), incorporated by reference in 35 Ill. Adm.
    Code 720.111(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.277 Special Requirements for Incompatible Wastes
     
    a) Incompatible wastes or incompatible wastes and materials (see Appendix
    appendix V of 40 CFR 265 (Examples of Potentially Incompatible Waste),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b), for examples) must
    not be placed in the same container, unless Section 725.117(b) is complied with.
     
    b) Hazardous waste must not be placed in an unwashed container that previously
    held an incompatible waste or material (see Appendix appendix V of 40 CFR 265,
    incorporated by reference in 35 Ill. Adm. Code 720.111(b), for examples), unless
    Section 725.117(b) is complied with.
     
    c) A storage container holding a hazardous waste that is incompatible with any
    waste or other materials stored nearby in other containers, piles, open tanks, or
    surface impoundments must be separated from the other materials or protected
    from them by means of a dike, berm, wall, or other device.
     
    BOARD NOTE: The purpose of this is to prevent fires, explosions, gaseous emissions, leaching,
    or other discharge or hazardous waste or hazardous waste constituents that could result from the
    mixing of incompatible wastes or materials if containers break or leak.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART J: TANK SYSTEMS
     
    Section 725.290 Applicability
     
    The regulations of this Subpart J apply to owners and operators of facilities that use tank systems
    for storing or treating hazardous waste, except as otherwise provided in subsections (a), (b), or

     
    554
    (c) of this Section or in Section 725.101.
     
    a) Tank systems that are used to store or treat hazardous waste that contains no free
    liquids and that are situated inside a building with an impermeable floor are
    exempted from the requirements in Section 725.293. To demonstrate the absence
    or presence of free liquids in the stored or treated waste, the following test must
    be used: USEPA Method 9095 9095B (Paint Filter Liquids Test), as described in
    “Test Methods for Evaluating Solid Wastes, Physical/Chemical Methods,”
    USEPA Publication No. publication number EPA-530/SW-846), incorporated by
    reference in 35 Ill. Adm. Code 720.111(a).
     
    b) Tank systems, including sumps, as defined in 35 Ill. Adm. Code 720.110, that
    serve as part of a secondary containment system to collect or contain releases of
    hazardous wastes are exempted from the requirements in Section 725.293(a).
     
    c) Tanks, sumps, and other collection devices used in conjunction with drip pads, as
    defined in 35 Ill. Adm. Code 720.110 and regulated under Subpart W of this Part,
    must meet the requirements of this Subpart J.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.291 Assessment of Existing Tank System Integrity
     
    a) For each existing tank system that does not have secondary containment meeting
    the requirements of Section 725.293, the owner or operator must determine either
    that the tank system is not leaking or that it is unfit for use. Except as provided in
    subsection (c), the owner or operator shall, after January 12, 1988, obtain and
    keep on file at the facility a written assessment reviewed and certified by an
    independent, qualified, registered professional engineer in accordance with 35 Ill.
    Adm. Code 702.126(d), that attests to the tank system’s integrity.
     
    b) This assessment must determine whether the tank system is adequately designed
    and has sufficient structural strength and compatibility with the wastes to be
    stored or treated to ensure that it will not collapse, rupture, or fail. At a minimum,
    this assessment must consider the following:
     
    1) Design standards, if available, according to which the tank and ancillary
    equipment were constructed;
     
    2) Hazardous characteristics of the wastes that have been or will be handled;
     
    3) Existing corrosion protection measures;
     
    4) Documented age of the tank system, if available, (otherwise, an estimate
    of the age); and
     

     
    555
    5) Results of a leak test, internal inspection, or other tank integrity
    examination, such that the following conditions are met:
     
    A) For non-enterable underground tanks, this assessment must consist
    of a leak test that is capable of taking into account the effects of
    temperature variations, tank end deflection, vapor pocket, and high
    water table effects.
     
    B) For other than non-enterable underground tanks and for ancillary
    equipment, this assessment must be either a leak test, as described
    above, or an internal inspection or other tank integrity examination
    certified by an independent, qualified, registered professional
    engineer in accordance with 35 Ill. Adm. Code 702.126(d), that
    addresses cracks, leaks, corrosion, and erosion.
     
    BOARD NOTE: The practices described in the American Petroleum
    Institute (API) Publication, “Guide for Inspection of Refinery
    Equipment,” Chapter XIII, “Atmospheric and Low-Pressure Storage
    Tanks,” incorporated by reference in 35 Ill. Adm. Code 720.111(a), may
    be used, where applicable, as guidelines in conducting the integrity
    examination of an other than non-enterable underground tank system.
     
    c) Tank systems that store or treat materials that become hazardous wastes
    subsequent to July 14, 1986 must conduct this assessment within 12 months after
    the date that the waste becomes a hazardous waste.
     
    d) If, as a result of the assessment conducted in accordance with subsection (a) of
    this Section, a tank system is found to be leaking or unfit for use, the owner or
    operator must comply with the requirements of Sections 725.296.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.292 Design and Installation of New Tank Systems or Components
     
    a) An owner or operator of a new tank system or component must ensure that the
    foundation, structural support, seams, connections, and pressure controls (if
    applicable) are adequately designed and that the tank system has sufficient
    structural strength, compatibility with the wastes to be stored or treated, and
    corrosion protection so that it will not collapse, rupture, or fail. The owner or
    operator must obtain a written assessment reviewed and certified by an
    independent, qualified, registered professional engineer in accordance with 35 Ill.
    Adm. Code 702.126(d), attesting that the system has sufficient structural integrity
    and is acceptable for the storing and treating of hazardous waste. This assessment
    must include, at a minimum, the following information:
     
    1) Design standards according to which the tanks and ancillary equipment is

     
    556
    or will be constructed.
     
    2) Hazardous characteristics of the wastes to be handled.
     
    3) For new tank systems or components in which the external shell of a metal
    tank or any external metal component of the tank system is or will be in
    contact with the soil or with water, a determination by a corrosion expert
    of the following:
     
    A) Factors affecting the potential for corrosion, including but not
    limited to the following:
     
    i) Soil moisture content;
     
    ii) Soil pH;
     
    iii) Soil sulfides level;
     
    iv) Soil resistivity;
     
    v) Structure to soil potential;
     
    vi) Influence of nearby underground metal structures (e.g.,
    piping);
     
    vii) Stray electric current;
     
    viii) Existing corrosion-protection measures (e.g., coating,
    cathodic protection, etc.); and
     
    B) The type and degree of external corrosion protection that are
    needed to ensure the integrity of the tank system during the use of
    the tank system or component, consisting of one or more of the
    following:
     
    i) Corrosion-resistant materials of construction such as
    special alloys, or fiberglass-reinforced plastic;
     
    ii) Corrosion-resistant coating (such as epoxy, fiberglass, etc.)
    with cathodic protection (e.g., impressed current or
    sacrificial anodes); and
     
    iii) Electrical isolation devices such as insulating joints and
    flanges, etc.
     
    BOARD NOTE: The practices described in the National

     
    557
    Association of Corrosion Engineers (NACE) Standard. ,
    “Recommended Practice (RP-02-85) “Control of External
    Corrosion on Metallic Buried, Partially Buried, or Submerged
    Liquid Storage Systems,” NACE Recommended Practice RP0285,
    and API Publication 1632, “Cathodic Protection of Underground
    Petroleum Storage Tanks and Piping Systems,” API
    Recommended Practice 1632, each incorporated by reference in 35
    Ill. Adm. Code 720.111(a), may be used, where applicable, as
    guidelines in providing corrosion protection for tank systems.
     
    4) For underground tank system components that are likely to be affected by
    vehicular traffic, a determination of design or operational measures that
    will protect the tank system against potential damage; and
     
    5) Design considerations to ensure the following:
     
    A) Tank foundations will maintain the load of a full tank;
     
    B) Tank systems will be anchored to prevent flotation or
    dislodgement where the tank system is placed in a saturated zone,
    or is located within a seismic fault zone; and
     
    C) Tank systems will withstand the effects of frost heave.
     
    b) The owner and operator of a new tank system must ensure that proper handling
    procedures are adhered to in order to prevent damage to the system during
    installation. Prior to covering, enclosing or placing a new tank system or
    component in use, an independent, qualified installation inspector or an
    independent, qualified, registered professional engineer, either of whom is trained
    and experienced in the proper installation of tank systems or components, must
    inspect the system or component for the presence of any of the following items:
     
    1) Weld breaks;
     
    2) Punctures;
     
    3) Scrapes of protective coatings;
     
    4) Cracks;
     
    5) Corrosion; and
     
    6) Other structural damage or inadequate construction or installation. All
    discrepancies must be remedied before the tank system is covered,
    enclosed, or placed in use.
     

     
    558
    c) New tank systems or components and piping that are placed underground and
    which are backfilled must be provided with a backfill material that is a
    noncorrosive, porous, and homogeneous substance which is carefully installed so
    that the backfill is placed completely around the tank and compacted to ensure
    that the tank and piping are fully and uniformly supported.
     
    d) All new tanks and ancillary equipment must be tested for tightness prior to being
    covered, enclosed or placed in use. If a tank system is found not to be tight, all
    repairs necessary to remedy the leaks in the system must be performed prior to the
    tank system being covered, enclosed, or placed in use.
     
    e) Ancillary equipment must be supported and protected against physical damage
    and excessive stress due to settlement, vibration, expansion, or contraction.
     
    BOARD NOTE: The piping system installation procedures described in API
    Publication 1615, “Installation of Underground Petroleum Storage Systems,” API
    Recommended Practice 1615, or ANSI Standard B31.3, “Chemical Plant and
    Petroleum Refinery Piping,” ASME/ANSI Standard B31.3-1987, as
    supplemented by B31.3a-1988 and B31.3b-1988, each incorporated by reference
    in 35 Ill. Adm. Code 720.111(a), may be used where applicable, as guidelines for
    proper installation of piping systems.
     
    f) The owner and operator must provide the type and degree of corrosion protection
    necessary, based on the information provided under subsection (a)(3) of this
    Section, to ensure the integrity of the tank system during use of the tanks system.
    An independent corrosion expert must supervise the installation of a corrosion
    protection system that is field fabricated to ensure proper installation.
     
    g) The owner and operator must obtain and keep on file at the facility written
    statements by those persons required to certify the design of the tank system and
    supervise the installation of the tank system in accordance with the requirements
    of subsections (b) through (f) of this Section to attest that the tank system was
    properly designed and installed and that repairs, pursuant to subsections (b) and
    (d) of this Section were performed. These written statements must also include
    the certification statement, as required in 35 Ill. Adm. Code 702.126(d).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.293 Containment and Detection of Releases
     
    a) In order to prevent the release of hazardous waste or hazardous constituents to the
    environment, secondary containment that meets the requirements of this Section
    must be provided (except as provided in subsections (f) and (g) of this Section).
     
    1) For a new tank system or component, prior to its being put into service;
     

     
    559
    2) For all existing tanks used to store or treat USEPA Hazardous Waste
    Numbers F020, F021, F022, F023, F026, and F027, as defined in 35 Ill.
    Adm. Code 721.131, within two years after January 12, 1987;
     
    3) For those existing tank systems of known and documentable age, within
    two years after January 12, 1987, or when the tank systems have reached
    15 years of age, whichever come later;
     
    4) For those existing tank systems for which the age cannot be documented,
    within eight years of January 12, 1987; but if the age of the facility is
    greater than seven years, secondary containment must be provided by the
    time the facility reaches 15 years of age or within two years of January 12,
    1987, whichever comes later; and
     
    5) For tank systems that store or treat materials that become hazardous
    wastes subsequent to January 12, 1987, within the time intervals required
    in subsections (a)(1) through (a)(4) of this Section, except that the date
    that a material becomes a hazardous waste must be used in place of
    January 12, 1987.
     
    b) Secondary containment systems must be as follows:
     
    1) Designed, installed, and operated to prevent any migration of wastes or
    accumulated liquid out of the system to the soil, groundwater, or surface
    water at any time during the use of the tank system; and
     
    2) Capable of detecting and collecting releases and accumulated liquids until
    the collected material is removed.
     
    c) To meet the requirements of subsection (b) of this Section, secondary
    containment systems must be at a minimum as follows:
     
    1) Constructed of or lined with materials that are compatible with the wastes
    to be placed in the tank system and of sufficient strength and thickness to
    prevent failure due to pressure gradients (including static head and
    external hydrological forces), physical contact with the waste to which
    they are exposed, climatic conditions, the stress of installation, and the
    stress of daily operation (including stresses from nearby vehicular traffic);
     
    2) Placed on a foundation or base capable of providing support to the
    secondary containment system and resistance to pressure gradients above
    and below the system and capable of preventing failure due to settlement,
    compression, or uplift;
     
    3) Provided with a leak detection system that is designed and operated so that
    it will detect the failure of either the primary and secondary containment

     
    560
    structure or any release of hazardous waste or accumulated liquid in the
    secondary containment system within 24 hours, or as otherwise provided
    in the RCRA permit if the operator has demonstrated to the Agency, by
    way of permit application, that the existing detection technology or site
    conditions will not allow detection of a release within 24 hours;
     
    4) Sloped or otherwise designed or operated to drain and remove liquids
    resulting from leaks, spills, or precipitation. Spilled or leaked waste and
    accumulated precipitation must be removed from the secondary
    containment system within 24 hours, or as otherwise provided in the
    RCRA permit if the operator has demonstrated to the Agency, by way of
    permit application, that removal of the released waste or accumulated
    precipitation cannot be accomplished within 24 hours.
     
    BOARD NOTE: If the collected material is a hazardous waste under 35 Ill. Adm.
    Code 721, it is subject to management as a hazardous waste in accordance with all
    applicable requirements of 35 Ill. Adm. Code 722 through 725. If the collected
    material is discharged through a point source to waters of the State, it is subject to
    the NPDES permit requirement of Section 12(f) of the Environmental Protection
    Act and 35 Ill. Adm. Code 309. If discharged to a Publicly Owned Treatment
    Works (POTW), it is subject to the requirements of 35 Ill. Adm. Code 307 and
    310. If the collected material is released to the environment, it may be subject to
    the reporting requirements of 35 Ill. Adm. Code 750.410 and federal 40 CFR
    302.6, incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    d) Secondary containment for tanks must include one or more of the following
    devices:
     
    1) A liner (external to the tank);
     
    2) A vault;
     
    3) A double-walled tank; or
     
    4) An equivalent device as approved by the Board in an adjusted standards
    proceeding.
     
    e) In addition to the requirements of subsections (b), (c), and (d), secondary
    containment systems must satisfy the following requirements:
     
    1) External liner systems must be as follows:
     
    A) Designed or operated to contain 100 percent of the capacity of the
    largest tank within the liner system’s boundary;
     
    B) Designed or operated to prevent run-on or infiltration of

     
    561
    precipitation into the secondary containment system, unless the
    collection system has sufficient excess capacity to contain run-on
    or infiltration. Such additional capacity must be sufficient to
    contain precipitation from a 25-year, 24-hour rainfall event;
     
    C) Free of cracks or gaps; and
     
    D) Designed and installed to completely surround the tank and to
    cover all surrounding earth likely to come into contact with the
    waste if released from the tanks (i.e., capable of preventing lateral
    as well as vertical migration of the waste).
     
    2) Vault systems must be as follows:
     
    A) Designed or operated to contain 100 percent of the capacity of the
    largest tank within the vault system’s boundary;
     
    B) Designed or operated to prevent run-on or infiltration of
    precipitation into the secondary containment system, unless the
    collection system has sufficient excess capacity to contain run-on
    or infiltration. Such additional capacity must be sufficient to
    contain precipitation from a 25-year, 24-hour rainfall event;
     
    C) Constructed with chemical-resistant water stops in place at all
    joints (if any);
     
    D) Provided with an impermeable interior coating or lining that is
    compatible with the stored waste and that will prevent migration of
    waste into the concrete;
     
    E) Provided with a means to protect against the formation of and
    ignition of vapors within the vault, if the waste being stored or
    treated:
     
    i) Meets the definition of ignitable waste under 35 Ill. Adm.
    Code 721.121; or
     
    ii) Meets the definition of reactive waste under 35 Ill. Adm.
    Code 721.123 and may form an ignitable or explosive
    vapor; and
     
    F) Provided with an exterior moisture barrier or be otherwise
    designed or operated to prevent migration of moisture into the
    vault if the vault is subject to hydraulic pressure.
     
    3) Double-walled tanks must be as follows:

     
    562
     
    A) Designed as an integral structure (i.e., an inner tank within an outer
    shell) so that any release from the inner tank is contained by the
    outer shell;
     
    B) Protected, if constructed of metal, from both corrosion of the
    primary tank interior and the external surface of the outer shell;
    and
     
    C) Provided with a built-in continuous leak detection system capable
    of detecting a release within 24 hours or as otherwise provided in
    the RCRA permit if the operator has demonstrated to the Agency,
    by way of permit application, that the existing leak detection
    technology or site conditions will not allow detection of a release
    within 24 hours.
     
    BOARD NOTE: The provisions outlined in the Steel Tank Institute (STI)
    document, “Standard for Dual Wall Underground Steel Storage Tanks,”
    incorporated by reference in 35 Ill. Adm. Code 720.111(a), may be used
    as guidelines for aspects of the design of underground steel double-walled
    tanks.
     
    f) Ancillary equipment must be provided with full secondary containment (e.g.,
    trench, jacketing, double-walled piping, etc.) that meets the requirements of
    subsections (c) and (h) of this Section, except for the following:
     
    1) Aboveground piping (exclusive of flanges, joints, valves, and
    connections) that are visually inspected for leaks on a daily basis;
     
    2) Welded flanges, welded joints, and welded connections that are visually
    inspected for leaks on a daily basis;
     
    3) Sealless or magnetic coupling pumps and sealless valves that are visually
    inspected for leaks on a daily basis; and
     
    4) Pressurized aboveground piping systems with automatic shut-off devices
    (e.g., excess flow check valves, flow metering shutdown devices, loss of
    pressure actuated shut-off devices, etc.) that are visually inspected for
    leaks on a daily basis.
     
    g) Pursuant to Section 28.1 of the Environmental Protection Act [415 ILCS 5/28.1],
    and in accordance with Subpart D of 35 Ill. Adm. Code 104, an adjusted standard
    will be granted by the Board regarding alternative design and operating practices
    only if the Board finds either that the alternative design and operating practices,
    together with location characteristics, will prevent the migration of any hazardous
    waste or hazardous constituents into the groundwater or surface water at least as

     
    563
    effectively as secondary containment during the active life of the tank system, or
    that in the event of a release that does migrate to groundwater or surface water, no
    substantial present or potential hazard will be posed to human health or the
    environment. New underground tank systems may not receive an adjusted
    standard from the secondary containment requirements of this Section through a
    justification in accordance with subsection (g)(2) of this Section.
     
    1) When determining whether to grant alternative design and operating
    practices based on a demonstration of equivalent protection of
    groundwater and surface water, the Board will consider whether the
    petitioner has justified an adjusted standard based on the following
    factors:
     
    A) The nature and quantity of the waste;
     
    B) The proposed alternate design and operation;
     
    C) The hydrogeologic setting of the facility, including the thickness of
    soils between the tank system and groundwater; and
     
    D) All other factors that would influence the quality and mobility of
    the hazardous constituents and the potential for them to migrate to
    groundwater or surface water.
     
    2) In deciding whether to grant alternative design and operating practices
    based on a demonstration of no substantial present or potential hazard, the
    Board will consider whether the petitioner has justified an adjusted
    standard based on the following factors:
     
    A) The potential adverse effects on groundwater, surface water, and
    land quality taking the following into account:
     
    i) The physical and chemical characteristics of the waste in
    the tank system, including its potential for migration;
     
    ii) The hydrogeological characteristics of the facility and
    surrounding land;
     
    iii) The potential for health risks caused by human exposure to
    waste constituents;
     
    iv) The potential for damage to wildlife; crops, vegetation, and
    physical structures caused by exposure to waste
    constituents; and
     
    v) The persistence and permanence of the potential adverse

     
    564
    effects;
     
    B) The potential adverse effects of a release on groundwater quality,
    taking the following into account:
     
    i) The quantity and quality of groundwater and the direction
    of groundwater flow;
     
    ii) The proximity and withdrawal rates of water in the area;
     
    iii) The current and future uses of groundwater in the area; and
     
    iv) The existing quality of groundwater, including other
    sources of contamination and their cumulative impact on
    the groundwater quality;
     
    C) The potential adverse effects of a release on surface water quality,
    taking the following into account:
     
    i) The quantity and quality of groundwater and the direction
    of groundwater flow;
     
    ii) The patterns of rainfall in the region;
     
    iii) The proximity of the tank system to surface waters;
     
    iv) The current and future uses of surface waters in the area
    and water quality standards established for those surface
    waters; and
     
    v) The existing quality of surface water, including other
    sources of contamination and the cumulative impact on
    surface water quality; and
     
    D) The potential adverse effects of a release on the land surrounding
    the tank system, taking the following into account:
     
    i) The patterns of rainfall in the region; and
     
    ii) The current and future uses of the surrounding land.
     
    3) The owner or operator of a tank system, for which alternative design and
    operating practices had been granted in accordance with the requirements
    of subsection (g)(1), at which a release of hazardous waste has occurred
    from the primary tank system but has not migrated beyond the zone of
    engineering control (as established in the alternative design and operating

     
    565
    practices), must fulfill the following requirements:
     
    A) It must comply with the requirements of Section 725.296, except
    Section 725.296(d); and
     
    B) It must decontaminate or remove contaminated soil to the extent
    necessary to assure the following:
     
    i) It must enable the tank system, for which alternative design
    and operating practices were granted, to resume operation
    with the capability for the detection of and response to
    releases at least equivalent to the capability it had prior to
    the release; and
     
    ii) It must prevent the migration of hazardous waste or
    hazardous constituents to groundwater or surface water.
     
    C) If contaminated soil cannot be removed or decontaminated in
    accordance with subsection (g)(3)(B), it must comply with the
    requirements of Section 725.297(b).
     
    4) The owner or operator of a tank system, for which alternative design and
    operating practices had been granted in accordance with the requirements
    of subsection (g)(1) of this Section, at which a release of hazardous waste
    has occurred from the primary tank system and has migrated beyond the
    zone of engineering control (as established in the alternative design and
    operating practices, must fulfill the following requirements:
     
    A) It must comply with the requirements of Section 725.296(a), (b),
    (c), and (d); and
     
    B) It must prevent the migration of hazardous waste or hazardous
    constituents to groundwater or surface water, if possible, and
    decontaminate or remove contaminated soil. If contaminated soil
    cannot be decontaminated or removed, or if groundwater has been
    contaminated, the owner or operator must comply with the
    requirements of Section 725.297(b);
     
    C) If repairing, replacing, or reinstalling the tank system, it must
    provide secondary containment in accordance with the
    requirements of subsections (a) through (f) of this Section, or make
    the alternative design and operating practices demonstration to the
    Board again with respect to secondary containment and meet the
    requirements for new tank systems in Section 725.292 if the tank
    system is replaced. The owner or operator must comply with these
    requirements even if contaminated soil is decontaminated or

     
    566
    removed, and groundwater or surface water has not been
    contaminated.
     
    h) In order to make an alternative design and operating practices demonstration, the
    owner or operator must follow the following procedures, in addition to those
    specified in Section 28.1 of the Act [415 ILCS 5/28.1] and Subpart D of 35 Ill.
    Adm. Code 104:
     
    1) The owner or operator must file a petition for approval of alternative
    design and operating practices according to the following schedule:
     
    A) For existing tank systems, at least 24 months prior to the date that
    secondary containment must be provided in accordance with
    subsection (a) of this Section; and
     
    B) For new tank systems, at least 30 days prior to entering into a
    contract for installation of the tank system.
     
    2) As part of the petition, the owner or operator must also submit the
    following to the Board:
     
    A) A description of the steps necessary to conduct the demonstration
    and a timetable for completing each of the steps. The
    demonstration must address each of the factors listed in subsection
    (g)(1) or (g)(2) of this Section; and
     
    B) The portion of the Part B permit application specified in 35 Ill.
    Adm. Code 703.202.
     
    3) The owner or operator must complete its showing within 180 days after
    filing its petition for approval of alternative design and operating
    practices.
     
    4) The Agency must issue or modify the RCRA permit so as to require the
    permittee to construct and operate the tank system in the manner that was
    provided in any Board order approving alternative design and operating
    practices.
     
    i) All tank systems, until such time as secondary containment meeting the
    requirements of this Section is provided, must comply with the following:
     
    1) For non-enterable underground tanks, a leak test that meets the
    requirements of Section 725.291(b)(5) must be conducted at least
    annually.
     
    2) For other than non-enterable underground tanks and for all ancillary

     
    567
    equipment, an annual leak test, as described in subsection (i)(1) of this
    Section, or an internal inspection or other tank integrity examination, by
    an independent, qualified, registered professional engineer, that addresses
    cracks, leaks, corrosion and erosion must be conducted at least annually.
    The owner or operator must remove the stored waste from the tank, if
    necessary, to allow the condition of all internal tank surfaces to be
    assessed.
     
    BOARD NOTE: The practices described in API Publication, “Guide for
    Inspection of Refining Refinery Equipment,” Chapter XIII, “Atmospheric
    and Low Pressure Storage Tanks,” incorporated by reference in 35 Ill.
    Adm. Code 720.111(a), may be used, when applicable, as guidelines for
    assessing the overall condition of the tank system.
     
    3) The owner or operator must maintain on file at the facility a record of the
    results of the assessments conducted in accordance with subsections (i)(1)
    through (i)(3) of this Section.
     
    4) If a tank system or component is found to be leaking or unfit for use as a
    result of the leak test or assessment in subsections (i)(1) through (i)(3) of
    this Section, the owner or operator must comply with the requirements of
    Section 725.296.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.295 Inspections
     
    a) The owner or operator must inspect the following, where present, at least once
    each operating day:
     
    1) Overfill/spill control equipment (e.g., waste-feed cutoff systems, bypass
    systems, and drainage systems) to ensure that it is in good working order;
     
    2) The aboveground portion of the tank system, if any, to detect corrosion or
    releases of waste;
     
    3) Data gathered from monitoring equipment (e.g., pressure and temperature
    gauges, monitoring wells, etc.) to ensure that the tank system is being
    operated according to its design; and
     
    4) The construction materials and the area immediately surrounding the
    externally accessible portion of the tank system including secondary
    containment structures (e.g., dikes) to detect erosion or signs of releases of
    hazardous waste (e.g., wet spots, dead vegetation, etc.);
     
    BOARD NOTE: Section 725.115(c) requires the owner or operator to remedy

     
    568
    any deterioration or malfunction the owner or operator finds. Section 725.296
    requires the owner or operator to notify the Agency within 24 hours of confirming
    a release. Also, federal 40 CFR 302, incorporated by reference in 35 Ill. Adm.
    Code 720.111(b), may require the owner or operator to notify the National
    Response Center of a release.
     
    b) The owner or operator must inspect cathodic protection systems, if present,
    according to, at a minimum, the following schedule to ensure that they are
    functioning properly:
     
    1) The proper operation of the cathodic protection system must be confirmed
    within six months after initial installation, and annually thereafter; and
     
    2) All sources of impressed current must be inspected or tested, as
    appropriate, at least every other month.
     
    BOARD NOTE: The practices described in NACE Standard, “Recommended
    Practice (RP-02-85), “Control of External Corrosion on Metallic Buried, Partially
    Buried, or Submerged Liquid Storage Systems,” NACE Recommended Practice
    RP02-85, or API Publication 1632, “Cathodic Protection of Underground
    Petroleum Storage Tanks and Piping Systems,” API Recommended Practice
    1632, each incorporated by reference in 35 Ill. Adm. Code 720.111(a), may be
    used, where applicable, as guidelines in maintaining and inspecting cathodic
    protection systems.
     
    c) The owner or operator must document in the operating record of the facility an
    inspection of those items in subsections (a) and (b) of this Section.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.296 Response to Leaks or Spills and Disposition of Tank Systems
     
    A tank system or secondary containment system from which there has been a leak or spill, or
    which is unfit for use, must be removed from service immediately. The owner or operator must
    satisfy the following requirements:
     
    a) Cease using; prevent flow or addition of wastes. The owner or operator must
    immediately stop the flow of hazardous waste into the tank system or secondary
    containment system and inspect the system to determine the cause of the release.
     
    b) Removal of waste from tank system or secondary containment system.
     
    1) If the release was from the tank system, the owner or operator must,
    within 24 hours after detection of the leak, remove as much of the waste as
    is necessary to prevent further release of hazardous waste to the
    environment and to allow inspection and repair of the tank system to be

     
    569
    performed.
     
    2) If the release was to a secondary containment system, all released
    materials must be removed within 24 hours to prevent harm to human
    health and the environment.
     
    c) Containment of visible releases to the environment. The owner or operator must
    immediately conduct a visual inspection of the release and, based upon that
    inspection, do the following:
     
    1) Prevent further migration of the leak or spill to soils or surface water; and
     
    2) Remove and properly dispose of any visible contamination of the soil or
    surface water.
     
    d) Notifications; reports.
     
    1) Any release to the environment, except as provided in subsection (d)(2) of
    this Section, must be reported to the Agency within 24 hours after
    detection.
     
    2) A leak or spill of hazardous waste is exempted from the requirements of
    this subsection (d) if the following occur:
     
    A) The spill is less than or equal to a quantity of one pound; and
     
    B) The spill is immediately contained and cleaned-up.
     
    3) Within 30 days after detection of a release to the environment, a report
    containing the following information must be submitted to the Agency:
     
    A) Likely route of migration of the release;
     
    B) Characteristics of the surrounding soil (soil composition, geology,
    hydrogeology, climate, etc.);
     
    C) Results of any monitoring or sampling conducted in connection
    with the release (if available). If sampling or monitoring data
    relating to the release are not available within 30 days, these data
    must be submitted to the Agency as soon as they become available;
     
    D) Proximity to downgradient drinking water, surface water, and
    population areas; and
     
    E) Description of response actions taken or planned.
     

     
    570
    e) Provision of secondary containment, repair, or closure.
     
    1) Unless the owner or operator satisfies the requirements of subsections
    (e)(2) through (e)(4) of this Section, the tank system must be closed in
    accordance with Section 725.297.
     
    2) If the cause of the release was a spill that has not damaged the integrity of
    the system, the owner or operator may return the system to service as soon
    as the released waste is removed and repairs, if necessary, are made.
     
    3) If the cause of the release was a leak from the primary tank system into the
    secondary containment system, the system must be repaired prior to
    returning the tank system to service.
     
    4) If the source of the release was a leak to the environment from a
    component of a tank system without secondary containment, the owner or
    operator must provide the component of the system from which the leak
    occurred with secondary containment that satisfies the requirements of
    Section 725.293 before it is returned to service, unless the source of the
    leak is an aboveground portion of a tank system. If the source is an
    aboveground component that can be inspected visually, the component
    must be repaired and may be returned to service without secondary
    containment as long as the requirements of subsection (f) of this Section
    are satisfied. If a component is replaced to comply with the requirements
    of this subsection (e)(4), that component must satisfy the requirements for
    new tank systems or components in Sections 725.292 and 725.293.
    Additionally, if a leak has occurred in any portion of a tank system
    component that is not readily accessible for visual inspection (e.g., the
    bottom of an inground or onground tank), the entire component must be
    provided with secondary containment in accordance with Section 725.293
    prior to being returned to use.
     
    f) Certification of major repairs. If the owner or operator has repaired a tank system
    in accordance with subsection (e) of this Section, and the repair has been
    extensive (e.g., installation of an internal liner, repair of a ruptured primary
    containment or secondary containment vessel, etc.), the tank system must not be
    returned to service unless the owner or operator has obtained a certification by an
    independent qualified, registered professional engineer in accordance with 35 Ill.
    Adm. Code 702.126(d) that the repaired system is capable of handling hazardous
    wastes without release for the intended life of the system. This certification must
    be submitted to the Agency within seven days after returning the tank system to
    use.
     
    BOARD NOTE: See Section 725.115(c) for the requirements necessary to remedy a failure.
    Also, federal 40 CFR 302.6, incorporated by reference in 35 Ill. Adm. Code 720.111(b), requires
    the owner or operator to notify the National Response Center of a release of any “reportable

     
    571
    quantity.”
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.298 Special Requirements for Ignitable or Reactive Wastes
     
    a) Ignitable or reactive waste must not be placed in a tank system, unless either of
    the following conditions is fulfilled:
     
    1) The waste is treated, rendered or mixed before or immediately after
    placement in the tank system so that the following two conditions are
    fulfilled:
     
    A) The resulting waste, mixture, or dissolved material no longer meets
    the definition of ignitable or reactive waste under 35 Ill. Adm.
    Code 721.121 or 721.123; and
     
    B) Section 725.117(b) is complied with;
     
    2) The waste is stored or treated in such a way that it is protected from any
    material or conditions that may cause the waste to ignite or react; or
     
    3) The tank system is used solely for emergencies.
     
    b) The owner or operator of a facility where ignitable or reactive waste is stored or
    tested in tanks must comply with the requirements for the maintenance of
    protective distances between the waste management area and any public ways,
    streets, alleys, or an adjoining property line that can be built upon as required in
    Tables 2-1 through 2-6 of the National Fire Protection Association’s “Flammable
    and Combustible Liquids Code,” NFPA 30, incorporated by reference in 35 Ill.
    Adm. Code 720.111(a).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.301 Generators of 100 to 1,000 Kilograms of Hazardous Waste Per Month
     
    a) The requirements of this Section apply to small quantity generators that generate
    more than 100 kg but less than 1,000 kg of hazardous waste in a calendar month,
    that accumulate hazardous waste in tanks for less than 180 days (or 270 days if
    the generator must ship the waste greater than 200 miles), and that do not
    accumulate over 6,000 kg on-site at any time.
     
    b) A generator of between 100 and 1,000 kg/mo hazardous waste must comply with
    the following general operating requirements:
     
    1) Treatment or storage of hazardous waste in tanks must comply with

     
    572
    Section 725.117(b);
     
    2) Hazardous wastes or treatment reagents must not be placed in a tank if
    they could cause the tank or its inner liner to rupture, leak, corrode, or
    otherwise fail before the end of its intended life;
     
    3) Uncovered tanks must be operated to ensure at least 60 centimeters (2
    feet) of freeboard unless the tank is equipped with a containment structure
    (e.g., dike or trench), a drainage control system, or a diversion structure
    (e.g., standby tank) with a capacity that equals or exceeds the volume of
    the top 60 centimeters (2 feet) of the tank; and
     
    4) Where hazardous waste is continuously fed into a tank, the tank must be
    equipped with a means to stop this inflow (e.g., waste feed cutoff system
    or by-pass system to a stand-by tank).
     
    BOARD NOTE: These systems are intended to be used in the event of a
    leak or overflow from the tank due to a system failure (e.g., a malfunction
    in the treatment process, a crack in the tank, etc.).
     
    c) A generator of between 100 and 1,000 kg/mo accumulating hazardous waste in
    tanks must inspect the following, where present:
     
    1) Discharge control equipment (e.g., waste feed cutoff systems, by-pass
    systems, and drainage systems) at least once each operating day, to ensure
    that it is in good working order;
     
    2) Data gathered from monitoring equipment (e.g., pressure and temperature
    gauges) at least once each operating day to ensure that the tank is being
    operated according to its design;
     
    3) The level of waste in the tank at least once each operating day to ensure
    compliance with subsection (b)(3) of this Section;
     
    4) The construction materials of the tank at least weekly to detect corrosion
    or leaking of fixtures or seams; and
     
    5) The construction materials of and the area immediately surrounding
    discharge confinement structures (e.g., dikes) at least weekly to detect
    erosion or obvious signs of leakage (e.g., wet spots or dead vegetation).
     
    BOARD NOTE: As required by Section 725.115(c), the owner or
    operator must remedy any deterioration or malfunction the owner or
    operator finds.
     
    d) A generator of between 100 and 1,000 kg/mo accumulating hazardous waste in

     
    573
    tanks must, upon closure of the facility, remove all hazardous waste from tanks,
    discharge control equipment, and discharge confinement structures.
     
    BOARD NOTE: At closure, as throughout the operating period, unless the owner
    or operator demonstrates, in accordance with 35 Ill. Adm. Code 721.103(d) or (e),
    that any solid waste removed from the tank is not a hazardous waste, the owner or
    operator becomes a generator of hazardous waste and must manage it in
    accordance with all applicable requirements of 35 Ill. Adm. Code 722, 723, and
    725.
     
    e) A generator of between 100 and 1,000 kg/mo must comply with the following
    special requirements for ignitable or reactive waste:
     
    1) Ignitable or reactive waste must not be placed in a tank unless one of the
    following conditions are fulfilled:
     
    A) The waste is treated, rendered, or mixed before or immediately
    after placement in a tank so that the following is true of the waste:
     
    i) The resulting waste, mixture, or dissolution of material no
    longer meets the definition of ignitable or reactive waste
    under 35 Ill. Adm. Code 721.121 or 721.123, and
     
    ii) Section 725.117(b) is complied with;
     
    B) The waste is stored or treated in such a way that it is protected
    from any material or conditions that may cause the waste to ignite
    or react; or
     
    C) The tank is used solely for emergencies.
     
    2) The owner or operator of a facility that treats or stores ignitable or reactive
    waste in covered tanks must comply with the buffer zone requirements for
    tanks contained in Tables 2-1 through 2-6 of the National Fire Protection
    Association’s “Flammable and Combustible Liquids Code,” NFPA 30,
    incorporated by reference in 35 Ill. Adm. Code 720.111(a).
     
    f) A generator of between 100 and 1,000 kg/mo must comply with the following
    special requirements for incompatible wastes:
     
    1) Incompatible wastes or incompatible wastes and materials (see Appendix
    E appendix V of 40 CFR 265 (Examples of Potentially Incompatible
    Waste), incorporated by reference in 35 Ill. Adm. Code 720.111(b), for
    examples) must not be placed in the same tank unless Section 725.117(b)
    is complied with.
     

     
    574
    2) Hazardous waste must not be placed in an unwashed tank that previously
    held an incompatible waste or material unless Section 725.117(b) is
    complied with.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART K: SURFACE IMPOUNDMENTS
     
    Section 725.324 Containment System
     
    An earthen dike must have a protective cover, such as grass, shale, or rock to minimize wind and
    water erosion and to preserve its structural integrity.
     
    BOARD NOTE: Two versions of 40 CFR 265.223 exist in the federal regulations. USEPA
    added the second at 57 Fed. Reg. 3486, January 29, 1992. Section 725.324 is derived from the
    original version of 40 CFR 265.223.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.330 Special Requirements for Incompatible Wastes
     
    Incompatible wastes, or incompatible waste and materials (see Appendix V of 40 CFR 265
    (Examples of Potentially Incompatible Waste), incorporated by reference in 35 Ill. Adm. Code
    720.111(b), for examples) must not be placed in the same surface impoundment, unless Section
    725.117(b) is complied with.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART L: WASTE PILES
     
    Section 725.357 Special Requirements for Incompatible Wastes
     
    a) Incompatible wastes, or incompatible wastes and materials (see Appendix V of 40
    CFR 265 (Examples of Potentially Incompatible Waste), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b), for examples) must not be placed in
    the same pile, unless Section 725.117(b) is complied with.
     
    b) A pile of hazardous waste that is incompatible with any waste or other material
    stored nearby in other containers, piles, open tanks, or surface impoundments
    must be separated from the other materials or protected from them by means of a
    dike, berm, wall, or other device.
     
    BOARD NOTE: The purpose of this is to prevent fires, explosions, gaseous
    emissions, leaching, or other discharge of hazardous waste or hazardous waste
    constituents that could result from the contact or mixing of incompatible wastes
    or materials.

     
    575
     
    c) Hazardous waste must not be piled on the same area where incompatible wastes
    or materials were previously piled, unless that area has been decontaminated
    sufficiently to ensure compliance with Section 725.117(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART M: LAND TREATMENT
     
    Section 725.382 Special Requirements for Incompatible Wastes
     
    Incompatible wastes or incompatible wastes and materials (see Appendix V of 40 CFR 265
    (Examples of Potentially Incompatible Waste), incorporated by reference in 35 Ill. Adm. Code
    720.111(b), for examples) must not be placed in the same land treatment area unless Section
    725.117(b) is complied with.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART N: LANDFILLS
     
    Section 725.413 Special Requirements for Incompatible Wastes
     
    Incompatible wastes or incompatible wastes and materials (see Appendix V of 40 CFR 265
    (Examples of Potentially Incompatible Waste), incorporated by reference in 35 Ill. Adm. Code
    720.111(b), for examples) must not be placed in the same landfill cell, unless Section 725.117(b)
    is complied with.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.414 Special Requirements for Liquid Wastes
     
    a) This subsection (a) corresponds with 40 CFR 265.314(a), which pertains to the
    placement of bulk or non-containerized liquid waste or waste containing free
    liquids in a landfill prior to May 8, 1985. This statement maintains structural
    consistency with USEPA rules.
     
    b) The placement of bulk or non-containerized liquid hazardous waste or hazardous
    waste containing free liquids (whether or not sorbents have been added) in any
    landfill is prohibited.
     
    c) Containers holding free liquids must not be placed in a landfill unless one of the
    following conditions is fulfilled:
     
    1) One of the following occurs with regard to all free-standing liquid:
     
    A) It has been removed by decanting or other methods;

     
    576
     
    B) It has been mixed with sorbent or solidified so that free-standing
    liquid is no longer observed; or
     
    C) It has been otherwise eliminated;
     
    2) The container is very small, such as an ampule;
     
    3) The container is designed to hold free liquids for use other than storage,
    such as a battery or capacitor; or
     
    4) The container is a lab pack, as defined in Section 724.416 and is disposed
    of in accordance with Section 724.416.
     
    d) To demonstrate the absence or presence of free liquids in either a containerized or
    a bulk waste, the following test must be used: Method 9095 9095B (Paint Filter
    Liquids Test), as described in “Test Methods for Evaluating Solid Wastes,
    Physical/Chemical Methods,” USEPA Publication No. publication number EPA-
    530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
     
    e) The placement of any liquid that is not a hazardous waste in a landfill is
    prohibited (35 Ill. Adm. Code 729.311).
     
    f) Sorbents used to treat free liquids to be disposed of in landfills must be
    nonbiodegradable. Nonbiodegradable sorbents are one of the following:
    materials listed or described in subsection (f)(1) of this Section; materials that
    pass one of the tests in subsection (f)(2) of this Section; or materials that are
    determined by the Board to be nonbiodegradable through the adjusted standard
    procedure of Section 28.1 of the Act [415 ILCS 5/28.1] and Subpart D of 35 Ill.
    Adm. Code 104.
     
    1) Nonbiodegradable sorbents are the following:
     
    A) Inorganic minerals, other inorganic materials, and elemental
    carbon (e.g., aluminosilicates, clays, smectites, Fuller’s earth,
    bentonite, calcium bentonite, montmorillonite, calcined
    montmorillonite, kaolinite, micas (illite), vermiculites, zeolites,
    calcium carbonate (organic free limestone), oxides/hydroxides,
    alumina, lime, silica (sand), diatomaceous earth, perlite (volcanic
    glass), expanded volcanic rock, volcanic ash, cement kiln dust, fly
    ash, rice hull ash, activated charcoal/activated carbon, etc.); or
     
    B) High molecular weight synthetic polymers (e.g., polyethylene,
    high density polyethylene (HDPE), polypropylene, polystyrene,
    polyurethane, polyacrylate, polynorborene, polyisobutylene,
    ground synthetic rubber, cross-linked allylstyrene, and tertiary

     
    577
    butyl copolymers). This does not include polymers derived from
    biological material or polymers specifically designed to be
    degradable; or
     
    C) Mixtures of these nonbiodegradable materials.
     
    2) Tests for nonbiodegradable sorbents.
     
    A) The sorbent material is determined to be nonbiodegradable under
    ASTM Method G21-70 (1984a)--“ (Standard Practice for
    Determining Resistance of Synthetic Polymer Materials to
    Fungi),” incorporated by reference in 35 Ill. Adm. Code
    720.111(a);
     
    B) The sorbent material is determined to be nonbiodegradable under
    ASTM Method G22-76 (1984b)--“ (Standard Practice for
    Determining Resistance of Plastics to Bacteria),” incorporated by
    reference in 35 Ill. Adm. Code 720.111(a); or
     
    C) The sorbent material is determined to be non-biodegradable under
    OECD test Guideline for Testing of Chemicals, Method 301B
    (CO2 Evolution (Modified Sturm Test)), incorporated by reference
    in 35 Ill. Adm. Code 720.111(a).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.416 Disposal of Small Containers of Hazardous Waste in Overpacked Drums
    (Lab Packs)
     
    Small containers of hazardous waste in overpacked drums (lab packs) may be placed in a landfill
    if the following requirements are met:
     
    a) Hazardous waste must be packaged in non-leaking inside containers. The inside
    containers must be of a design and constructed of a material that will not react
    dangerously with, be decomposed by, or be ignited by the waste held therein.
    Inside containers must be tightly and securely sealed. The inside containers must
    be of the size and type specified in the USDOT hazardous materials regulations,
    (49 CFR 173 (Shippers--General Requirements for Shipments and Packages), 178
    (Specifications for Packagings), and 179 (Specifications for Tank Cars), each
    incorporated by reference in 35 Ill. Adm. Code 720.111(b)), if those regulations
    specify a particular inside container for the waste.
     
    b) The inside containers must be overpacked in an open head USDOT-specification
    metal shipping container, (49 CFR 178 (Specifications for Packagings) and 179
    (Specifications for Tank Cars), incorporated by reference in 35 Ill. Adm. Code
    720.111(b), of no more than 416 liter (110 gallon) capacity and surrounded by, at

     
    578
    a minimum, a sufficient quantity of sorbent material, determined to be
    nonbiodegradable in accordance with 35 Ill. Adm. Code 725.414(f) to completely
    sorb all of the liquid contents of the inside containers. The metal outer container
    must be full after packing with inside containers and sorbent material.
     
    c) The sorbent material used must not be capable of reacting dangerously with,
    being decomposed by, or being ignited by the contents of the inside containers, in
    accordance with Section 725.117(b).
     
    d) Incompatible wastes, as defined in 35 Ill. Adm. Code 720.110, must not be placed
    in the same outside container.
     
    e) Reactive waste, other than cyanide- or sulfide-bearing waste, as defined in 35 Ill.
    Adm. Code 721.123(a)(5), must be treated or rendered non-reactive prior to
    packaging in accordance with subsections (a) through (d) of this Section.
    Cyanide- or sulfide-bearing reactive waste may be packaged in accordance with
    subsections (a) through (d) of this Section without first being treated or rendered
    non-reactive.
     
    f) Such disposal is in compliance with the requirements of 35 Ill. Adm. Code 728.
    Persons that incinerate lab packs according to the requirements of 35 Ill. Adm.
    Code 728.142(c)(1) may use fiber drums in place of metal outer containers. Such
    fiber drums must meet the USDOT specifications in 49 CFR 173.12 (Exceptions
    for Shipments of Waste Materials), incorporated by reference in 35 Ill. Adm.
    Code 720.111(b), and be overpacked according to subsection (b) of this Section.
     
    g) Pursuant to 35 Ill. Adm. Code 729.312, the use of labpacks for disposal of liquid
    wastes or wastes containing free liquids allowed under this Section is restricted to
    labwaste and non-periodic waste, as those terms are defined in that Part.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART O: INCINERATORS
     
    Section 725.440 Applicability
     
    a) The regulations in this Subpart O apply to owners or operators of hazardous waste
    incinerators (as defined in 35 Ill. Adm. Code 720.110), except as 35 Ill. Adm.
    Code 724.101 provides otherwise.
     
    b) Integration of the MACT standards.
     
    1) Except as provided by subsections (b)(2) and (b)(3) of this Section, the
    standards of this Part no longer apply when an owner or operator
    demonstrates compliance with the maximum achievable control
    technology (MACT) requirements of subpart EEE of 40 CFR 63 (National

     
    579
    Emission Standards for Hazardous Air Pollutants from Hazardous Waste
    Combustors), incorporated by reference in 35 Ill. Adm. Code 720.111(b),
    by conducting a comprehensive performance test and submitting to the
    Agency a Notification of Compliance, under 40 CFR 63.1207(j) and
    63.1210(b), documenting compliance with the requirements of subpart
    EEE of 40 CFR 63.
     
    2) The MACT standards of subpart EEE of 40 CFR 63 do not replace the
    closure requirements of Section 724.451 or the applicable requirements of
    Subparts A through H, BB, and CC of this Part.
     
    3) Section 725.445, generally prohibiting burning of hazardous waste during
    startup and shutdown, remains in effect if the owner or operator elects to
    comply with 35 Ill. Adm. Code 703.320(b)(1)(A) to minimize emissions
    of toxic compounds from startup and shutdown.
     
    BOARD NOTE: Operating conditions used to determine effective treatment of
    hazardous waste remain effective after the owner or operator demonstrates
    compliance with the standards of subpart EEE of 40 CFR 63. Sections 9.1 and
    39.5 of the Environmental Protection Act [415 ILCS 5/9.1 and 39.5] make the
    federal MACT standards directly applicable to entities in Illinois and authorize
    the Agency to issue permits based on the federal standards.
     
    c) An owner or operator of an incinerator that burns hazardous waste is exempt from
    all of the requirements of this Subpart O, except Section 725.451 (Closure),
    provided that the owner or operator has documented, in writing, that the waste
    would not reasonably be expected to contain any of the hazardous constituents
    listed in Appendix H to 35 Ill. Adm. Code 721 and such documentation is
    retained at the facility, if the waste to be burned is one of the following:
     
    1) It is listed as a hazardous waste in Subpart D of 35 Ill. Adm. Code 721,
    solely because it is ignitable (Hazard Code I), corrosive (Hazard Code C),
    or both;
     
    2) It is listed as a hazardous waste in Subpart D of 35 Ill. Adm. Code 721,
    solely because it is reactive (Hazard Code R) for characteristics other than
    those listed in 35 Ill. Adm. Code 721.123(a)(4) and (a)(5), and will not be
    burned when other hazardous wastes are present in the combustion zone;
     
    3) It is a hazardous waste solely because it possesses the characteristic of
    ignitability, corrosivity, or both, as determined by the tests for
    characteristics of hazardous wastes under Subpart C of 35 Ill. Adm. Code
    721; or
     
    4) It is a hazardous waste solely because it possesses the reactivity
    characteristics described by 35 Ill. Adm. Code 721.123 (a)(1), (a)(2),

     
    580
    (a)(3), (a)(6), (a)(7), or (a)(8) and will not be burned when other
    hazardous wastes are present in the combustion zone.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART W: DRIP PADS
     
    Section 725.543 Design and Operating Requirements
     
    a) Drip pads must fulfill the following requirements:
     
    1) Not be constructed of earthen materials, wood, or asphalt, unless the
    asphalt is structurally supported;
     
    2) Be sloped to free-drain to the associated collection system treated wood
    drippage, rain, other waters, or solutions of drippage and water or other
    wastes;
     
    3) Have a curb or berm around the perimeter;
     
    4) In addition, the drip pad must fulfill the following requirements:
     
    A) Have a hydraulic conductivity of less than or equal to 1
    ×
    10
    -7
     
    centimeters per second, e.g., existing concrete drip pads must be
    sealed, coated, or covered with a surface material with a hydraulic
    conductivity of less than or equal to 1
    ×
    10
    -7
    centimeters per
    second such that the entire surface where drippage occurs or may
    run across is capable of containing such drippage and mixtures of
    drippage and precipitation, materials, or other wastes while being
    routed to an associated collection system. This surface material
    must be maintained free of cracks and gaps that could adversely
    affect its hydraulic conductivity, and the material must be
    chemically compatible with the preservatives that contact the drip
    pad. The requirements of this provision apply only to the existing
    drip pads and those drip pads for which the owner or operator
    elects to comply with Section 725.542(a) instead of Section
    725.542(b).
     
    B) The owner or operator must obtain and keep on file at the facility a
    written assessment of the drip pad, reviewed and certified by an
    independent qualified registered professional engineer that attests
    to the results of the evaluation. The assessment must be reviewed,
    updated, and recertified annually. The evaluation must document
    the extent to which the drip pad meets the design and operating
    standards of this Section, except for in subsection (b) of this
    Section.

     
    581
     
    5) Be of sufficient structural strength and thickness to prevent failure due to
    physical contact, climatic conditions, the stress of installation, and the
    stress of daily operations, e.g., variable and moving loads such as vehicle
    traffic, movement of wood, etc.
     
    BOARD NOTE: In judging the structural integrity requirement of this subsection
    (a), the Agency should generally consider applicable standards established by
    professional organizations generally recognized by the industry, including ACI
    318-83 (Building Code Requirements for Reinforced Concrete) or ASTM C94-
    90, (Standard Specification for Ready-Mixed Concrete), incorporated by
    reference in 35 Ill. Adm. Code 720.111(a).
     
    b) If an owner or operator elects to comply with Section 725.542(b) instead of
    Section 725.542(a), the drip pad must have the following features:
     
    1) A synthetic liner installed below the drip pad that is designed, constructed,
    and installed to prevent leakage from the drip pad into the adjacent
    subsurface soil or groundwater or surface water at any time during the
    active life (including the closure period) of the drip pad. The liner must
    be constructed of materials that will prevent waste from being absorbed
    into the liner and to prevent releases into the adjacent subsurface soil or
    groundwater or surface water during the active life of the facility. The
    liner must be constructed as follows:
     
    A) Constructed of materials that have appropriate chemical properties
    and sufficient strength and thickness to prevent failure due to
    pressure gradients (including static head and external
    hydrogeologic forces), physical contact with the waste or drip pad
    leakage to which they are exposed, climatic conditions, the stress
    of installation, and the stress of daily operation (including stresses
    from vehicular traffic on the drip pad);
     
    B) Placed upon a foundation or base capable of providing support to
    the liner and resistance to pressure gradients above and below the
    liner to prevent failure of the liner due to settlement, compression,
    or uplift; and
     
    C) Installed to cover all surrounding earth that could come in contact
    with the waste or leakage; and
     
    2) A leakage detection system immediately above the liner that is designed,
    constructed, maintained, and operated to detect leakage from the drip pad.
    The leakage detection system must be constructed as follows:
     
    A) Constructed of materials that fulfill the following requirements:

     
    582
     
    i) They are chemically resistant to the waste managed in the
    drip pad and the leakage that might be generated; and
     
    ii) They are of sufficient strength and thickness to prevent
    collapse under the pressures exerted by overlaying
    materials and by any equipment used at the drip pad; and
     
    B) Designed and operated to function without clogging through the
    scheduled closure of the drip pad; and
     
    C) Designed so that it will detect the failure of the drip pad or the
    presence of a release of hazardous waste or accumulated liquid at
    the earliest practicable time.
     
    3) A leakage collection system immediately above the liner that is designed,
    constructed, maintained, and operated to collect leakage from the drip pad
    such that it can be removed from below the drip pad. The date, time, and
    quantity of any leakage collected in this system and removed must be
    documented in the operating log.
     
    c) Drip pads must be maintained such that they remain free of cracks, gaps,
    corrosion, or other deterioration that could cause hazardous waste to be released
    from the drip pad.
     
    BOARD NOTE: See subsection (m) of this Section for remedial action required if
    deterioration or leakage is detected.
     
    d) The drip pad and associated collection system must be designed and operated to
    convey, drain and collect liquid resulting from drippage or precipitation in order
    to prevent run-off.
     
    e) Unless the drip pad is protected by a structure, as described in Section 725.540(b),
    the owner or operator must design, construct, operate, and maintain a run-on
    control system capable of preventing flow onto the drip pad during peak
    discharge from at least a 24-hour, 25-year storm, unless the system has sufficient
    excess capacity to contain any run-on that might enter the system.
     
    f) Unless the drip pad is protected by a structure or cover, as described in Section
    725.540(b), the owner or operator must design, construct, operate, and maintain a
    run-off management system to collect and control at least the water volume
    resulting from a 24-hour, 25-year storm.
     
    g) The drip pad must be evaluated to determine that it meets the requirements of
    subsections (a) through (f) of this Section. The owner or operator must obtain a
    statement from an independent, qualified, registered professional engineer

     
    583
    certifying that the drip pad design meets the requirements of this Section.
     
    h) Drippage and accumulated precipitation must be removed from the associated
    collection system as necessary to prevent overflow onto the drip pad.
     
    i) The drip pad surface must be cleaned thoroughly at least once every seven days
    using an appropriate and effective cleaning technique, including but not limited
    to, rinsing, washing with detergents or other appropriate solvents, or steam
    cleaning, with residues being properly managed, such that accumulated residues
    of hazardous waste or other materials are removed as to allow weekly inspections
    of the entire drip pad surface without interference or hindrance from accumulated
    residues of hazardous waste or other materials on the drip pad. The owner or
    operator must document, in the facility’s operating log, the date and time of each
    cleaning and the cleaning procedure.
     
    j) Drip pads must be operated and maintained in a manner to minimize tracking of
    hazardous waste or hazardous waste constituents off the drip pad as a result of
    activities by personnel or equipment.
     
    k) After being removed from the treatment vessel, treated wood from pressure and
    non-pressure processes must be held on the drip pad until drippage has ceased.
    The owner or operator must maintain records sufficient to document that all
    treated wood is held on the pad, in accordance with this Section, following
    treatment.
     
    l) Collection and holding units associated with run-on and run-off control systems
    must be emptied or otherwise managed as soon as possible after storms to
    maintain design capacity of the system.
     
    m) Throughout the active life of the drip pad, if the owner or operator detects a
    condition that may have caused or has caused a release of hazardous waste, the
    condition must be repaired within a reasonably prompt period of time following
    discovery, in accordance with the following procedures:
     
    1) Upon detection of a condition that may have caused or has caused a
    release of hazardous waste (e.g., upon detection of leakage in the leak
    detection system), the owner or operator must perform the following acts:
     
    A) Enter a record of the discovery in the facility operating log;
     
    B) Immediately remove from service the portion of the drip pad
    affected by the condition;
     
    C) Determine what steps must be taken to repair the drip pad, clean up
    any leakage from below the drip pad, and establish a schedule for
    accomplishing the clean up and repairs;

     
    584
     
    D) Within 24 hours after discovery of the condition, notify the
    Agency of the condition and, within 10 working days, provide
    written notice to the Agency with a description of the steps that
    will be taken to repair the drip pad and clean up any leakage, and
    the schedule for accomplishing this work.
     
    2) The Agency must: review the information submitted; make a
    determination regarding whether the pad must be removed from service
    completely or partially until repairs and clean up are complete; and notify
    the owner or operator of the determination and the underlying rationale in
    writing.
     
    3) Upon completing all repairs and clean up, the owner or operator must
    notify the Agency in writing and provide a certification, signed by an
    independent, qualified, registered professional engineer, that the repairs
    and clean up have been completed according to the written plan submitted
    in accordance with subsection (m)(1)(D) of this Section.
     
    n) The owner or operator must maintain, as part of the facility operating log,
    documentation of past operating and waste handling practices. This must include
    identification of preservative formulations used in the past, a description of
    drippage management practices and a description of treated wood storage and
    handling practices.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART AA: AIR EMISSION STANDARDS FOR PROCESS VENTS
     
    Section 725.933 Standards: Closed-Vent Systems and Control Devices
     
    a) Compliance Required.
     
    1) Owners or operators of closed-vent systems and control devices used to
    comply with provisions of this Part must comply with the provisions of
    this Section.
     
    2) Implementation Schedule.
     
    A) The owner or operator of an existing facility that cannot install a
    closed-vent system and control device to comply with the
    provisions of this Subpart AA on the effective date that the facility
    becomes subject to the provisions of this Subpart AA must prepare
    an implementation schedule that includes dates by which the
    closed-vent system and control device will be installed and in
    operation. The controls must be installed as soon as possible, but

     
    585
    the implementation schedule may allow up to 30 months after the
    effective date that the facility becomes subject to this Subpart AA
    for installation and startup.
     
    B) Any unit that begins operation after December 21, 1990, and
    which is subject to the provisions of this Subpart AA when
    operation begins, must comply with the rules immediately (i.e.,
    must have control devices installed and operating on startup of the
    affected unit); the 30-month implementation schedule does not
    apply.
     
    C) The owner or operator of any facility in existence on the effective
    date of a statutory or regulatory amendment that renders the
    facility subject to this Subpart AA must comply with all
    requirements of this Subpart AA as soon as practicable but no later
    than 30 months after the effective date of the amendment. When
    control equipment required by this Subpart AA can not be installed
    and begin operation by the effective date of the amendment, the
    facility owner or operator must prepare an implementation
    schedule that includes the following information: specific calendar
    dates for award of contracts or issuance of purchase orders for the
    control equipment, initiation of on-site installation of the control
    equipment, completion of the control equipment installation, and
    performance of any testing to demonstrate that the installed
    equipment meets the applicable standards of this Subpart AA. The
    owner or operator must enter the implementation schedule in the
    operating record or in a permanent, readily available file located at
    the facility.
     
    D) An owner or operator of a facility or unit that becomes newly
    subject to the requirements of this Subpart AA after December 8,
    1997, due to an action other than those described in subsection
    (a)(2)(iii) of this Section must comply with all applicable
    requirements immediately (i.e., the facility or unit must have
    control devices installed and operating on the date the facility or
    unit becomes subject to this Subpart AA; the 30-month
    implementation schedule does not apply).
     
    b) A control device involving vapor recovery (e.g., a condenser or adsorber) must be
    designed and operated to recover the organic vapors vented to it with an
    efficiency of 95 weight percent or greater unless the total organic emission limits
    of Section 725.932(a)(1) for all affected process vents is attained at an efficiency
    less than 95 weight percent.
     
    c) An enclosed combustion device (e.g., a vapor incinerator, boiler, or process
    heater) must be designed and operated to reduce the organic emissions vented to

     
    586
    it by 95 weight percent or greater; to achieve a total organic compound
    concentration of 20 ppmv, expressed as the sum of the actual compounds, not
    carbon equivalents, on a dry basis corrected to three percent oxygen; or to provide
    a minimum residence time of 0.50 seconds at a minimum temperature of 760
    degrees Celsius (° C). If a boiler or process heater is used as the control device,
    then the vent stream must be introduced into the flame combustion zone of the
    boiler or process heater.
     
    d) Flares.
     
    1) A flare must be designed for and operated with no visible emissions as
    determined by the methods specified in subsection (e)(1) of this Section
    except for periods not to exceed a total of five minutes during any two
    consecutive hours.
     
    2) A flare must be operated with a flame present at all times, as determined
    by the methods specified in subsection (f)(2)(c) of this Section.
     
    3) A flare must be used only if the net heating value of the gas being
    combusted is 11.2 MJ/scm (300 Btu/scf) or greater if the flare is steam-
    assisted or air-assisted, or if the net heating value of the gas being
    combusted is 7.45 MJ/scm (200 Btu/scf) or greater if the flare is
    nonassisted. The net heating value of the gas being combusted must be
    determined by the methods specified in subsection (e)(2) of this Section.
     
    4) Exit Velocity.
     
    A) A steam-assisted or nonassisted flare must be designed for and
    operated with an exit velocity, as determined by the methods
    specified in subsection (e)(3) of this Section, less than 18.3 m/s (60
    ft/s), except as provided in subsections (d)(4)(B) and (d)(4)(C) of
    this Section.
     
    B) A steam-assisted or nonassisted flare designed for and operated
    with an exit velocity, as determined by the methods specified in
    subsection (e)(3) of this Section, equal to or greater than 18.3 m/s
    (60 ft/s) but less than 122 m/s (400 ft/s) is allowed if the net
    heating value of the gas being combusted is greater than 37.3
    MJ/scm (1,000 Btu/scf).
     
    C) A steam-assisted or nonassisted flare designed for and operated
    with an exit velocity, as determined by the methods specified in
    subsection (e)(3) of this Section, less than the velocity, V as
    determined by the method specified in subsection (e)(4) and less
    than 122 m/s (400 ft/s) is allowed.
     

     
    587
    5) An air-assisted flare must be designed and operated with an exit velocity
    less than the velocity, V, as determined by the method specified in
    subsection (e)(5) of this Section.
     
    6) A flare used to comply with this Section must be steam-assisted, air-
    assisted, or nonassisted.
     
    e) Compliance determination and equations.
     
    1) Reference Method 22 (Visual Determination of Fugitive Emissions from
    Material Sources and Smoke Emissions from Flares) in appendix A to 40
    CFR 60 (Test Methods), incorporated by reference in 35 Ill. Adm. Code
    720.111(b), must be used to determine the compliance of a flare with the
    visible emission provisions of this Subpart AA. The observation period is
    two hours and must be used according to Method 22.
     
    2) The net heating value of the gas being combusted in a flare must be
    calculated using the following equation:
     
    T
    i
    i
    i
    1
    n
    H
    = K C H
    ××
    =
      
     
    Where:
     
    HT is the net heating value of the sample in MJ/scm; where the net
    enthalpy per mole of offgas is based on combustion at 25° C and
    760 mm Hg, but the standard temperature for determining the
    volume corresponding to 1 mole is 20° C;
     
    K = 1.74
    ×
    10
    -7
    (1/ppm)(g mol/scm)(MJ/kcal) where the standard
    temperature for (g mol/scm) is 20° C;
     
    Σ
    Xi means the sum of the values of X for each component i, from
    i=1 to n;
     
    Ci is the concentration of sample component i in ppm on a wet
    basis, as measured for organics by Reference Method 18
    (Measurement of Gaseous Organic Compound Emissions by Gas
    Chromatography) in appendix A to 40 CFR 60 (Test Methods),
    and for carbon monoxide, by ASTM D 1946-90 (Standard Practice
    for Analysis of Reformed Gas by Gas Chromatography), each
    incorporated by reference in 35 Ill. Adm. Code 720.111(a)
    720.111; and
     

     
    588
    Hi is the net heat of combustion of sample component i, kcal/gmol
    at 25° C and 760 mm Hg. The heats of combustion must be
    determined using ASTM D 2382-88 (Standard Test Method for
    Heat of Combustion of Hydrocarbon Fuels by Bomb Calorimeter
    (High Precision Method)), incorporated by reference in 35 Ill.
    Adm. Code 720.111(a), if published values are not available or
    cannot be calculated.
     
    3) The actual exit velocity of a flare must be determined by dividing the
    volumetric flow rate (in units of standard temperature and pressure), as
    determined by Reference Methods 2 (Determination of Stack Gas Velocity
    and Volumetric Flow Rate (Type S Pitot Tube)), 2A (Direct Measurement
    of Gas Volume through Pipes and Small Ducts), 2C (Determination of Gas
    Velocity and Volumetric Flow Rate in Small Stacks or Ducts (Standard
    Pitot Tube)), or 2D (Measurement of Gas Volume Flow Rates in Small
    Pipes and Ducts) in appendix A to 40 CFR 60 (Test Methods),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b), as appropriate,
    by the unobstructed (free) cross-sectional area of the flare tip.
     
    4) The maximum allowed velocity in m/s, V for a flare complying with
    subsection (d)(4)(C) of this Section must be determined by the following
    equation:
     
    ()
    log V
    H 28.8
    31.7
    10 max
    T
    =
    +
     
     
    Where:
     
    log10 means logarithm to the base 10; and
     
    HT is the net heating value as determined in subsection (e)(2) of
    this Section.
     
    5) The maximum allowed velocity in m/s, V for an air-assisted flare must be
    determined by the following equation:
     
    V = 8 .7 0 6 + 0 .7 0 8 4 H T
    Where:
     
    HT is the net heating value as determined in subsection (e)(2) of
    this Section.
     
    f) The owner or operator must monitor and inspect each control device required to
    comply with this Section to ensure proper operation and maintenance of the

     
    589
    control device by implementing the following requirements:
     
    1) Install, calibrate, maintain, and operate according to the manufacturer’s
    specifications a flow indicator that provides a record of vent stream flow
    from each affected process vent to the control device at least once every
    hour. The flow indicator sensor must be installed in the vent stream at the
    nearest feasible point to the control device inlet but before being
    combined with other vent streams.
     
    2) Install, calibrate, maintain, and operate according to the manufacturer’s
    specifications a device to continuously monitor control device operation,
    as specified below:
     
    A) For a thermal vapor incinerator, a temperature monitoring device
    equipped with a continuous recorder. The device must have
    accuracy of ±1 percent of the temperature being monitored in ° C
    or ± 0.5° C, whichever is greater. The temperature sensor must be
    installed at a location in the combustion chamber downstream of
    the combustion zone.
     
    B) For a catalytic vapor incinerator, a temperature monitoring device
    equipped with a continuous recorder. The device must be capable
    of monitoring temperature at two locations and have an accuracy
    of ±1 percent of the temperature being monitored in ° C or ± 0.5°
    C, whichever is greater. One temperature sensor must be installed
    in the vent stream at the nearest feasible point to the catalyst bed
    inlet and a second temperature sensor must be installed in the vent
    stream at the nearest feasible point to the catalyst bed outlet.
     
    C) For a flare, a heat sensing monitoring device equipped with a
    continuous recorder that indicates the continuous ignition of the
    pilot flame.
     
    D) For a boiler or process heater having a design heat input capacity
    less than 44 MW, a temperature monitoring device equipped with a
    continuous recorder. The device must have an accuracy of ±1
    percent of the temperature being monitored in ° C or ± 0.5° C,
    whichever is greater. The temperature sensor must be installed at a
    location in the furnace downstream of the combustion zone.
     
    E) For a boiler or process heater having a design heat input capacity
    greater than or equal to 44 MW, a monitoring device equipped
    with a continuous recorder to measure parameters that indicate
    good combustion operating practices are being used.
     
    F) For a condenser, either of the following:

     
    590
     
    i) A monitoring device equipped with a continuous recorder
    to measure the concentration level of the organic
    compounds in the exhaust vent stream from the condenser;
    or
     
    ii) A temperature monitoring device equipped with a
    continuous recorder. The device must be capable of
    monitoring temperature with an accuracy of ±1 percent of
    the temperature being monitored in degrees Celsius (° C) or
    ±0.5° C, whichever is greater. The temperature sensor
    must be installed at a location in the exhaust vent stream
    from the condenser exit (i.e., product side).
     
    G) For a carbon adsorption system, such as a fixed-bed carbon
    adsorber that regenerates the carbon bed directly in the control
    device, either of the following:
     
    i) A monitoring device equipped with a continuous recorder
    to measure the concentration level of the organic
    compounds in the exhaust vent stream from the carbon bed;
    or
     
    ii) A monitoring device equipped with a continuous recorder
    to measure a parameter that indicates the carbon bed is
    regenerated on a regular, predetermined time cycle.
     
    3) Inspect the readings from each monitoring device required by subsections
    (f)(1) and (f)(2) of this Section at least once each operating day to check
    control device operation and, if necessary, immediately implement the
    corrective measures necessary to ensure the control device operates in
    compliance with the requirements of this Section.
     
    g) An owner or operator using a carbon adsorption system such as a fixed-bed
    carbon adsorber that regenerates the carbon bed directly onsite in the control
    device must replace the existing carbon in the control device with fresh carbon at
    a regular, predetermined time interval that is no longer than the carbon service life
    established as a requirement of Section 725.935(b)(4)(C)(vi).
     
    h) An owner or operator using a carbon adsorption system, such as a carbon canister,
    that does not regenerate the carbon bed directly onsite in the control device must
    replace the existing carbon in the control device with fresh carbon on a regular
    basis by using one of the following procedures:
     
    1) Monitor the concentration level of the organic compounds in the exhaust
    vent stream from the carbon adsorption system on a regular schedule, and

     
    591
    replace the existing carbon with fresh carbon immediately when carbon
    breakthrough is indicated. The monitoring frequency must be daily or at
    an interval no greater than 20 percent of the time required to consume the
    total carbon working capacity established as a requirement of Section
    725.935(b)(4)(C)(vii), whichever is longer.
     
    2) Replace the existing carbon with fresh carbon at a regular, predetermined
    time interval that is less than the design carbon replacement interval
    established as a requirement of Section 725.935(b)(4)(C)(vii).
     
    i) An owner or operator of an affected facility seeking to comply with the provisions
    of this Part by using a control device other than a thermal vapor incinerator,
    catalytic vapor incinerator, flare, boiler, process heater, condenser, or carbon
    adsorption system is required to develop documentation including sufficient
    information to describe the control device operation and identify the process
    parameter or parameters that indicate proper operation and maintenance of the
    control device.
     
    j) A closed-vent system must meet either of the following design requirements:
     
    1) A closed-vent system must be designed to operate with no detectable
    emissions, as indicated by an instrument reading of less than 500 ppmv
    above background, as determined by the methods specified at Section
    725.934(b), and by visual inspections; or
     
    2) A closed-vent system must be designed to operate at a pressure below
    atmospheric pressure. The system must be equipped with at least one
    pressure gauge or other pressure measurement device that can be read
    from a readily accessible location to verify that negative pressure is being
    maintained in the closed-vent system when the control device is operating.
     
    k) The owner or operator must monitor and inspect each closed-vent system required
    to comply with this Section to ensure proper operation and maintenance of the
    closed-vent system by implementing the following requirements:
     
    1) Each closed-vent system that is used to comply with subsection (j)(1) of
    this Section must be inspected and monitored in accordance with the
    following requirements:
     
    A) An initial leak detection monitoring of the closed-vent system must
    be conducted by the owner or operator on or before the date that
    the system becomes subject to this Section. The owner or operator
    must monitor the closed-vent system components and connections
    using the procedures specified in Section 725.934(b) to
    demonstrate that the closed-vent system operates with no
    detectable emissions, as indicated by an instrument reading of less

     
    592
    than 500 ppmv above background.
     
    B) After initial leak detection monitoring required in subsection
    (k)(1)(A) of this Section, the owner or operator must inspect and
    monitor the closed-vent system as follows:
     
    i) Closed-vent system joints, seams, or other connections that
    are permanently or semi-permanently sealed (e.g., a welded
    joint between two sections of hard piping or a bolted and
    gasketed ducting flange) must be visually inspected at least
    once per year to check for defects that could result in air
    pollutant emissions. The owner or operator must monitor a
    component or connection using the procedures specified in
    Section 725.934(b) to demonstrate that it operates with no
    detectable emissions following any time the component is
    repaired or replaced (e.g., a section of damaged hard piping
    is replaced with new hard piping) or the connection is
    unsealed (e.g., a flange is unbolted).
     
    ii) Closed-vent system components or connections other than
    those specified in subsection (k)(1)(B)(i) of this Section
    must be monitored annually and at other times as requested
    by the Agency, except as provided for in subsection (n) of
    this Section, using the procedures specified in Section
    725.934(b) to demonstrate that the components or
    connections operate with no detectable emissions.
     
    C) In the event that a defect or leak is detected, the owner or operator
    must repair the defect or leak in accordance with the requirements
    of subsection (k)(3) of this Section.
     
    D) The owner or operator must maintain a record of the inspection
    and monitoring in accordance with the requirements specified in
    Section 725.935.
     
    2) Each closed-vent system that is used to comply with subsection (j)(2) of
    this Section must be inspected and monitored in accordance with the
    following requirements:
     
    A) The closed-vent system must be visually inspected by the owner or
    operator to check for defects that could result in air pollutant
    emissions. Defects include, but are not limited to, visible cracks,
    holes, or gaps in ductwork or piping or loose connections.
     
    B) The owner or operator must perform an initial inspection of the
    closed-vent system on or before the date that the system becomes

     
    593
    subject to this Section. Thereafter, the owner or operator must
    perform the inspections at least once every year.
     
    C) In the event that a defect or leak is detected, the owner or operator
    must repair the defect in accordance with the requirements of
    subsection (k)(3) of this Section.
     
    D) The owner or operator must maintain a record of the inspection
    and monitoring in accordance with the requirements specified in
    Section 725.935.
     
    3) The owner or operator must repair all detected defects as follows:
     
    A) Detectable emissions, as indicated by visual inspection or by an
    instrument reading greater than 500 ppmv above background, must
    be controlled as soon as practicable, but not later than 15 calendar
    days after the emission is detected, except as provided for in
    subsection (k)(3)(C) of this Section.
     
    B) A first attempt at repair must be made no later than five calendar
    days after the emission is detected.
     
    C) Delay of repair of a closed-vent system for which leaks have been
    detected is allowed if the repair is technically infeasible without a
    process unit shutdown, or if the owner or operator determines that
    emissions resulting from immediate repair would be greater than
    the fugitive emissions likely to result from delay of repair. Repair
    of such equipment must be completed by the end of the next
    process unit shutdown.
     
    D) The owner or operator must maintain a record of the defect repair
    in accordance with the requirements specified in Section 725.935.
     
    l) A closed-vent system or control device used to comply with provisions of this
    Subpart AA must be operated at all times when emissions may be vented to it.
     
    m) The owner or operator using a carbon adsorption system to control air pollutant
    emissions must document that all carbon removed that is a hazardous waste and
    that is removed from the control device is managed in one of the following
    manners, regardless of the volatile organic concentration of the carbon:
     
    1) It is regenerated or reactivated in a thermal treatment unit that meets one
    of the following:
     
    A) The owner or operator of the unit has been issued a final permit
    under 35 Ill. Adm. Code 702, 703, and 705 that implements the

     
    594
    requirements of Subpart X of 35 Ill. Adm. Code 724; or
     
    B) The unit is equipped with and operating air emission controls in
    accordance with the applicable requirements of Subparts AA and
    CC of this Part or 35 Ill. Adm. Code 724; or
     
    C) The unit is equipped with and operating air emission controls in
    accordance with a federal national emission standard for hazardous
    air pollutants under 40 CFR 61 (National Emission Standards for
    Hazardous Air Pollutants) or 40 CFR 63 (National Emission
    Standards for Hazardous Air Pollutants for Source Categories),
    each incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    2) It is incinerated in a hazardous waste incinerator for which the owner or
    operator has done either of the following:
     
    A) The owner or operator has been issued a final permit under 35 Ill.
    Adm. Code 702, 703, and 705 that implements the requirements of
    Subpart O of 35 Ill. Adm. Code 724, or
     
    B) The owner or operator has designed and operates the incinerator in
    accordance with the interim status requirements of Subpart O of
    this Part.
     
    3) It is burned in a boiler or industrial furnace for which the owner or
    operator has done either of the following:
     
    A) The owner or operator has been issued a final permit under 35 Ill.
    Adm. Code 702, 703, and 705 that implements the requirements of
    Subpart H of 35 Ill. Adm. Code 726, or
     
    B) The owner or operator has designed and operates the boiler or
    industrial furnace in accordance with the interim status
    requirements of Subpart H of 35 Ill. Adm. Code 726.
     
    n) Any components of a closed-vent system that are designated, as described in
    Section 725.935(c)(9), as unsafe to monitor are exempt from the requirements of
    subsection (k)(1)(B)(ii) of this Section if both of the following conditions are
    fulfilled:
     
    1) The owner or operator of the closed-vent system has determined that the
    components of the closed-vent system are unsafe to monitor because
    monitoring personnel would be exposed to an immediate danger as a
    consequence of complying with subsection (k)(1)(B)(ii) of this Section;
    and
     

     
    595
    2) The owner or operator of the closed-vent system adheres to a written plan
    that requires monitoring the closed-vent system components using the
    procedure specified in subsection (k)(1)(B)(ii) of this Section as
    frequently as practicable during safe-to-monitor times.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.934 Test Methods and Procedures
     
    a) Each owner or operator subject to the provisions of this Subpart AA must comply
    with the test methods and procedures requirements provided in this Section.
     
    b) When a closed-vent system is tested for compliance with no detectable emissions,
    as required in Section 725.933(k), the test must comply with the following
    requirements:
     
    1) Monitoring must comply with Reference Method 21 (Determination of
    Volatile Organic Compound Leaks) in appendix A to 40 CFR 60 (Test
    Methods), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    2) The detection instrument must meet the performance criteria of Reference
    Method 21.
     
    3) The instrument must be calibrated before use on each day of its use by the
    procedures specified in Reference Method 21.
     
    4) Calibration gases must be:
     
    A) Zero air (less than 10 ppm of hydrocarbon in air).
     
    B) A mixture of methane or n-hexane and air at a concentration of
    approximately, but less than, 10,000 ppm methane or n-hexane.
     
    5) The background level must be determined as set forth in Reference
    Method 21.
     
    6) The instrument probe must be traversed around all potential leak
    interfaces as close to the interface as possible, as described in Reference
    Method 21.
     
    7) The arithmetic difference between the maximum concentration indicated
    by the instrument and the background level is compared with 500 ppm for
    determining compliance.
     
    c) Performance tests to determine compliance with Section 725.932(a) and with the
    total organic compound concentration limit of Section 725.933(c) must comply

     
    596
    with the following:
     
    1) Performance tests to determine total organic compound concentrations and
    mass flow rates entering and exiting control devices must be conducted
    and data reduced in accordance with the following reference methods and
    calculation procedures:
     
    A) Method 2 (Determination of Stack Gas Velocity and Volumetric
    Flow Rate (Type S Pitot Tube)) in appendix A to 40 CFR 60 (Test
    Methods), incorporated by reference in 35 Ill. Adm. Code
    720.111(b), for velocity and volumetric flow rate.
     
    B) Method 18 (Measurement of Gaseous Organic Compound
    Emissions by Gas Chromatography) or 25A (Determination of
    Total Gaseous Organic Concentration Using a Flame Ionization
    Analyzer) in appendix A to 40 CFR 60 (Test Methods),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b), for
    organic content. If Method 25A is used, the organic hazardous air
    pollutant (HAP) used as the calibration gas must be the single HAP
    that represents the largest percent by volume of the emissions. The
    use of Method 25A is acceptable if the response from the high-
    level calibration gas is at least 20 times the standard deviation of
    the response from the zero calibration gas when the instrument is
    zeroed on the most sensitive scale.
     
    C) Each performance test must consist of three separate runs, each run
    conducted for at least 1 hour under the conditions that exist when
    the hazardous waste management unit is operating at the highest
    load or capacity level reasonably expected to occur. For the
    purpose of determining total organic compound concentrations and
    mass flow rates, the average of results of all runs applies. The
    average must be computed on a time-weighed basis.
     
    D) Total organic mass flow rates must be determined by the following
    equation:
     
    i) For a source utilizing Method 18:
     
    h
    2sd
    i
    i
    -6
    E
    = Q
    x(
    n
    i = 1
    C x MW )x0.0416x10
      
     
    Where:
     

     
    597
    Eh = The total organic mass flow rate, kg/h;
     
    Q2sd = The volumetric flow rate of gases entering or
    exiting control device, dscm/h, as determined by
    Method 2 in 40 CFR 60, incorporated by reference
    in 35 Ill. Adm. Code 720.111(b);
     
    n = The number of organic compounds in the vent
    gas;
     
    Ci = The organic concentration in ppm, dry basis, of
    compound i in the vent gas, as determined by
    Method 18 in 40 CFR 60, incorporated by reference
    in 35 Ill. Adm. Code 720.111(b);
     
    MWi = The molecular weight of organic compound
    i in the vent gas, kg/kg-mol;
     
    0.0416 = The conversion factor for molar volume,
    kg-mol/m
    3
    , at 293 K and 760 mm Hg; and
     
    10
    -6
    = The conversion factor from ppm.
     
    ii) For a source utilizing Method 25A:
     
    6
    h
    10
    0416
    .
    0
    MW
    C
      
    Q
    =
    E
    ×
    ×
    ×
    ×
      
     
    Where:
     
    Eh = The total organic mass flow rate, kg/h;
     
    Q = The volumetric flow rate of gases entering or
    exiting control device, dscm/h, as determined by
    Method 2;
     
    C = The organic concentration in ppm, dry basis, of
    compound i in the vent gas, as determined by
    Method 25A;
     
    MW = The molecular weight of propane, 44 kg/kg-
    mol;
     
    0.0416 = The conversion factor for molar volume,
    kg-mol/m
    3
    , at 293 K and 760 mm Hg; and

     
    598
     
    10
    -6
    = The conversion factor from ppm.
     
    E) The annual total organic emission rate must be determined by the
    following equation:
     
    A = F
    ×
    H
     
    Where:
     
    A is total organic emission rate, kg/y;
     
    F is the total organic mass flow rate, kg/h, as calculated in
    subsection (c)(1)(D) of this Section; and
     
    H is the total annual hours of operation for the affected
    unit.
     
    F) Total organic emissions from all affected process vents at the
    facility must be determined by summing the hourly total organic
    mass emissions rates (F, as determined in subsection (c)(1)(D) of
    this Section) and by summing the annual total organic mass
    emission rates (A, as determined in subsection (c)(1)(E) of this
    Section) for all affected process vents at the facility.
     
    2) The owner or operator must record such process information as is
    necessary to determine the conditions of the performance tests.
    Operations during periods of startup, shutdown, and malfunction do not
    constitute representative conditions for the purpose of a performance test.
     
    3) The owner or operator of an affected facility must provide, or cause to be
    provided, performance testing facilities as follows:
     
    A) Sampling ports adequate for the test methods specified in
    subsection (c)(1) of this Section.
     
    B) Safe sampling platforms.
     
    C) Safe access to sampling platforms.
     
    D) Utilities for sampling and testing equipment.
     
    4) For the purpose of making compliance determinations, the time-weighted
    average of the results of the three runs must apply. In the event that a
    sample is accidentally lost or conditions occur in which one of the three
    runs must be discontinued because of forced shutdown, failure of an

     
    599
    irreplaceable portion of the sample train, extreme meteorological
    conditions, or other circumstances beyond the owner or operator’s control,
    compliance may, upon the Agency’s approval, be determined using the
    average of the results of the two other runs.
     
    d) To show that a process vent associated with a hazardous waste distillation,
    fractionation, thin-film evaporation, solvent extraction, or air or steam stripping
    operation is not subject to the requirements of this Subpart AA, the owner or
    operator must make an initial determination that the time-weighted, annual
    average total organic concentration of the waste managed by the waste
    management unit is less than 10 ppmw using one of the following two methods:
     
    1) Direct measurement of the organic concentration of the waste using the
    following procedures:
     
    A) The owner or operator must take a minimum of four grab samples
    of waste for each wastestream managed in the affected unit under
    process conditions expected to cause the maximum waste organic
    concentration.
     
    B) For waste generated onsite, the grab samples must be collected at a
    point before the waste is exposed to the atmosphere, such as in an
    enclosed pipe or other closed system that is used to transfer the
    waste after generation to the first affected distillation,
    fractionation, thin-film evaporation, solvent extraction, or air or
    steam stripping operation. For waste generated offsite, the grab
    samples must be collected at the inlet to the first waste
    management unit that receives the waste provided the waste has
    been transferred to the facility in a closed system such as a tank
    truck and the waste is not diluted or mixed with other waste.
     
    C) Each sample must be analyzed and the total organic concentration
    of the sample must be computed using Method 9060 9060A (Total
    Organic Carbon) or 8260 of “Test Methods for Evaluating Solid
    Waste, Physical/Chemical Methods,” USEPA publication number
    EPA-530/SW-846, incorporated by reference under 35 Ill. Adm.
    Code 720.111(a), or analyzed for its individual constituents.
     
    D) The arithmetic mean of the results of the analyses of the four
    samples apply for each wastestream managed in the unit in
    determining the time-weighted, annual average total organic
    concentration of the waste. The time-weighted average is to be
    calculated using the annual quantity of each waste stream
    processed and the mean organic concentration of each wastestream
    managed in the unit.
     

     
    600
    2) Using knowledge of the waste to determine that its total organic
    concentration is less than 10 ppmw. Documentation of the waste
    determination is required. Examples of documentation that must be used
    to support a determination under this subsection (d)(2) include the
    following:
     
    A) Production process information documenting that no organic
    compounds are used;
     
    B) Information that the waste is generated by a process that is
    identical to a process at the same or another facility that has
    previously been demonstrated by direct measurement to generate a
    wastestream having a total organic content less than 10 ppmw; or
     
    C) Prior speciation analysis results on the same wastestream where it
    is documented that no process changes have occurred since that
    analysis that could affect the waste total organic concentration.
     
    e) The determination that distillation, fractionation, thin-film evaporation, solvent
    extraction, or air or steam stripping operations that manage hazardous wastes with
    time-weighted, annual average total organic concentrations less than 10 ppmw
    must be made as follows:
     
    1) By the effective date that the facility becomes subject to the provisions of
    this Subpart AA or by the date when the waste is first managed in a waste
    management unit, whichever is later; and
     
    2) For continuously generated waste, annually; or
     
    3) Whenever there is a change in the waste being managed or a change in the
    process that generates or treats the waste.
     
    f) When an owner or operator and the Agency do not agree on whether a distillation,
    fractionation, thin-film evaporation, solvent extraction, or air or steam stripping
    operation manages a hazardous waste with organic concentrations of at least 10
    ppmw based on knowledge of the waste, the procedures in Method 8260 in SW-
    846, incorporated by reference in 35 Ill. Adm. Code 720.111(a), must be used to
    resolve the dispute dispute may be resolved using direct measurement, as
    specified in subsection (d)(1) of this Section.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.935 Recordkeeping Requirements
     
    a) Compliance Required.
     

     
    601
    1) Each owner or operator subject to the provisions of this Subpart AA must
    comply with the recordkeeping requirements of this Section.
     
    2) An owner or operator of more than one hazardous waste management unit
    subject to the provisions of this Subpart AA may comply with the
    recordkeeping requirements for these hazardous waste management units
    in one recordkeeping system if the system identifies each record by each
    hazardous waste management unit.
     
    b) Owners and operators must record the following information in the facility
    operating record:
     
    1) For facilities that comply with the provisions of Section 725.933(a)(2), an
    implementation schedule that includes dates by which the closed-vent
    system and control device will be installed and in operation. The schedule
    must also include a rationale of why the installation cannot be completed
    at an earlier date. The implementation schedule must be in the facility
    operating record by the effective date that the facility becomes subject to
    the provisions of this Subpart AA.
     
    2) Up-to-date documentation of compliance with the process vent standards
    in Section 725.932, including the following:
     
    A) Information and data identifying all affected process vents, annual
    throughput and operating hours of each affected unit, estimated
    emission rates for each affected vent and for the overall facility
    (i.e., the total emissions for all affected vents at the facility), and
    the approximate location within the facility of each affected unit
    (e.g., identify the hazardous waste management units on a facility
    plot plan).
     
    B) Information and data supporting determination of vent emissions
    and emission reductions achieved by add-on control devices based
    on engineering calculations or source tests. For the purpose of
    determining compliance, determinations of vent emissions and
    emission reductions must be made using operating parameter
    values (e.g., temperatures, flow rates, or vent stream organic
    compounds and concentrations) that represent the conditions that
    result in maximum organic emissions, such as when the waste
    management unit is operating at the highest load or capacity level
    reasonably expected to occur. If the owner or operator takes any
    action (e.g., managing a waste of different composition or
    increasing operating hours of affected waste management units)
    that would result in an increase in total organic emissions from
    affected process vents at the facility, then a new determination is
    required.

     
    602
     
    3) Where an owner or operator chooses to use test date to determine the
    organic removal efficiency or total organic compound concentration
    achieved by the control device, a performance test plan. The test plan
    must include the following:
     
    A) A description of how it is determined that the planned test is going
    to be conducted when the hazardous waste management unit is
    operating at the highest load or capacity level reasonably expected
    to occur. This must include the estimated or design flow rate and
    organic content of each vent stream and define the acceptable
    operating ranges of key process and control device parameters
    during the test program.
     
    B) A detailed engineering description of the closed-vent system and
    control device including the following:
     
    i) Manufacturer’s name and model number of control device;
     
    ii) Type of control device;
     
    iii) Dimensions of the control device;
     
    iv) Capacity; and
     
    v) Construction materials.
     
    C) A detailed description of sampling and monitoring procedures,
    including sampling and monitoring locations in the system, the
    equipment to be used, sampling and monitoring frequency, and
    planned analytical procedures for sample analysis.
     
    4) Documentation of compliance with Section 725.933 must include the
    following information:
     
    A) A list of all information references and sources used in preparing
    the documentation;
     
    B) Records, including the dates of each compliance test required by
    Section 725.933(j);
     
    C) If engineering calculations are used, a design analysis,
    specifications, drawings, schematics, and piping and
    instrumentation diagrams based on the appropriate sections of
    “APTI Course 415: (Control of Gaseous Emissions,” USEPA
    publication number 450/2-81-005, incorporated by reference in 35

     
    603
    Ill. Adm. Code 720.111(a)), or other engineering texts, approved
    by the Agency, that present basic control device design
    information. Documentation provided by the control device
    manufacturer or vendor that describes the control device design in
    accordance with subsections (b)(4)(C)(i) through (b)(4)(C)(vii) of
    this Section may be used to comply with this requirement. The
    design analysis must address the vent stream characteristics and
    control device operation parameters as specified below.
     
    i) For a thermal vapor incinerator, the design analysis must
    consider the vent stream composition, constituent
    concentrations, and flow rate. The design analysis must
    also establish the design minimum and average temperature
    in the combustion zone and the combustion zone residence
    time.
     
    ii) For a catalytic vapor incinerator, the design analysis must
    consider the vent stream composition, constituent
    concentrations, and flow rate. The design analysis must
    also establish the design minimum and average
    temperatures across the catalyst bed inlet and outlet.
     
    iii) For a boiler or process heater, the design analysis must
    consider the vent stream composition, constituent
    concentrations, and flow rate. The design analysis must
    also establish the design minimum and average flame zone
    temperatures, combustion zone residence time and
    description of method and location where the vent stream is
    introduced into the combustion zone.
     
    iv) For a flare, the design analysis must consider the vent
    stream composition, constituent concentrations, and flow
    rate. The design analysis must also consider the
    requirements specified in Section 725.933(d).
     
    v) For a condenser, the design analysis must consider the vent
    stream composition, constituent concentrations, flow rate,
    relative humidity, and temperature. The design analysis
    must also establish the design outlet organic compound
    concentration level, design average temperature of the
    condenser exhaust vent stream and design average
    temperatures of the coolant fluid at the condenser inlet and
    outlet.
     
    vi) For a carbon adsorption system, such as a fixed-bed
    adsorber that regenerates the carbon bed directly onsite in

     
    604
    the control device, the design analysis must consider the
    vent stream composition, constituent concentrations, flow
    rate, relative humidity and temperature. The design
    analysis must also establish the design exhaust vent stream
    organic compound concentration level, number and
    capacity of carbon beds, type and working capacity of
    activated carbon used for carbon beds, design total steam
    flow over the period of each complete carbon bed
    regeneration cycle, duration of the carbon bed steaming and
    cooling/drying cycles, design carbon bed temperature after
    regeneration, design carbon bed regeneration time and
    design service life of carbon.
     
    vii) For a carbon adsorption system, such as a carbon canister
    that does not regenerate the carbon bed directly onsite in
    the control device, the design analysis must consider the
    vent stream composition, constituent concentrations, flow
    rate, relative humidity and temperature. The design
    analysis must also establish the design outlet organic
    concentration level, capacity of carbon bed, type and
    working capacity of activated carbon used for carbon bed
    and design carbon replacement interval based on the total
    carbon working capacity of the control device and source
    operating schedule;
     
    D) A statement signed and dated by the owner or operator certifying
    that the operating parameters used in the design analysis
    reasonably represent the conditions that exist when the hazardous
    waste management unit is or would be operating at the highest load
    or capacity level reasonably expected to occur;
     
    E) A statement signed and dated by the owner or operator certifying
    that the control device is designed to operate at an efficiency of 95
    percent or greater unless the total organic concentration limit of
    Section 725.932(a) is achieved at an efficiency less than 95 weight
    percent or the total organic emission limits of Section 725.932(a)
    for affected process vents at the facility are attained by a control
    device involving vapor recovery at an efficiency less than 95
    weight percent. A statement provided by the control device
    manufacturer or vendor certifying that the control equipment meets
    the design specifications may be used to comply with this
    requirement; and
     
    F) If performance tests are used to demonstrate compliance, all test
    results.
     

     
    605
    c) Design documentation and monitoring operating and inspection information for
    each closed-vent system and control device required to comply with the
    provisions of this Part must be recorded and kept up-to-date in the facility
    operating record. The information must include the following:
     
    1) Description and date of each modification that is made to the closed-vent
    system or control device design;
     
    2) Identification of operating parameter, description of monitoring device,
    and diagram of monitoring sensor location or locations used to comply
    with Section 725.933(f)(1) and (f)(2);
     
    3) Monitoring, operating and inspection information required by Section
    725.933(f) through (k);
     
    4) Date, time, and duration of each period that occurs while the control
    device is operating when any monitored parameter exceeds the value
    established in the control device design analysis, as specified below:
     
    A) For a thermal vapor incinerator designed to operate with a
    minimum residence time of 0.50 second at a minimum temperature
    of 760
    °
    C, any period when the combustion temperature is below
    760
    °
    C.
     
    B) For a thermal vapor incinerator designed to operate with an
    organic emission reduction efficiency of 95 percent or greater, any
    period when the combustion zone temperature is more than 28° C
    below the design average combustion zone temperature established
    as a requirement of subsection (b)(4)(C)(i) of this Section.
     
    C) For a catalytic vapor incinerator, any period when either of the
    following occurs:
     
    i) Temperature of the vent stream at the catalyst bed inlet is
    more than 28° C below the average temperature of the inlet
    vent stream established as a requirement of subsection
    (b)(4)(C)(ii) of this Section; or
     
    ii) Temperature difference across the catalyst bed is less than
    80 percent of the design average temperature difference
    established as a requirement of subsection (b)(4)(C)(ii) of
    this Section.
     
    D) For a boiler or process heater, any period when either of the
    following occurs:
     

     
    606
    i) Flame zone temperature is more than 28° C below the
    design average flame zone temperature established as a
    requirement of subsection (b)(4)(C)(iii) of this Section; or
     
    ii) Position changes where the vent stream is introduced to the
    combustion zone from the location established as a
    requirement of subsection (b)(4)(C)(iii) of this Section.
     
    E) For a flare, period when the pilot flame is not ignited.
     
    F) For a condenser that complies with Section 725.933(f)(2)(F)(i),
    any period when the organic compound concentration level or
    readings of organic compounds in the exhaust vent stream from the
    condenser are more than 20 percent greater than the design outlet
    organic compound concentration level established as a requirement
    of subsection (b)(4)(C)(v) of this Section.
     
    G) For a condenser that complies with Section 725.933(f)(2)(F)(ii),
    any period when either of the following occurs:
     
    i) Temperature of the exhaust vent stream from the condenser
    is more than 6° C above the design average exhaust vent
    stream temperature established as a requirement of
    subsection (b)(4)(C)(v) of this Section; or
     
    ii) Temperature of the coolant fluid exiting the condenser is
    more than 6° C above the design average coolant fluid
    temperature at the condenser outlet established as a
    requirement of subsection (b)(4)(C)(v) of this Section.
     
    H) For a carbon adsorption system such as a fixed-bed carbon
    adsorber that regenerates the carbon bed directly onsite in the
    control device and complies with Section 725.933(f)(2)(G)(i), any
    period when the organic compound concentration level or readings
    of organic compounds in the exhaust vent stream from the carbon
    bed are more than 20 percent greater than the design exhaust vent
    stream organic compound concentration level established as a
    requirement of subsection (b)(4)(C)(vi) of this Section.
     
    I) For a carbon adsorption system such as a fixed-bed carbon
    adsorber that regenerates the carbon bed directly onsite in the
    control device and complies with Section 725.933(f)(2)(G)(ii), any
    period when the vent stream continues to flow through the control
    device beyond the predetermined carbon bed regeneration time
    established as a requirement of subsection (b)(4)(C)(vi) of this
    Section;

     
    607
     
    5) Explanation for each period recorded under subsection (c)(4) of this
    Section of the cause for control device operating parameter exceeding the
    design value and the measures implemented to correct the control device
    operation;
     
    6) For carbon adsorption systems operated subject to requirements specified
    in Section 725.933(g) or (h)(2), any date when existing carbon in the
    control device is replaced with fresh carbon;
     
    7) For carbon adsorption systems operated subject to requirements specified
    in Section 725.933(h)(1), a log that records:
     
    A) Date and time when control device is monitored for carbon
    breakthrough and the monitoring device reading.
     
    B) Date when existing carbon in the control device is replaced with
    fresh carbon;
     
    8) Date of each control device startup and shutdown;
     
    9) An owner or operator designating any components of a closed-vent system
    as unsafe to monitor pursuant to Section 725.933(n) must record in a log
    that is kept in the facility operating record the identification of closed-vent
    system components that are designated as unsafe to monitor in accordance
    with the requirements of Section 725.933(n), an explanation for each
    closed-vent system component stating why the closed-vent system
    component is unsafe to monitor, and the plan for monitoring each closed-
    vent system component; and
     
    10) When each leak is detected as specified in Section 725.933(k), the
    following information must be recorded:
     
    A) The instrument identification number, the closed-vent system
    component identification number, and the operator name, initials,
    or identification number;
     
    B) The date the leak was detected and the date of first attempt to
    repair the leak;
     
    C) The date of successful repair of the leak;
     
    D) Maximum instrument reading measured by Method 21
    (Determination of Volatile Organic Compound Leaks) of appendix
    A to 40 CFR 60, appendix A (Test Methods), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b), after it is successfully

     
    608
    repaired or determined to be nonrepairable; and
     
    E) “Repair delayed” and the reason for the delay if a leak is not
    repaired within 15 calendar days after discovery of the leak.
     
    i) The owner or operator may develop a written procedure
    that identifies the conditions that justify a delay of repair.
    In such cases, reasons for delay of repair may be
    documented by citing the relevant sections of the written
    procedure.
     
    ii) If delay of repair was caused by depletion of stocked parts,
    there must be documentation that the spare parts were
    sufficiently stocked on-site before depletion and the reason
    for depletion; and
     
    d) Records of the monitoring, operating and inspection information required by
    subsections (c)(3) through (c)(10) of this Section must be maintained by the
    owner or operator for at least three years following the date of each occurrence,
    measurement, corrective action, or record.
     
    e) For a control device other than a thermal vapor incinerator, catalytic vapor
    incinerator, flare, boiler, process heater, condenser or carbon adsorption system,
    monitoring and inspection information indicating proper operation and
    maintenance of the control device must be recorded in the facility operating
    record.
     
    f) Up-to-date information and data used to determine whether or not a process vent
    is subject to the requirements in Section 725.932, including supporting
    documentation as required by Section 725.934(d)(2), when application of the
    knowledge of the nature of the hazardous wastestream or the process by which it
    was produced is used, must be recorded in a log that is kept in the facility
    operating record.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART BB: AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS
     
    Section 725.950 Applicability
     
    a) The regulations in this Subpart BB apply to owners and operators of facilities that
    treat, store, or dispose of hazardous wastes (except as provided in Section
    725.101).
     
    b) Except as provided in Section 725.964(k), this Subpart BB applies to equipment
    that contains or contacts hazardous wastes with organic concentrations of at least

     
    609
    10 percent by weight that are managed in one of the following:
     
    1) A unit that is subject to the RCRA permitting requirements of 35 Ill. Adm.
    Code 702, 703, and 705;
     
    2) A unit (including a hazardous waste recycling unit) that is not exempt
    from permitting under the provisions of 35 Ill. Adm. Code 722.134(a)
    (i.e., a hazardous waste recycling unit that is not a “90-day” tank or
    container) and that is located at a hazardous waste management facility
    otherwise subject to the permitting requirements of 35 Ill. Adm. Code 702,
    703, and 705; or
     
    3) A unit that is exempt from permitting under the provisions of 35 Ill. Adm.
    Code 722.134(a) (i.e., a “90-day” tank or container) and which is not a
    recycling unit under the provisions of 35 Ill. Adm. Code 721.106.
     
    c) Each piece of equipment to which this Subpart BB applies must be marked in
    such a manner that it can be distinguished readily from other pieces of equipment.
     
    d) Equipment that is in vacuum service is excluded from the requirements of
    Sections 725.952 to 725.960, if it is identified as required in Section
    725.964(g)(5).
     
    e) Equipment that contains or contacts hazardous waste with an organic
    concentration of at least 10 percent by weight for less than 300 hours per calendar
    year is excluded from the requirements of Sections 725.952 through 725.960 if it
    is identified as required in Section 725.964(g)(6).
     
    f) This subsection (f) corresponds with 40 CFR 265.1050(f), which relates
    exclusively to a facility outside Illinois. This statement maintains structural
    consistency with the corresponding federal regulations.
     
    g) Purged coatings and solvents from surface coating operations subject to the
    federal national emission standards for hazardous air pollutants (NESHAPs) for
    the surface coating of automobiles and light-duty trucks at Subpart IIII of 40 CFR
    63, incorporated by reference in 35 Ill. Adm. Code 720.111(b), (National
    Emission Standards for Hazardous Air Pollutants: Surface Coating of
    Automobiles and Light-Duty Trucks) are not subject to the requirements of this
    Subpart BB.
     
    BOARD NOTE: The requirements of Sections 725.952 through 725.964 apply to equipment
    associated with hazardous waste recycling units previously exempt under 35 Ill. Adm. Code
    721.106(c)(1). Other exemptions under 35 Ill. Adm. Code 721.104 and 725.101(e) are not
    affected by these requirements.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)

     
    610
     
    Section 725.963 Test Methods and Procedures
     
    a) Each owner or operator subject to the provisions of this Subpart BB must comply
    with the test methods and procedures requirements provided in this Section.
     
    b) Leak detection monitoring, as required in Sections 725.952 through 725.962,
    must comply with the following requirements:
     
    1) Monitoring must comply with Reference Method 21 (Determination of
    Volatile Organic Compound Leaks) in appendix A to 40 CFR 60 (Test
    Methods), incorporated by reference in 35 Ill. Adm. Code 720.111(b);
     
    2) The detection instrument must meet the performance criteria of Reference
    Method 21;
     
    3) The instrument must be calibrated before use on each day of its use by the
    procedures specified in Reference Method 21;
     
    4) Calibration gases must be as follows:
     
    A) Zero air (less than 10 ppm of hydrocarbon in air);
     
    B) A mixture of methane or n-hexane and air at a concentration of
    approximately, but less than, 10,000 ppm methane or n-hexane;
    and
     
    5) The instrument probe must be traversed around all potential leak
    interfaces as close to the interface as possible as described in Reference
    Method 21.
     
    c) When equipment is tested for compliance with no detectable emissions, as
    required in Sections 725.952(e), 725.953(i), 725.954, and 725.957(f), the test
    must comply with the following requirements:
     
    1) The requirements of subsections (b)(1) through (b)(4) of this Section
    apply;
     
    2) The background level must be determined as set forth in Reference
    Method 21;
     
    3) The instrument probe must be traversed around all potential leak
    interfaces as close to the interface as possible as described in Reference
    Method 21; and
     
    4) This arithmetic difference between the maximum concentration indicated

     
    611
    by the instrument and the background level is compared with 500 ppm for
    determining compliance.
     
    d) In accordance with the waste analysis plan required by Section 725.113(b), an
    owner or operator of a facility must determine, for each piece of equipment,
    whether the equipment contains or contacts a hazardous waste with organic
    concentration that equals or exceeds 10 percent by weight using the following:
     
    1) Methods described in ASTM Methods D 2267-88 (Standard Test Method
    for Aromatics in Light Naphthas and Aviation Gasolines by Gas
    Chromatography), E 168-88 (Standard Practices for General Techniques
    of Infrared Quantitative Analysis), E 169-87 (Standard Practices for
    General Techniques of Ultraviolet-Visible Quantitative Analysis), or E
    260-85 (Standard Practice for Packed Column Gas Chromatography), each
    incorporated by reference in 35 Ill. Adm. Code 720.111(a);
     
    2) Method 9060
    9060A (Total Organic Carbon) or 8260 of “Test Methods
    for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    publication number EPA-530/SW-846, incorporated by reference in 35 Ill.
    Adm. Code 720.111(a), or analyzed for its individual organic constituents;
    or
     
    3) Application of the knowledge of the nature of the hazardous wastestream
    or the process by which it was produced. Documentation of a waste
    determination by knowledge is required. Examples of documentation that
    must be used to support a determination under this provision include
    production process information documenting that no organic compounds
    are used, information that the waste is generated by a process that is
    identical to a process at the same or another facility that has previously
    been demonstrated by direct measurement to have a total organic content
    less than 10 percent, or prior speciation analysis results on the same
    wastestream where it is also documented that no process changes have
    occurred since that analysis that could affect the waste total organic
    concentration.
     
    e) If an owner or operator determines that a piece of equipment contains or contacts
    a hazardous waste with organic concentrations at least 10 percent by weight, the
    determination can be revised only after following the procedures in subsection
    (d)(1) or (d)(2) of this Section.
     
    f) When an owner or operator and the Agency do not agree on whether a piece of
    equipment contains or contacts a hazardous waste with organic concentrations at
    least 10 percent by weight, the procedures in subsection (d)(1) or (d)(2) of this
    Section must be used to resolve the dispute.
     
    g) Samples used in determining the percent organic content must be representative

     
    612
    of the highest total organic content hazardous waste that is expected to be
    contained in or contact the equipment.
     
    h) To determine if pumps or valves are in light liquid service, the vapor pressures of
    constituents must either be obtained from standard reference texts or be
    determined by ASTM D 2879-92 (Standard Test Method for Vapor Pressure-
    Temperature Relationship and Initial Decomposition Temperature of Liquids by
    Isoteniscope), incorporated by reference in 35 Ill. Adm. Code 720.111(a).
     
    i) Performance tests to determine if a control device achieves 95 weight percent
    organic emission reduction must comply with the procedures of Section
    725.934(c)(1) through (c)(4).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.964 Recordkeeping Requirements
     
    a) Lumping Units.
     
    1) Each owner or operator subject to the provisions of this Subpart BB must
    comply with the recordkeeping requirements of this Section.
     
    2) An owner or operator of more than one hazardous waste management unit
    subject to the provisions of this Subpart BB may comply with the
    recordkeeping requirements for these hazardous waste management units
    in one recordkeeping system if the system identifies each record by each
    hazardous waste management unit.
     
    b) Owners and operators must record the following information in the facility
    operating record:
     
    1) For each piece of equipment to which this Subpart BB applies, the
    following:
     
    A) Equipment identification number and hazardous waste
    management unit identification;
     
    B) Approximate locations within the facility (e.g., identify the
    hazardous waste management unit on a facility plot plan);
     
    C) Type of equipment (e.g., a pump or pipeline valve);
     
    D) Percent-by-weight total organics in the hazardous wastestream at
    the equipment;
     
    E) Hazardous waste state at the equipment (e.g., gas/vapor or liquid);

     
    613
    and
     
    F) Method of compliance with the standard (e.g., “monthly leak
    detection and repair” or “equipped with dual mechanical seals”);
     
    2) For facilities that comply with the provisions of Section 725.933(a)(2), an
    implementation schedule, as specified in that Section;
     
    3) Where an owner or operator chooses to use test data to demonstrate the
    organic removal efficiency or total organic compound concentration
    achieved by the control device, a performance test plan, as specified in
    Section 725.935(b)(3); and
     
    4) Documentation of compliance with Section 725.960, including the
    detailed design documentation or performance test results specified in
    Section 725.935(b)(4).
     
    c) When each leak is detected, as specified in Section 725.952, 725.953, 725.957, or
    725.958, the following requirements apply:
     
    1) A weatherproof and readily visible identification, marked with the
    equipment identification number, the date evidence of a potential leak was
    found in accordance with Section 725.958(a), and the date the leak was
    detected, must be attached to the leaking equipment;
     
    2) The identification on equipment except on a valve, may be removed after
    it has been repaired; and
     
    3) The identification on a valve may be removed after it has been monitored
    for two successive months as specified in Section 725.957(c) and no leak
    has been detected during those two months.
     
    d) When each leak is detected, as specified in Sections 725.952, 725.953, 725.957,
    or 725.958, the following information must be recorded in an inspection log and
    must be kept in the facility operating record:
     
    1) The instrument and operator identification numbers and the equipment
    identification number;
     
    2) The date evidence of a potential leak was found in accordance with
    Section 725.958(a);
     
    3) The date the leak was detected and the dates of each attempt to repair the
    leak;
     
    4) Repair methods applied in each attempt to repair the leak;

     
    614
     
    5) “Above 10,000,” if the maximum instrument reading measured by the
    methods specified in Section 725.963(b) after each repair attempt is equal
    to or greater than 10,000 ppm;
     
    6) “Repair delayed” and the reason for the delay if a leak is not repaired
    within 15 calendar days after discovery of the leak;
     
    7) Documentation supporting the delay of repair of a valve in compliance
    with Section 725.959(c);
     
    8) The signature of the owner or operator (or designate) whose decision it
    was that repair could not be effected without a hazardous waste
    management unit shutdown;
     
    9) The expected date of successful repair of the leak if a leak is not repaired
    within 15 calendar days; and
     
    10) The date of successful repair of the leak.
     
    e) Design documentation and monitoring, operating, and inspection information for
    each closed-vent system and control device required to comply with the
    provisions of Section 725.960 must be recorded and kept up-to-date in the facility
    operating record as specified in Section 725.935(c)(1) and (c)(2), and monitoring,
    operating and inspection information in Section 725.935(c)(3) through (c)(8).
     
    f) For a control device other than a thermal vapor incinerator, catalytic vapor
    incinerator, flare, boiler, process heater, condenser, or carbon adsorption system,
    monitoring and inspection information indicating proper operation and
    maintenance of the control device must be recorded in the facility operating
    record.
     
    g) The following information pertaining to all equipment subject to the requirements
    in Sections 725.952 through 725.960 must be recorded in a log that is kept in the
    facility operating record:
     
    1) A list of identification numbers for equipment (except welded fittings)
    subject to the requirements of this Subpart BB.
     
    2) List of Equipment.
     
    A) A list of identification numbers for equipment that the owner or
    operator elects to designate for no detectable emissions, as
    indicated by an instrument reading of less than 500 ppm above
    background, under the provisions of Sections 725.952(e),
    725.953(i), and 725.957(f).

     
    615
     
    B) The designation of this equipment as subject to the requirements of
    Section 725.952(e), 725.953(i), or 725.957(f) must be signed by
    the owner or operator.
     
    3) A list of equipment identification numbers for pressure relief devices
    required to comply with Section 725.954(a).
     
    4) Compliance tests.
     
    A) The dates of each compliance test required in Sections 725.952(e),
    725.953(i), 725.954, and 725.957(f).
     
    B) The background level measured during each compliance test.
     
    C) The maximum instrument reading measured at the equipment
    during each compliance test.
     
    5) A list of identification numbers for equipment in vacuum service.
     
    6) Identification, either by list or location (area or group) of equipment that
    contains or contacts hazardous waste with an organic concentration of at
    least 10 percent by weight for less than 300 hours per year.
     
    h) The following information pertaining to all valves subject to the requirements of
    Section 725.957(g) and (h) must be recorded in a log that is kept in the facility
    operating record:
     
    1) A list of identification numbers for valves that are designated as unsafe to
    monitor, an explanation for each valve stating why the valve is unsafe to
    monitor, and the plan for monitoring each valve; and
     
    2) A list of identification numbers for valves that are designated as difficult
    to monitor, an explanation for each valve stating why the valve is difficult
    to monitor, and the planned schedule for monitoring each valve.
     
    i) The following information must be recorded in the facility operating record for
    valves complying with Section 725.962:
     
    1) A schedule of monitoring; and
     
    2) The percent of valves found leaking during each monitoring period.
     
    j) The following information must be recorded in a log that is kept in the facility
    operating record:
     

     
    616
    1) Criteria required in Sections 725.952(d)(5)(B) and 725.953(e)(2) and an
    explanation of the criteria; and
     
    2) Any changes to these criteria and the reasons for the changes.
     
    k) The following information must be recorded in a log that is kept in the facility
    operating record for use in determining exemptions, as provided in Section
    725.950 and other specific Subparts:
     
    1) An analysis determining the design capacity of the hazardous waste
    management unit;
     
    2) A statement listing the hazardous waste influent to and effluent from each
    hazardous waste management unit subject to the requirements in Section
    725.960 and an analysis determining whether these hazardous wastes are
    heavy liquids; and
     
    3) An up-to-date analysis and the supporting information and data used to
    determine whether or not equipment is subject to the requirements in
    Sections 725.952 through 725.960. The record must include supporting
    documentation, as required by Section 725.963(d)(3), when application of
    the knowledge of the nature of the hazardous wastestream or the process
    by which it was produced is used. If the owner or operator takes any
    action (e.g., changing the process that produced the waste) that could
    result in an increase in the total organic content of the waste contained in
    or contacted by equipment determined not to be subject to the
    requirements in Sections 725.952 through 725.960, then a new
    determination is required.
     
    l) Records of the equipment leak information required by subsection (d) of this
    Section and the operating information required by subsection (e) of this Section
    need be kept only three years.
     
    m) The owner or operator of any facility with equipment that is subject to this
    Subpart and to federal regulations at 40 CFR 60, 61, or 63, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b), may elect to determine compliance
    with this Subpart BB by documentation of compliance either pursuant to Section
    725.964 or by documentation of compliance with the regulations at 40 CFR 60
    (Standards of Performance for New Stationary Sources), 61 (National Emission
    Standards for Hazardous Air Pollutants), or 63 (National Emission Standards for
    Hazardous Air Pollutants for Source Categories), pursuant to the relevant
    provisions of 40 CFR 60, 61, or 63, each incorporated by reference in 35 Ill.
    Adm. Code 720.111(b). The documentation of compliance under the regulation
    at 40 CFR 60, 61, or 63 must be kept with or made readily available with the
    facility operating record.
     

     
    617
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE
    IMPOUNDMENTS, AND CONTAINERS
     
    Section 725.980 Applicability
     
    a) The requirements of this Subpart CC apply to owners and operators of all
    facilities that treat, store, or dispose of hazardous waste in tanks, surface
    impoundments, or containers that are subject to Subpart I, J, or K of this Part,
    except as Section 725.101 and subsection (b) of this Section provide otherwise.
     
    b) The requirements of this Subpart CC do not apply to the following waste
    management units at the facility:
     
    1) A waste management unit that holds hazardous waste placed in the unit
    before December 6, 1996, and in which no hazardous waste is added to the
    unit on or after December 6, 1996;
     
    2) A container that has a design capacity less than or equal to 0.1 m
    3
    (3.5 ft
    3
     
    or 26.4 gal);
     
    3) A tank in which an owner or operator has stopped adding hazardous waste
    and the owner or operator has begun implementing or completed closure
    pursuant to an approved closure plan;
     
    4) A surface impoundment in which an owner or operator has stopped adding
    hazardous waste (except to implement an approved closure plan) and the
    owner or operator has begun implementing or completed closure pursuant
    to an approved closure plan;
     
    5) A waste management unit that is used solely for on-site treatment or
    storage of hazardous waste that is placed in the unit as a result of
    implementing remedial activities required pursuant to the Act or Board
    regulations or under the corrective action authorities of RCRA sections
    3004(u), 3004(v), or 3008(h); CERCLA authorities; or similar federal or
    State authorities;
     
    6) A waste management unit that is used solely for the management of
    radioactive mixed waste in accordance with all applicable regulations
    under the authority of the Atomic Energy Act of 1954 (42 USC 2011 et
    seq.) and the Nuclear Waste Policy Act of 1982 (42 USC 10101 et seq.);
     
    7) A hazardous waste management unit that the owner or operator certifies is
    equipped with and operating air emission controls in accordance with the
    requirements of an applicable federal Clean Air Act regulation codified

     
    618
    under 40 CFR 60 (Standards of Performance for New Stationary Sources),
    61 (National Emission Standards for Hazardous Air Pollutants), or 63
    (National Emission Standards for Hazardous Air Pollutants for Source
    Categories), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
    For the purpose of complying with this subsection (b)(7), a tank for which
    the air emission control includes an enclosure, as opposed to a cover, must
    be in compliance with the enclosure and control device requirements of
    Section 725.985(i), except as provided in Section 725.983(c)(5); and
     
    8) A tank that has a process vent, as defined in 35 Ill. Adm. Code 725.931.
     
    c) For the owner and operator of a facility subject to this Subpart CC that has
    received a final RCRA permit prior to December 6, 1996, the following
    requirements apply:
     
    1) The requirements of Subpart CC of 35 Ill. Adm. Code 724 must be
    incorporated into the permit when the permit is reissued, renewed, or
    modified in accordance with the requirements of 35 Ill. Adm. Code 703
    and 705.
     
    2) Until the date when the permit is reissued, renewed, or modified in
    accordance with the requirements of 35 Ill. Adm. Code 703 and 705, the
    owner and operator is subject to the requirements of this Subpart CC.
     
    d) The requirements of this Subpart CC, except for the recordkeeping requirements
    specified in Section 725.990(i), are stayed for a tank or container used for the
    management of hazardous waste generated by organic peroxide manufacturing
    and its associated laboratory operations, when the owner or operator of the unit
    meets all of the following conditions:
     
    1) The owner or operator identifies that the tank or container receives
    hazardous waste generated by an organic peroxide manufacturing process
    producing more than one functional family of organic peroxides or
    multiple organic peroxides within one functional family, that one or more
    of these organic peroxides could potentially undergo self-accelerating
    thermal decomposition at or below ambient temperatures, and that organic
    peroxides are the predominant products manufactured by the process. For
    the purposes of this subsection, “organic peroxide” means an organic
    compound that contains the bivalent -O-O- structure and which may be
    considered to be a structural derivative of hydrogen peroxide where one or
    both of the hydrogen atoms has been replaced by an organic radical;
     
    2) The owner or operator prepares documentation, in accordance with
    Section 725.990(i), explaining why an undue safety hazard would be
    created if air emission controls specified in Sections 725.985 through
    725.988 are installed and operated on the tanks and containers used at the

     
    619
    facility to manage the hazardous waste generated by the organic peroxide
    manufacturing process or processes meeting the conditions of subsection
    (d)(1) of this Section; and
     
    3) The owner or operator notifies the Agency in writing that hazardous waste
    generated by an organic peroxide manufacturing process or processes
    meeting the conditions of subsection (d)(1) of this Section are managed at
    the facility in tanks or containers meeting the conditions of subsection
    (d)(2) of this Section. The notification must state the name and address of
    the facility and be signed and dated by an authorized representative of the
    facility owner or operator.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.981 Definitions
     
    As used in this Subpart CC and in 35 Ill. Adm. Code 724, all terms not defined herein will have
    the meanings given to them in the Act and 35 Ill. Adm. Code 720 through 726.
     
    “Average volatile organic concentration” or “average VO concentration” means
    the mass-weighted average volatile organic concentration of a hazardous waste,
    as determined in accordance with the requirements of Section 725.984.
     
    “Closure device” means a cap, hatch, lid, plug, seal, valve, or other type of fitting
    that blocks an opening in a cover so that when the device is secured in the closed
    position it prevents or reduces air pollutant emissions to the atmosphere. Closure
    devices include devices that are detachable from the cover (e.g., a sampling port
    cap), manually operated (e.g., a hinged access lid or hatch), or automatically
    operated (e.g., a spring-loaded pressure relief valve).
     
    “Continuous seal” means a seal that forms a continuous closure that completely
    covers the space between the edge of the floating roof and the wall of a tank. A
    continuous seal may be a vapor-mounted seal, liquid-mounted seal, or metallic
    shoe seal. A continuous seal may be constructed of fastened segments so as to
    form a continuous seal.
     
    “Cover” means a device that provides a continuous barrier over the hazardous
    waste managed in a unit to prevent or reduce air emissions to the atmosphere. A
    cover may have openings (such as access hatches, sampling ports, and gauge
    wells) that are necessary for operation, inspection, maintenance, or repair of the
    unit on which the cover is used. A cover may be a separate piece of equipment
    that can be detached and removed from the unit or a cover may be formed by
    structural features permanently integrated into the design of the unit.
     
    “Enclosure” means a structure that surrounds a tank or container, captures organic
    vapors emitted from the tank or container, and vents the captured vapors through

     
    620
    a closed-vent system to a control device.
     
    “External floating roof” means a pontoon-type or double-deck type cover that
    rests on the surface of a hazardous waste being managed in a tank with no fixed
    roof.
     
    “Fixed roof” means a cover that is mounted on a unit in a stationary position and
    does not move with fluctuations in the level of the material managed in the unit.
     
    “Floating membrane cover” means a cover consisting of a synthetic flexible
    membrane material that rests upon and is supported by the hazardous waste being
    managed in a surface impoundment.
     
    “Floating roof” means a cover consisting of a double-deck, pontoon single-deck,
    or internal floating cover that rests upon and is supported by the material being
    contained, and is equipped with a continuous seal.
     
    “Hard-piping” means pipe or tubing that is manufactured and properly installed in
    accordance with relevant standards and good engineering practices.
     
    “In light material service” means that the container is used to manage a material
    for which both of the following conditions apply: the vapor pressure of one or
    more of the organic constituents in the material is greater than 0.3 kilopascals
    (kPa) at 20°C (1.2 inches H2O at 68°F); and the total concentration of the pure
    organic constituents having a vapor pressure greater than 0.3 kPa at 20°C (1.2
    inches H2O at 68°F) is equal to or greater than 20 percent by weight.
     
    “Internal floating roof” means a cover that rests or floats on the material surface
    (but not necessarily in complete contact with it) inside a tank that has a fixed roof.
     
    “Liquid-mounted seal” means a foam or liquid-filled primary seal mounted in
    contact with the hazardous waste between the tank wall and the floating roof,
    continuously around the circumference of the tank.
     
    “Malfunction” means any sudden, infrequent, and not reasonably preventable
    failure of air pollution control equipment, process equipment, or a process to
    operate in a normal or usual manner. A failure that is caused in part by poor
    maintenance or careless operation is not a malfunction.
     
    “Maximum organic vapor pressure” means the sum of the individual organic
    constituent partial pressures exerted by the material contained in a tank at the
    maximum vapor pressure-causing conditions (i.e., temperature, agitation, pH
    effects of combining wastes, etc.) reasonably expected to occur in the tank. For
    the purpose of this Subpart CC, maximum organic vapor pressure is determined
    using the procedures specified in Section 725.984(c).
     

     
    621
    “Metallic shoe seal” means a continuous seal that is constructed of metal sheets
    that are held vertically against the wall of the tank by springs, weighted levers, or
    other mechanisms and which is connected to the floating roof by braces or other
    means. A flexible coated fabric (envelope) spans the annular space between the
    metal sheet and the floating roof.
     
    “No detectable organic emissions” means no escape of organics to the
    atmosphere, as determined using the procedure specified in Section 725.984(d).
     
    “Point of waste origination” means as follows:
     
    When the facility owner or operator is the generator of the hazardous
    waste, the “point of waste origination” means the point where a solid
    waste produced by a system, process, or waste management unit is
    determined to be a hazardous waste, as defined in 35 Ill. Adm. Code 721.
     
    BOARD NOTE: In this case, this term is being used in a manner similar
    to the use of the term “point of generation” in air standards established for
    waste management operations under authority of the federal Clean Air Act
    in 40 CFR 60 (Standards of Performance for New Stationary Sources), 61
    (National Emission Standards for Hazardous Air Pollutants), or 63
    (National Emission Standards for Hazardous Air Pollutants for Source
    Categories), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    When the facility owner and operator are not the generator of the
    hazardous waste, “point of waste origination” means the point where the
    owner or operator accepts delivery or takes possession of the hazardous
    waste.
     
    “Point of waste treatment” means the point where a hazardous waste to be treated
    in accordance with Section 725.983(c)(2) exits the treatment process. Any waste
    determination must be made before the waste is conveyed, handled, or otherwise
    managed in a manner that allows the waste to volatilize to the atmosphere.
     
    “Safety device” means a closure device, such as a pressure relief valve, frangible
    disc, fusible plug, or any other type of device that functions exclusively to prevent
    physical damage or permanent deformation to a unit or its air emission control
    equipment by venting gases or vapors directly to the atmosphere during unsafe
    conditions resulting from an unplanned, accidental, or emergency event. For the
    purpose of this Subpart CC, a safety device is not used for routine venting of
    gases or vapors from the vapor headspace underneath a cover such as during
    filling of the unit or to adjust the pressure in this vapor headspace in response to
    normal daily diurnal ambient temperature fluctuations. A safety device is
    designed to remain in a closed position during normal operations and open only
    when the internal pressure, or another relevant parameter, exceeds the device
    threshold setting applicable to the air emission control equipment as determined

     
    622
    by the owner or operator based on manufacturer recommendations, applicable
    regulations, fire protection and prevention codes, standard engineering codes and
    practices, or other requirements for the safe handling of flammable, ignitable,
    explosive, reactive, or hazardous materials.
     
    “Single-seal system” means a floating roof having one continuous seal. This seal
    may be vapor-mounted, liquid-mounted, or a metallic shoe seal.
     
    “Vapor-mounted seal” means a continuous seal that is mounted so that there is a
    vapor space between the hazardous waste in the unit and the bottom of the seal.
     
    “Volatile organic concentration” or “VO concentration” means the fraction by
    weight of organic compounds contained in a hazardous waste expressed in terms
    of parts per million (ppmw), as determined by direct measurement or by
    knowledge of the waste, in accordance with the requirements of Section 725.984.
    For the purpose of determining the VO concentration of a hazardous waste,
    organic compounds with a Henry’s law constant value of at least 0.1 mole-
    fraction-in-the-gas-phase/mole-fraction-in-the-liquid-phase (0.1 Y/X) (which can
    also be expressed as 1.8
    ×
    10
    -6
    atmospheres/gram-mole/m
    3
    ) at 25° C (77° F) must
    be included. Appendix F of this Part presents a list of compounds known to have
    a Henry’s law constant value less than the cutoff level.
     
    “Waste determination” means performing all applicable procedures in accordance
    with the requirements of Section 725.984 to determine whether a hazardous waste
    meets standards specified in this Subpart CC. Examples of a waste determination
    include performing the procedures in accordance with the requirements of Section
    725.984 to determine the average VO concentration of a hazardous waste at the
    point of waste origination, determining the average VO concentration of a
    hazardous waste at the point of waste treatment and comparing the results to the
    exit concentration limit specified for the process used to treat the hazardous
    waste, the organic reduction efficiency and the organic biodegradation efficiency
    for a biological process used to treat a hazardous waste and comparing the results
    to the applicable standards, or determining the maximum volatile organic vapor
    pressure for a hazardous waste in a tank and comparing the results to the
    applicable standards.
     
    “Waste stabilization process” means any physical or chemical process used to
    either reduce the mobility of hazardous constituents in a hazardous waste or
    eliminate free liquids as determined by Test Method 9095 9095B (Paint Filter
    Liquids Test) in “Test Methods for Evaluating Solid Waste, Physical/Chemical
    Methods,” USEPA publication number EPA-530/SW-846, incorporated by
    reference in 35 Ill. Adm. Code 720.111(a). A waste stabilization process includes
    mixing the hazardous waste with binders or other materials and curing the
    resulting hazardous waste and binder mixture. Other synonymous terms used to
    refer to this process are “waste fixation” or “waste solidification.” This does not
    include the addition of absorbent materials to the surface of a waste to absorb free

     
    623
    liquid without mixing, agitation, or subsequent curing.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.983 Standards: General
     
    a) This Section applies to the management of hazardous waste in tanks, surface
    impoundments, and containers subject to this Subpart CC.
     
    b) The owner or operator must control air pollutant emissions from each hazardous
    waste management unit in accordance with the standards specified in Sections
    725.985 through 725.988, as applicable to the hazardous waste management unit,
    except as provided for in subsection (c) of this Section.
     
    c) A tank, surface impoundment, or container is exempted from standards specified
    in Sections 725.985 through 725.988, provided that all hazardous waste placed in
    the waste management unit is one of the following:
     
    1) A tank, surface impoundment, or container for which all hazardous waste
    entering the unit has an average VO concentration at the point of waste
    origination of less than 500 parts per million by weight (ppmw). The
    average VO concentration must be determined by the procedures specified
    in Section 725.984(a). The owner or operator must review and update, as
    necessary, this determination at least once every 12 months following the
    date of the initial determination for the hazardous waste streams entering
    the unit;
     
    2) A tank, surface impoundment, or container for which the organic content
    of all the hazardous waste entering the waste management unit has been
    reduced by an organic destruction or removal process that achieves any
    one of the following conditions:
     
    A) The process removes or destroys the organics contained in the
    hazardous waste to such a level that the average VO concentration
    of the hazardous waste at the point of waste treatment is less than
    the exit concentration limit (Ct) established for the process. The
    average VO concentration of the hazardous waste at the point of
    waste treatment and the exit concentration limit for the process
    must be determined using the procedures specified in Section
    725.984(b);
     
    B) The process removes or destroys the organics contained in the
    hazardous waste to such a level that the organic reduction
    efficiency (R) for the process is equal to or greater than 95 percent,
    and the average VO concentration of the hazardous waste at the
    point of waste treatment is less than 100 ppmw. The organic

     
    624
    reduction efficiency for the process and the average VO
    concentration of the hazardous waste at the point of waste
    treatment must be determined using the procedures specified in
    Section 725.984(b);
     
    C) The process removes or destroys the organics contained in the
    hazardous waste to such a level that the actual organic mass
    removal rate (MR) for the process is equal to or greater than the
    required organic mass removal rate (RMR) established for the
    process. The required organic mass removal rate and the actual
    organic mass removal rate for the process must be determined
    using the procedures specified in Section 725.984(b);
     
    D) The process is a biological process that destroys or degrades the
    organics contained in the hazardous waste so that either of the
    following conditions is met:
     
    i) The organic reduction efficiency (R) for the process is
    equal to or greater than 95 percent, and the organic
    biodegradation efficiency (Rbio) for the process is equal to
    or greater than 95 percent. The organic reduction
    efficiency and the organic biodegradation efficiency for the
    process must be determined using the procedures specified
    in Section 725.984(b); and
     
    ii) The total actual organic mass biodegradation rate (MRbio)
    for all hazardous waste treated by the process is equal to or
    greater than the required organic mass removal rate (RMR).
    The required organic mass removal rate and the actual
    organic mass biodegradation rate for the process must be
    determined using the procedures specified in Section
    725.984(b);
     
    E) The process is one that removes or destroys the organics contained
    in the hazardous waste and meets all of the following conditions:
     
    i) From the point of waste origination through the point
    where the hazardous waste enters the treatment process, the
    hazardous waste is continuously managed in waste
    management units that use air emission controls in
    accordance with the standards specified in Section 725.985
    through Section 725.988, as applicable to the waste
    management unit;
     
    ii) From the point of waste origination through the point
    where the hazardous waste enters the treatment process,

     
    625
    any transfer of the hazardous waste is accomplished
    through continuous hard-piping or other closed system
    transfer that does not allow exposure of the waste to the
    atmosphere;
     
    BOARD NOTE: The USEPA considers a drain system that
    meets the requirements of federal subpart RR of 40 CFR
    63, “(National Emission Standards for Individual Drain
    Systems),” to be a closed system.
     
    iii) The average VO concentration of the hazardous waste at
    the point of waste treatment is less than the lowest average
    VO concentration at the point of waste origination
    determined for each of the individual hazardous waste
    streams entering the process or 500 ppmw, whichever value
    is lower. The average VO concentration of each individual
    hazardous waste stream at the point of waste origination
    must be determined using the procedures specified in
    Section 725.984(a). The average VO concentration of the
    hazardous waste at the point of waste treatment must be
    determined using the procedures specified in Section
    725.984(b);
     
    F) A process that removes or destroys the organics contained in the
    hazardous waste to a level such that the organic reduction
    efficiency (R) for the process is equal to or greater than 95 percent
    and the owner or operator certifies that the average VO
    concentration at the point of waste origination for each of the
    individual waste streams entering the process is less than 10,000
    ppmw. The organic reduction efficiency for the process and the
    average VO concentration of the hazardous waste at the point of
    waste origination must be determined using the procedures
    specified in Section 724.983(b) and Section 724.983(a),
    respectively;
     
    G) A hazardous waste incinerator for which either of the following
    conditions is true:
     
    i) The owner or operator has been issued a final permit under
    35 Ill. Adm. Code 702, 703, and 705 that implements the
    requirements of Subpart O of 35 Ill. Adm. Code 724; or
     
    ii) The owner or operator has designed and operates the
    incinerator in accordance with the interim status
    requirements of Subpart O of this Part;
     

     
    626
    H) A boiler or industrial furnace for which either of the following
    conditions is true:
     
    i) The owner or operator has been issued a final permit under
    35 Ill. Adm. Code 702, 703, and 705 that implements the
    requirements of Subpart H of 35 Ill. Adm. Code 726; or
     
    ii) The owner or operator has designed and operates the
    industrial furnace or incinerator in accordance with the
    interim status requirements of Subpart H of 35 Ill. Adm.
    Code 726; and
     
    I) For the purpose of determining the performance of an organic
    destruction or removal process in accordance with the conditions
    in each of subsections (c)(2)(A) through (c)(2)(F) of this Section,
    the owner or operator must account for VO concentrations
    determined to be below the limit of detection of the analytical
    method by using the following VO concentration:
     
    i) If Method 25D (Determination of the Volatile Organic
    Concentration of Waste Samples) in appendix A to 40 CFR
    60, appendix A (Test Methods), incorporated by reference
    in 35 Ill. Adm. Code 720.111(b), is used for the analysis,
    one-half the blank value determined in the method at
    Section 4.4 of Method 25D or a value of 25 ppmw,
    whichever is less; and
     
    ii) If any other analytical method is used, one-half the sum of
    the limits of detection established for each organic
    constituent in the waste that has a Henry’s law constant
    value at least 0.1 mole-fraction-in-the-gas-phase/mole-
    fraction-in-the-liquid-phase (0.1 Y/X) (which can also be
    expressed as 1.8 x 10
    -6
    atmospheres/gram-mole/m
    3
    ) at 25°
    C;
     
    3) A tank or surface impoundment used for biological treatment of hazardous
    waste in accordance with the requirements of subsection (c)(2)(D) of this
    Section;
     
    4) A tank, surface impoundment, or container for which all hazardous waste
    placed in the unit fulfills either of the following two conditions:
     
    A) It meets the numerical concentration limits for organic hazardous
    constituents, applicable to the hazardous waste, as specified in
    Table T to 35 Ill. Adm. Code 728; or
     

     
    627
    B) The organic hazardous constituents in the waste have been treated
    by the treatment technology established by USEPA for the waste,
    as set forth in 35 Ill. Adm. Code 728.142(a), or treated by an
    equivalent method of treatment approved by the Agency pursuant
    to 35 Ill. Adm. Code 728.142(b); or
     
    5) A tank used for bulk feed of hazardous waste to a waste incinerator, and
    all of the following conditions are met:
     
    A) The tank is located inside an enclosure vented to a control device
    that is designed and operated in accordance with all applicable
    requirements specified under federal subpart FF of 40 CFR 61,
    “(National Emission Standards for Benzene Waste Operations),”
    incorporated by reference in 35 Ill. Adm. Code 720.111(a)
    720.111(b), for a facility at which the total annual benzene
    quantity from the facility waste is equal to or greater than 10
    megagrams (11 tons) per year;
     
    B) The enclosure and control device serving the tank were installed
    and began operation prior to November 25, 1996; and
     
    C) The enclosure is designed and operated in accordance with the
    criteria for a permanent total enclosure as specified in “Procedure
    T--Criteria for and Verification of a Permanent or Temporary Total
    Enclosure” under appendix B to 40 CFR 52.741, appendix B
    (VOM Measurement Techniques for Capture Efficiency),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b). The
    enclosure may have permanent or temporary openings to allow
    worker access; passage of material into or out of the enclosure by
    conveyor, vehicles, or other mechanical or electrical equipment; or
    to direct air flow into the enclosure. The owner or operator must
    perform the verification procedure for the enclosure as specified in
    Section 5.0 to “Procedure T--Criteria for and Verification of a
    Permanent or Temporary Total Enclosure” annually.
     
    d) The Agency may at any time perform or request that the owner or operator
    perform a waste determination for a hazardous waste managed in a tank, surface
    impoundment, or container that is exempted from using air emission controls
    under the provisions of this Section as follows:
     
    1) The waste determination for average VO concentration of a hazardous
    waste at the point of waste origination must be performed using direct
    measurement in accordance with the applicable requirements of Section
    725.984(a). The waste determination for a hazardous waste at the point of
    waste treatment must be performed in accordance with the applicable
    requirements of Section 725.984(b);

     
    628
     
    2) In performing a waste determination pursuant to subsection (d)(1) of this
    Section, the sample preparation and analysis must be conducted as
    follows:
     
    A) In accordance with the method used by the owner or operator to
    perform the waste analysis, except in the case specified in
    subsection (d)(2)(B) of this Section; and
     
    B) If the Agency determines that the method used by the owner or
    operator was not appropriate for the hazardous waste managed in
    the tank, surface impoundment, or container, then the Agency may
    choose an appropriate method;
     
    3) Where the owner or operator is requested to perform the waste
    determination, the Agency may elect to have an authorized representative
    observe the collection of the hazardous waste samples used for the
    analysis;
     
    4) Where the results of the waste determination performed or requested by
    the Agency do not agree with the results of a waste determination
    performed by the owner or operator using knowledge of the waste, then
    the results of the waste determination performed in accordance with the
    requirements of subsection (d)(1) of this Section must be used to establish
    compliance with the requirements of this Subpart CC; and
     
    5) Where the owner or operator has used an averaging period greater than
    one hour for determining the average VO concentration of a hazardous
    waste at the point of waste origination, the Agency may elect to establish
    compliance with this Subpart CC by performing or requesting that the
    owner or operator perform a waste determination using direct
    measurement, based on waste samples collected within a 1-hour period as
    follows:
     
    A) The average VO concentration of the hazardous waste at the point
    of waste origination must be determined by direct measurement in
    accordance with the requirements of Section 725.984(a);
     
    B) Results of the waste determination performed or requested by the
    Agency showing that the average VO concentration of the
    hazardous waste at the point of waste origination is equal to or
    greater than 500 ppmw must constitute noncompliance with this
    Subpart CC, except in a case as provided for in subsection
    (d)(4)(C) of this Section; and
     
    C) Where the average VO concentration of the hazardous waste at the

     
    629
    point of waste origination previously has been determined by the
    owner or operator using an averaging period greater than one hour
    to be less than 500 ppmw but because of normal operating process
    variations the VO concentration of the hazardous waste determined
    by direct measurement for any given 1-hour period may be equal
    to or greater than 500 ppmw, information that was used by the
    owner or operator to determine the average VO concentration of
    the hazardous waste (e.g., test results, measurements, calculations,
    and other documentation) and recorded in the facility records in
    accordance with the requirements of Sections 725.984(a) and
    725.990 must be considered by the Agency together with the
    results of the waste determination performed or requested by the
    Agency in establishing compliance with this Subpart CC.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.984 Waste Determination Procedures
     
    a) Waste determination procedure for volatile organic (VO) concentration of a
    hazardous waste at the point of waste origination.
     
    1) An owner or operator must determine the average VO concentration at the
    point of waste origination for each hazardous waste placed in a waste
    management unit exempted under the provisions of Section 725.983(c)(1)
    from using air emission controls in accordance with standards specified in
    Section 725.985 through Section 725.988, as applicable to the waste
    management unit.
     
    A) An owner or operator must make an initial determination of the
    average VO concentration of the waste stream before the first time
    any portion of the material in the hazardous waste stream is placed
    in a waste management unit exempted under the provisions of
    Section 725.983(c)(1) from using air emission controls. Thereafter,
    an owner or operator must make an initial determination of the
    average VO concentration of the waste stream for each averaging
    period that a hazardous waste is managed in the unit.
     
    B) An owner or operator must perform a new waste determination
    whenever changes to the source generating the waste stream are
    reasonably likely to cause the average VO concentration of the
    hazardous waste to increase to a level that is equal to or greater than
    the VO concentration limits specified in Section 725.983(c)(1).
     
    2) For a waste determination that is required by subsection (a)(1) of this
    Section, the average VO concentration of a hazardous waste at the point of
    waste origination must be determined using either direct measurement, as

     
    630
    specified in subsection (a)(3) of this Section, or by knowledge of the
    waste, as specified in subsection (a)(4) of this Section.
     
    3) Direct measurement to determine average VO concentration of a
    hazardous waste at the point of waste origination.
     
    A) Identification. The owner or operator must identify and record the
    point of waste origination for the hazardous waste.
     
    B) Sampling. Samples of the hazardous waste stream must be
    collected at the point of waste origination in such a manner that
    volatilization of organics contained in the waste and in the
    subsequent sample is minimized and an adequately representative
    sample is collected and maintained for analysis by the selected
    method.
     
    i) The averaging period to be used for determining the
    average VO concentration for the hazardous waste stream
    on a mass-weighted average basis must be designated and
    recorded. The averaging period can represent any time
    interval that the owner or operator determines is
    appropriate for the hazardous waste stream but must not
    exceed one year.
     
    ii) A sufficient number of samples, but no fewer than four
    samples, must be collected for a hazardous waste
    determination. All of the samples for a given waste
    determination must be collected within a one-hour period.
    The average of the four or more sample results constitutes a
    waste determination for the waste stream. One or more
    waste determinations may be required to represent the
    complete range of waste compositions and quantities that
    occur during the entire averaging period due to normal
    variations in the operating conditions for the source or
    process generating the hazardous waste stream. Examples
    of such normal variations are seasonal variations in waste
    quantity or fluctuations in ambient temperature.
     
    iii) All samples must be collected and handled in accordance
    with written procedures prepared by the owner or operator
    and documented in a site sampling plan. This plan must
    describe the procedure by which representative samples of
    the hazardous waste stream are collected so that a
    minimum loss of organics occurs throughout the sample
    collection and handling process, and by which sample
    integrity is maintained. A copy of the written sampling

     
    631
    plan must be maintained on-site in the facility operating
    records. An example of an acceptable sampling plan
    includes a plan incorporating sample collection and
    handling procedures in accordance with the requirements
    specified in “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods,” USEPA Publication SW-
    846, incorporated by reference in 35 Ill. Adm. Code
    720.111(a), or in Method 25D (Determination of the
    Volatile Organic Concentration of Waste Samples) in
    appendix A to 40 CFR 60, appendix A (Test Methods),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    iv) Sufficient information, as specified in the “site sampling
    plan” required under subsection (a)(3)(B)(iii) of this Section,
    must be prepared and recorded to document the waste
    quantity represented by the samples and, as applicable, the
    operating conditions for the source or process generating the
    hazardous waste represented by the samples.
     
    C) Analysis. Each collected sample must be prepared and analyzed in
    accordance with one or more of the methods listed in subsections
    (a)(3)(C)(i) through (a)(3)(C)(ix) of this Section, including the
    appropriate quality assurance and quality control (QA/QC) checks
    and use of target compounds for calibration. If Method 25D in 40
    CFR 60, appendix A, incorporated by reference in 35 Ill. Adm.
    Code 720.111(b), is not used, then one or more methods should be
    chosen that are appropriate to ensure that the waste determination
    for the total concentration of volatile organic constituents or using
    one or more methods when the individual organic compound
    concentrations are identified and summed and the summed waste
    concentration accounts for and reflects all organic compounds in
    the waste with Henry’s law constant values at least 0.1 mole-
    fraction-in-the-gas-phase/mole-fraction-in-the-liquid-phase (0.1
    Y/X) (which can also be expressed as 1.8
    ×
    10
    -6
    atmospheres/gram-
    mole/m
    3
    ) at 25° C (77° F). Each of the analytical methods listed in
    subsections (a)(3)(C)(ii) through (a)(3)(C)(vii) of this Section has
    an associated list of approved chemical compounds for which
    USEPA considers the method appropriate for measurement. If an
    owner or operator uses USEPA Method 624, 625, 1624, or 1625 in
    40 CFR 136, appendix A, incorporated by reference in 35 Ill. Adm.
    Code 720.111(b), to analyze one or more compounds that are not
    on that method’s published list, the Alternative Test Procedure
    contained in 40 CFR 136.4 and 136.5, incorporated by reference in
    35 Ill. Adm. Code 720.111(b), must be followed. If an owner or
    operator uses USEPA Method 8260 or 8270 in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA

     
    632
    Publication SW-846, incorporated by reference in 35 Ill. Adm.
    Code 720.111(a), to analyze one or more compounds that are not
    on that method’s published list, the procedures in subsection
    (a)(3)(C)(viii) of this Section must be followed. At the owner’s or
    operator’s discretion, the owner or operator may adjust test data
    measured by a any appropriate method other than Method 25D to
    the corresponding average VO concentration value that would
    have been obtained, had the waste samples been analyzed using
    Method 25D to discount any contribution to the total volatile
    organic concentration that is a result of including a compound with
    a Henry’s law constant value of less than 0.1 Y/X at 25° C (77° F).
    To adjust these data, the measured concentration of each individual
    chemical constituent contained in the waste is multiplied by the
    constituent-specific adjustment factor (fm25D). If the owner or
    operator elects to adjust test data, the adjustment must be made to all
    individual chemical constituents with a Henry's law constant value
    greater than or equal to 0.1 Y/X at 25° C contained in the waste.
    Constituent-specific adjustment factors (fm25D) can be obtained by
    contacting the USEPA, Waste and Chemical Processes Group,
    Office of Air Quality Planning and Standards, Research Triangle
    Park, NC 27711. Other test methods may be used if they meet the
    requirements in subsection (a)(3)(C)(i) or (a)(3)(C)(ii) of this
    Section and provided the requirement is met to reflect all organic
    compounds in the waste with Henry’s law constant values greater
    than or equal to 0.1 Y/X (which can also be expressed as 1.8 x 10
    -6
     
    atmospheres/gram-mole/m3) at 25 degrees Celsius.
     
    i)
    Method 25D in 40 CFR 60, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    ii)
    Method 624 in 40 CFR 136, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    iii)
    Method 625 in 40 CFR 136, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b). Perform
    corrections to the compounds for which the analysis is
    being conducted based on the “accuracy as recovery” using
    the factors in Table 7 of the method.
     
    iv)
    Method 1624 in 40 CFR 136, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    v)
    Method 1625 in 40 CFR 136, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    vi)
    Method 8260 in “Test Methods for Evaluating Solid Waste,

     
    633
    Physical/Chemical Methods,” USEPA Publication SW-
    846, incorporated by reference in 35 Ill. Adm. Code
    720.111(a). Maintain a formal quality assurance program
    consistent with the requirements of Method 8260. The
    quality assurance program must include the elements set
    forth in subsection (a)(3)(F) of this Section.
     
    vii)
    Method 8270 in “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods,” USEPA Publication SW-
    846, incorporated by reference in 35 Ill. Adm. Code
    720.111(a). Maintain a formal quality assurance program
    consistent with the requirements of Method 8270. The
    quality assurance program must include the elements set
    forth in subsection (a)(3)(F) of this Section.
     
    viii)
    Any other USEPA standard method that has been validated
    in accordance with “Alternative Validation Procedure for
    USEPA Waste and Wastewater Methods,” 40 CFR 63,
    appendix D, incorporated by reference in 35 Ill. Adm. Code
    720.111(b). As an alternative, other USEPA standard
    methods may be validated by the procedure specified in
    subsection (a)(3)(C)(ix) of this Section.
     
    ix)
    Any other analysis method that has been validated in
    accordance with the procedures specified in Section 5.1 or
    Section 5.3, and the corresponding calculations in Section
    6.1 or Section 6.3, of Method 301 in 40 CFR 63, appendix
    A, incorporated by reference in 35 Ill. Adm. Code
    720.111(b). The data are acceptable if they meet the
    criteria specified in Section 6.1.5 or Section 6.3.3 of
    Method 301. If correction is required under Section 6.3.3
    of Method 301, the data are acceptable if the correction
    factor is within the range 0.7 to 1.30. Other Sections of
    Method 301 are not required.
     
    i) Any USEPA standard method that has been validated in
    accordance with appendix D to 40 CFR 63 (Alternative
    Validation Procedure for EPA Waste and Wastewater
    Methods), incorporated by reference in 35 Ill. Adm. Code
    720.111(b); or
     
    ii) Any other anaysis method that has been validated in
    accordance with the procedures specified in Section 5.1 or
    5.3, and the corresponding calculations in Section 6.1 or
    Section 6.3, of Method 301 (Field Validation of Pollutant
    Measurement Methods from Various Waste Media) in

     
    634
    appendix A to 40 CFR 63 (Test Methods), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b). The data are
    acceptable if the meet the criteria specified in Section 6.1.5
    or Section 6.3.3 of Method 301. If correction is required
    under Section 6.3.3 of Method 301, the data are acceptable
    if the correction factor is within the range 0.7 to 1.30.
    Other sections of Method 301 are not required.
     
    D) Calculations.
     
    i) The average VO concentration ( C ) on a mass-weighted
    basis must be calculated by using the results for all waste
    determinations conducted in accordance with subsections
    (a)(3)(B) and (a)(3)(C) of this Section and the following
    equation:
     
    C=
    1
    Q
    x
    n
    i = 1
    (Q x C )
    T
    i
    i
      
     
    Where:
     
    C = Average VO concentration of the hazardous
    waste at the point of waste origination on a
    mass-weighted basis, in ppmw;
     
    i = Individual waste determination “i” of the
    hazardous waste;
     
    n = Total number of waste determinations of the
    hazardous waste conducted for the
    averaging period (not to exceed one year);
     
    Qi = Mass quantity of the hazardous waste stream
    represented by Ci, in kg/hr;
     
    QT = Total mass quantity of the hazardous waste
    during the averaging period, in kg/hr; and
     
    Ci = Measured VO concentration of waste
    determination “i,” as determined in
    accordance with subsection (a)(3)(C) of this
    Section (i.e., the average of the four or
    more samples specified in subsection
    (a)(3)(B)(ii) of this Section), in ppmw.

     
    635
     
    ii) For the purpose of determining Ci, for individual waste
    samples analyzed in accordance with subsection (a)(3)(C)
    of this Section, the owner or operator must account for VO
    concentrations determined to be below the limit of
    detection of the analytical method by using the VO
    concentration determined according to subsection (a)(3)(G)
    of this Section.
     
    E) Provided that the test method is appropriate for the waste as
    required under subsection (a)(3)(C) of this Section, the Agency
    must determine compliance based on the test method used by the
    owner or operator as recorded pursuant to Section 725.990(f)(1).
     
    F) The quality assurance program elements required under
    subsections (a)(3)(C)(vi) and (a)(3)(C)(vii) of this Section are as
    follows:
     
    i) Documentation of site-specific procedures to minimize the
    loss of compounds due to volatilization, biodegradation,
    reaction, or sorption during the sample collection, storage,
    preparation, introduction, and analysis steps.
     
    ii) Measurement of the overall accuracy and precision of the
    specific procedures.
     
    BOARD NOTE: Subsections (a)(3)(F)(i) and (a)(3)(F)(ii) are
    derived from 40 CFR 265.984(a)(3)(iii)(F)(1), (a)(3)(iii)(F)(2),
    (a)(3)(iii)(G)(1), and (a)(3)(iii)(G)(2), which the Board has
    codified here to comport with Illinois Administrative Code format
    requirements.
     
    G) VO concentrations below the limit of detection must be considered
    to be as follows:
     
    i) If Method 25D in 40 CFR 60, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b), is used for the
    analysis, the VO concentration must be considered to be
    one-half the blank value determined in the method at
    Section 4.4 of Method 25D in 40 CFR 60, appendix A.
     
    ii) If any other analytical method is used, the VO
    concentration must be considered to be one-half the sum of
    the limits of detection established for each organic
    constituent in the waste that has a Henry’s law constant
    value at least 0.1 mole-fraction-in-the-gas-phase/mole-

     
    636
    fraction-in-the-liquid-phase (0.1 Y/X) (which can also be
    expressed as 1.8 x 10
    -6
    atmospheres/gram-mole/m
    3
    ) at 25°
    C.
     
    BOARD NOTE: Subsections (a)(3)(G)(i) and (a)(3)(G)(ii) are
    derived from 40 CFR 265.984(a)(3)(iv)(A)(1) and (a)(3)(iv)(A)(2),
    which the Board has codified here to comport with Illinois
    Administrative Code format requirements.
     
    4) Use of owner or operator knowledge to determine average VO
    concentration of a hazardous waste at the point of waste origination.
     
    A) Documentation must be prepared that presents the information
    used as the basis for the owner’s or operator’s knowledge of the
    hazardous waste stream’s average VO concentration. Examples of
    information that may be used as the basis for knowledge include
    the following: material balances for the source or process
    generating the hazardous waste stream; constituent-specific
    chemical test data for the hazardous waste stream from previous
    testing that are still applicable to the current waste stream;
    previous test data for other locations managing the same type of
    waste stream; or other knowledge based on information included in
    manifests, shipping papers, or waste certification notices.
     
    B) If test data are used as the basis for knowledge, then the owner or
    operator must document the test method, sampling protocol, and
    the means by which sampling variability and analytical variability
    are accounted for in the determination of the average VO
    concentration. For example, an owner or operator may use organic
    concentration test data for the hazardous waste stream that are
    validated in accordance with Method 301 in 40 CFR 63, appendix
    A, incorporated by reference in 35 Ill. Adm. Code 720.111(b), as
    the basis for knowledge of the waste.
     
    C) An owner or operator using chemical constituent-specific
    concentration test data as the basis for knowledge of the hazardous
    waste may adjust the test data to the corresponding average VO
    concentration value that would have been obtained had the waste
    samples been analyzed using Method 25D in 40 CFR 60, appendix
    A, incorporated by reference in 35 Ill. Adm. Code 720.111(b). To
    adjust these data, the measured concentration for each individual
    chemical constituent contained in the waste is multiplied by the
    appropriate constituent-specific adjustment factor (fm25D).
     
    D) In the event that the Agency and the owner or operator disagree on
    a determination of the average VO concentration for a hazardous

     
    637
    waste stream using knowledge, then the results from a
    determination of average VO concentration using direct
    measurement, as specified in subsection (a)(3) of this Section,
    must be used to establish compliance with the applicable
    requirements of this Subpart CC. The Agency may perform or
    request that the owner or operator perform this determination using
    direct measurement. The owner or operator may choose one or
    more appropriate methods to analyze each collected sample in
    accordance with the requirements of subsection (a)(3)(C) of this
    Section.
     
    b) Waste determination procedures for treated hazardous waste.
     
    1) An owner or operator must perform the applicable waste determination for
    each treated hazardous waste placed in a waste management unit
    exempted under the provisions of Section 725.983(c)(2)(A) through
    (c)(2)(F) from using air emission controls in accordance with the
    standards specified in Sections 725.985 through 725.988, as applicable to
    the waste management unit.
     
    A) An owner or operator must make an initial determination of the
    average VO concentration of the waste stream before the first time
    any portion of the material in the treated waste stream is placed in
    the waste management unit exempt under Section 725.983(c)(2),
    (c)(3), or (c)(4) from using air emission controls. Thereafter, an
    owner or operator must update the information used for the waste
    determination at least once every 12 months following the date of
    the initial waste determination.
     
    B) An owner or operator must perform a new waste determination
    whenever changes to the process generating or treating the waste
    stream are reasonably likely to cause the average VO concentration
    of the hazardous waste to increase to such a level that the applicable
    treatment conditions specified in Section 725.983 (c)(2), (c)(3), or
    (c)(4) are not achieved.
     
    2) The owner or operator must designate and record the specific provision in
    Section 725.983(c)(2) under which the waste determination is being
    performed. The waste determination for the treated hazardous waste must
    be performed using the applicable procedures specified in subsections
    (b)(3) through (b)(9) of this Section.
     
    3) Procedure to determine the average VO concentration of a hazardous
    waste at the point of waste treatment.
     
    A) Identification. The owner or operator must identify and record the

     
    638
    point of waste treatment for the hazardous waste.
     
    B) Sampling. Samples of the hazardous waste stream must be
    collected at the point of waste treatment in such a manner that
    volatilization of organics contained in the waste and in the
    subsequent sample is minimized and an adequately representative
    sample is collected and maintained for analysis by the selected
    method.
     
    i) The averaging period to be used for determining the
    average VO concentration for the hazardous waste stream
    on a mass-weighted average basis must be designated and
    recorded. The averaging period can represent any time
    interval that the owner or operator determines is
    appropriate for the hazardous waste stream but must not
    exceed one year.
     
    ii) A sufficient number of samples, but no fewer than four
    samples, must be collected and analyzed for a hazardous
    waste determination. All of the samples for a given waste
    determination must be collected within a one-hour period.
    The average of the four or more sample results constitutes a
    waste determination for the hazardous waste stream. One
    or more waste determinations may be required to represent
    the complete range of waste compositions and quantities
    that occur during the entire averaging period due to normal
    variations in the operating conditions for the process
    generating or treating the hazardous waste stream.
    Examples of such normal variations are seasonal variations
    in waste quantity or fluctuations in ambient temperature.
     
    iii) All samples must be collected and handled in accordance
    with written procedures prepared by the owner or operator
    and documented in a site sampling plan. This plan must
    describe the procedure by which representative samples of
    the hazardous waste stream are collected so that a
    minimum loss of organics occurs throughout the sample
    collection and handling process, and by which sample
    integrity is maintained. A copy of the written sampling
    plan must be maintained on-site in the facility operating
    records. An example of an acceptable sampling plan
    includes a plan incorporating sample collection and
    handling procedures in accordance with the requirements
    specified in “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods,” USEPA Publication No. SW-
    846, incorporated by reference in 35 Ill. Adm. Code

     
    639
    720.111(a), or sample collection and handling procedures
    for a total organic constituent concentration may be found
    in Method 25D in 40 CFR 60, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    iv) Sufficient information, as specified in the “site sampling
    plan” required under subsection (a)(3)(B)(iii) of this Section,
    must be prepared and recorded to document the waste
    quantity represented by the samples and, as applicable, the
    operating conditions for the process treating the hazardous
    waste represented by the samples.
     
    C) Analysis. Each collected sample must be prepared and analyzed in
    accordance with one or more of the methods listed in subsections
    (b)(3)(C)(i) through (b)(3)(C)(ix) of this Section, including
    appropriate quality assurance and quality control (QA/QC) checks
    and use of target compounds for calibration Method 25D for the
    total concentration of volatile organic constituents or using one or
    more methods when the individual organic compound
    concentrations are identified and summed, and the summed waste
    concentration accounts for and reflects all organic compounds in
    the waste with Henry’s law constant values at least 0.1 mole-
    fraction-inpthe-gas-phase/mole-fraction-in-the-liquid-phase (0.1
    Y/X) (which can also be expressed as 1.8 × 10
    -6
     
    atmospheres/gram-mole/m
    3
    ) at 25°C (75° F). When the owner or
    operator is making a waste determination for a treated hazardous
    waste that is to be compared to an average VO concentration at the
    point of waste origination or the point of waste entry to the
    treatment system, to determine if the conditions of 35 Ill. Adm.
    Code 724.982(c)(2)(A) through (c)(2)(F) or Section
    725.983(c)(2)(A) through (c)(2)(F) are met, then the waste samples
    must be prepared and analyzed using the same method or methods
    as were used in making the initial waste determinations at the point
    of waste origination or at the point of entry to the treatment
    system. If Method 25D in 40 CFR 60, appendix A is not used,
    then one or more methods should be chosen that are appropriate to
    ensure that the waste determination accounts for and reflects all
    organic compounds in the waste with Henry’s law constant values
    at least 0.1 mole-fraction-in-the-gas-phase/mole-fraction-in-the-
    liquid-phase (0.1 Y/X) (which can also be expressed as 1.8
    ×
    10
    -6
     
    atmospheres/gram-mole/m
    3
    ) at 25 degrees Celsius. Each of the
    analytical methods listed in subsections (b)(3)(C)(ii) through
    (b)(3)(C)(vii) of this Section has an associated list of approved
    chemical compounds, for which USEPA considers the method
    appropriate for measurement. If an owner or operator uses USEPA
    Method 624, 625, 1624, or 1625 in 40 CFR 136, appendix A,

     
    640
    incorporated by reference in 35 Ill. Adm. Code 720.111(b), to
    analyze one or more compounds that are not on that method’s
    published list, the Alternative Test Procedure contained in 40 CFR
    136.4 and 136.5, incorporated by reference in 35 Ill. Adm. Code
    720.111(b), must be followed. If an owner or operator uses
    USEPA Method 8260 or 8270 in “Test Methods for Evaluating
    Solid Waste, Physical/Chemical Methods,” USEPA Publication
    SW-846, incorporated by reference in 35 Ill. Adm. Code
    720.111(a), to analyze one or more compounds that are not on that
    method’s published list, the procedures in subsection
    (b)(3)(C)(viii) of this Section must be followed. At the owner’s or
    operator’s discretion, the owner or operator may adjust test data
    measured obtained by a any appropriate method other than Method
    25D to the corresponding average VO concentration value that
    would have been obtained, had the waste samples been analyzed
    using Method 25D to discount any contribution to the total volatile
    organic concentration that is a result of including a compound with
    a Henry’s law constant value less than 0.1 Y/X at 25° C. To adjust
    these data, the measured concentration of each individual chemical
    constituent contained in the waste is multiplied by the constituent-
    specific adjustment factor (fm25D). If the owner or operator elects to
    adjust test data, the adjustment must be made to all individual
    chemical constituents with a Henry's law constant value greater than
    or equal to 0.1 Y/X at 25° C contained in the waste. Constituent-
    specific adjustment factors (fm25D) can be obtained by contacting
    the USEPA, Waste and Chemical Processes Group, Office of Air
    Quality Planning and Standards, Research Triangle Park, NC
    27711. Other test methods may be used if they meet the
    requirements in subsection (a)(3)(C)(i) or (a)(3)(C)(ii) of this
    Section and provided the requirement is met to reflect all organic
    compounds in the waste with Henry’s law constant values greater
    than or equal to 0.1 Y/X (which can also be expressed as 1.8 x 10
    -6
     
    atmospheres/gram-mole/m3) at 25° C.
     
    i)
    Method 25D in 40 CFR 60, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    ii)
    Method 624 in 40 CFR 136, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    iii)
    Method 625 in 40 CFR 136, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b). Perform
    corrections to the compounds for which the analysis is
    being conducted based on the “accuracy as recovery” using
    the factors in Table 7 of the method.
     

     
    641
    iv)
    Method 1624 in 40 CFR 136, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    v)
    Method 1625 in 40 CFR 136, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    vi)
    Method 8260 in “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods,” USEPA Publication SW-
    846, incorporated by reference in 35 Ill. Adm. Code
    720.111(a). Maintain a formal quality assurance program
    consistent with the requirements of Method 8260. The
    quality assurance program must include the elements set
    forth in subsection (b)(3)(E) of this Section.
     
    vii)
    Method 8270 in “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods,” USEPA Publication SW-
    846, incorporated by reference in 35 Ill. Adm. Code
    720.111(a). Maintain a formal quality assurance program
    consistent with the requirements of Method 8270. The
    quality assurance program must include the elements set
    forth in subsection (b)(3)(E) of this Section.
     
    viii)
    Any other USEPA standard method that has been validated
    in accordance with “Alternative Validation Procedure for
    EPA Waste and Wastewater Methods,” 40 CFR 63,
    appendix D, incorporated by reference in 35 Ill. Adm. Code
    720.111(b). As an alternative, other USEPA standard
    methods may be validated by the procedure specified in
    subsection (b)(3)(C)(ix) of this Section.
     
    ix)
    Any other analysis method that has been validated in
    accordance with the procedures specified in Section 5.1 or
    Section 5.3, and the corresponding calculations in Section
    6.1 or Section 6.3, of Method 301 in 40 CFR 63, appendix
    A, incorporated by reference in 35 Ill. Adm. Code
    720.111(b). The data are acceptable if they meet the
    criteria specified in Section 6.1.5 or Section 6.3.3 of
    Method 301. If correction is required under Section 6.3.3
    of Method 301, the data are acceptable if the correction
    factor is within the range 0.7 to 1.30. Other Sections of
    Method 301 are not required.
     
    i) Any USEPA standard method that has been validated in
    accordance with appendix D to 40 CFR 63; or
     
    ii) Any other anaysis method that has been validated in

     
    642
    accordance with the procedures specified in Section 5.1 or
    5.3, and the corresponding calculations in Section 6.1 or
    Section 6.3, of Method 301. The data are acceptable if the
    meet the criteria specified in Section 6.1.5 or Section 6.3.3
    of Method 301. If correction is required under Section
    6.3.3 of Method 301, the data are acceptable if the
    correction factor is within the range 0.7 to 1.30. Other
    sections of Method 301 are not required.
     
    D) Calculations. The average VO concentration ( C ) on a mass-
    weighted basis must be calculated by using the results for all
    samples analyzed in accordance with subsection (b)(3)(C) of this
    Section and the following equation:
     
    C=
    1
    Q
    x
    n
    i = 1
    (Q xC )
    T
    i
    i
      
     
    Where:
     
    C = Average VO concentration of the hazardous waste
    at the point of waste treatment on a mass-weighted
    basis, in ppmw;
     
    i = Individual determination “i” of the hazardous
    waste;
     
    n = Total number of waste determinations of the
    hazardous waste collected for the averaging period
    (not to exceed one year);
     
    Qi = Mass quantity of the hazardous waste stream
    represented by Ci, in kg/hr;
     
    QT = Total mass quantity of hazardous waste during the
    averaging period, in kg/hr; and
     
    Ci = Measured VO concentration of waste
    determinations “i,” as determined in accordance
    with the requirements of subsection (b)(3)(C) of this
    Section (i.e., the average of the four or more
    samples specified in subsection (b)(3)(B)(ii) of this
    Section), in ppmw.
     
    E) Provided that the test method is appropriate for the waste as

     
    643
    required under subsection (b)(3)(C) of this Section, compliance
    must be determined based on the test method used by the owner or
    operator as recorded pursuant to Section 725.990(f)(1).
     
    4) Procedure to determine the exit concentration limit (Ct) for a treated
    hazardous waste.
     
    A) The point of waste origination for each hazardous waste treated by
    the process at the same time must be identified.
     
    B) If a single hazardous waste stream is identified in subsection
    (b)(4)(A) of this Section, then the exit concentration limit (Ct)
    must be 500 ppmw.
     
    C) If more than one hazardous waste stream is identified in subsection
    (b)(4)(A) of this Section, then the average VO concentration of
    each hazardous waste stream at the point of waste origination must
    be determined in accordance with the requirements of subsection
    (a) of this Section. The exit concentration limit (Ct) must be
    calculated by using the results determined for each individual
    hazardous waste stream and the following equation:
     
    t
    x
    x
    y
    x
    y
    C
    =
    m
    x = 1
    (Q
    xC
    )+
    n
    y = 1
    (Q
    x500ppmw)
    m
    x = 1
    Q
    +
    n
    y = 1
    Q
    ∑∑
    ∑∑
     
     
    Where:
     
    Ct = Exit concentration limit for treated hazardous waste,
    in ppmw;
     
    x = Individual hazardous waste stream “x” that has an
    average VO concentration less than 500 ppmw at
    the point of waste origination, as determined in
    accordance with the requirements of subsection (a)
    of this Section;
     
    y = Individual hazardous waste stream “y” that has an
    average VO concentration equal to or greater than
    500 ppmw at the point of waste origination, as
    determined in accordance with the requirements of

     
    644
    subsection (a) of this Section;
     
    m = Total number of “x” hazardous waste streams
    treated by process;
     
    n = Total number of “y” hazardous waste streams
    treated by process;
     
    Qx = Annual mass quantity of hazardous waste stream
    “x,” in kg/yr;
     
    Qy = Annual mass quantity of hazardous waste stream
    “y,” in kg/yr; and
     
    C
    x
    = Average VO concentration of hazardous waste
    stream “x” at the point of waste origination, as
    determined in accordance with the requirements of
    subsection (a) of this Section, in ppmw.
     
    5) Procedure to determine the organic reduction efficiency (R) for a treated
    hazardous waste.
     
    A) The organic reduction efficiency (R) for a treatment process must
    be determined based on results for a minimum of three consecutive
    runs.
     
    B) All hazardous waste streams entering the process and all hazardous
    waste streams exiting the treatment process must be identified.
    The owner or operator must prepare a sampling plan for measuring
    these streams that accurately reflects the retention time of the
    hazardous waste in the process.
     
    C) For each run, information must be determined for each hazardous
    waste stream identified in subsection (b)(5)(B) of this Section,
    using the following procedures:
     
    i) The mass quantity of each hazardous waste stream entering
    the process (Qb) and the mass quantity of each hazardous
    waste stream exiting the process (Qa) must be determined;
    and
     
    ii) The average VO concentration at the point of waste
    origination of each hazardous waste stream entering the
    process (Cb) during the run must be determined in
    accordance with the requirements of subsection (a)(3) of
    this Section. The average VO concentration at the point of

     
    645
    waste treatment of each hazardous waste stream exiting the
    process (Ca) during the run must be determined in
    accordance with the requirements of subsection (b)(3) of
    this Section.
     
    D) The waste volatile organic mass flow entering the process (Eb) and
    the waste volatile organic mass flow exiting the process (Ea) must
    be calculated by using the results determined in accordance with
    subsection (b)(5)(C) of this Section and the following equations:
     
    b
    6
    bj
    bj
    E
    =
    1
    10
    m
    j=1
    (Q
    xC
    )
      
     
    a
    6
    aj
    aj
    E
    =
    1
    10
    m
    j = 1
    (Q
    xC
    )
      
     
    Where:
     
    Ea = Waste volatile organic mass flow exiting the
    process, in kg/hr;
     
    Eb = Waste volatile organic mass flow entering the
    process, in kg/hr;
     
    m = Total number of runs (at least 3);
     
    j = Individual run “j”;
     
    Qbj = Mass quantity of hazardous waste entering the
    process during run “j,” in kg/hr;
     
    Qaj = Average mass quantity of waste exiting the process
    during run “j,” in kg/hr;
     
    aj
    C
    = Average VO concentration of hazardous waste
    exiting the process during run “j,” as determined in
    accordance with the requirements of subsection
    (b)(3) of this Section, in ppmw; and
     
    bj
    C
    = Average VO concentration of hazardous waste
    entering the process during run “j,” as determined in
    accordance with the requirements of subsection

     
    646
    725.984 (a)(3) of this Section, in ppmw.
     
    E) The organic reduction efficiency of the process must be calculated
    by using the results determined in accordance with subsection
    (b)(5)(D) of this Section and the following equation:
     
    R=
    E
    - E
    E
    x100%
    b
    a
    b
     
     
    Where:
     
    R = Organic reduction efficiency, in percent;
     
    Eb = Waste volatile organic mass flow entering the
    process, as determined in accordance with the
    requirements of subsection (b)(5)(D) of this
    Section, in kg/hr; and
     
    Ea = Waste volatile organic mass flow exiting the
    process, as determined in accordance with the
    requirements of subsection (b)(5)(D) of this
    Section, in kg/hr.
     
    6) Procedure to determine the organic biodegradation efficiency (Rbio) for a
    treated hazardous waste.
     
    A) The fraction of organics biodegraded (Fbio) must be determined
    using the procedure specified in appendix C to 40 CFR 63,
    appendix C (Determination of the Fraction Biodegraded (Fbio) in a
    Biological Treatment Unit), incorporated by reference in 35 Ill.
    Adm. Code 720.111(b).
     
    B) The organic biodegradation efficiency (Rbio) must be calculated by
    using the following equation:
     
    bio bio
    R
    = F
    x100%
     
    Where:
     
    Rbio = Organic biodegradation efficiency, in percent; and
     
    Fbio = Fraction of organic biodegraded, as determined in
    accordance with the requirements of subsection
    (b)(6)(A) of this Section.
     

     
    647
    7) Procedure to determine the required organic mass removal rate (RMR) for
    a treated hazardous waste.
     
    A) All of the hazardous waste streams entering the treatment process
    must be identified.
     
    B) The average VO concentration of the hazardous waste stream at
    the point of waste origination must be determined in accordance
    with the requirements of subsection (a) of this Section.
     
    C) For each individual hazardous waste stream that has an average
    volatile organic concentration equal to or greater than 500 ppmw at
    the point of waste origination, the average volumetric flow rate of
    hazardous waste and the density of the hazardous waste stream at
    the point of waste origination must be determined.
     
    D) The required organic mass removal rate (RMR) for the hazardous
    waste must be calculated by using the average VO concentration,
    average volumetric flow rate, and density determined for each
    individual hazardous waste stream, and the following equation:
     
    RMR =
    n
    y = 1
    V
    x k
    x
    (C
    - 500ppmw)
    10
    y
    y
    y
    6
      
     
    Where:
     
    RMR = Required organic mass removal rate, in kg/hr;
     
    y = Individual hazardous waste stream “y” that has an
    average volatile organic (VO) concentration equal
    to or greater than 500 ppmw at the point of waste
    origination, as determined in accordance with the
    requirements of subsection (a) of this Section;
     
    n = Total number of “y” hazardous waste streams
    treated by process;
     
    Vy = Average volumetric flow rate of hazardous waste
    stream “y” at the point of waste origination, in
    m
    3
    /hr;
     
    ky = Density of hazardous waste stream “y,” in kg/m
    3
    ;
    and
     

     
    648
    Cy = Average VO concentration of hazardous waste
    stream “y” at the point of waste origination, as
    determined in accordance with the requirements of
    subsection (a) of this Section, in ppmw.
     
    8) Procedure to determine the actual organic mass removal rate (MR) for a
    treated hazardous waste.
     
    A) The actual organic mass removal rate (MR) must be determined
    based on results for a minimum of three consecutive runs. The
    sampling time for each run must be one hour.
     
    B) The waste volatile organic mass flow entering the process (Eb) and
    the waste volatile organic mass flow exiting the process (Ea) must
    be determined in accordance with the requirements of subsection
    (b)(5)(D) of this Section.
     
    C) The actual organic mass removal rate (MR) must be calculated by
    using the mass flow rate determined in accordance with the
    requirements of subsection (b)(8)(B) of this Section and the
    following equation:
     
    MR = E
    - E
    b
    a
     
    Where:
     
    MR = Actual organic mass removal rate, in kg/hr;
     
    Eb = Waste volatile organic mass flow entering the
    process, as determined in accordance with the
    requirements of subsection (b)(5)(D) of this
    Section, in kg/hr; and
     
    Ea = Waste volatile organic mass flow exiting the
    process, as determined in accordance with the
    requirements of subsection (b)(5)(D) of this
    Section, in kg/hr.
     
    9) Procedure to determine the actual organic mass biodegradation rate
    (MRbio) for a treated hazardous waste.
     
    A) The actual organic mass biodegradation rate (MRbio) must be
    determined based on results for a minimum of three consecutive
    runs. The sampling time for each run must be one hour.
     

     
    649
    B) The waste organic mass flow entering the process (Eb) must be
    determined in accordance with the requirements of subsection
    (b)(5)(D) of this Section.
     
    C) The fraction of organic biodegraded (Fbio) must be determined
    using the procedure specified in appendix C to 40 CFR 63,
    appendix C, incorporated by reference in 35 Ill. Adm. Code
    720.111(b) (Determination of the Fraction Biodegraded (Fbio) in a
    Biological Treatment Unit).
     
    D) The actual organic mass biodegradation rate (MRbio) must be
    calculated by using the mass flow rates and fraction of organic
    biodegraded, as determined in accordance with the requirements of
    subsections (b)(9)(B) and (b)(9)(C) of this Section, respectively,
    and the following equation:
     
    bio b bio
    MR
    = E
    xF
      
     
    Where:
     
    MRbio = Actual organic mass biodegradation rate, in kg/hr;
     
    Eb = Waste organic mass flow entering the process, as
    determined in accordance with the requirements of
    subsection (b)(5)(D) of this Section, in kg/hr; and
     
    Fbio = Fraction of organic biodegraded, as determined in
    accordance with the requirements of subsection
    (b)(9)(C) of this Section.
     
    c) Procedure to determine the maximum organic vapor pressure of a hazardous
    waste in a tank.
     
    1) An owner or operator must determine the maximum organic vapor
    pressure for each hazardous waste placed in a tank using Tank Level 1
    controls in accordance with standards specified in Section 725.985(c).
     
    2) An owner or operator must use either direct measurement, as specified in
    subsection (c)(3) of this Section, or knowledge of the waste, as specified
    by subsection (c)(4) of this Section, to determine the maximum organic
    vapor pressure that is representative of the hazardous waste composition
    stored or treated in the tank.
     
    3) Direct measurement to determine the maximum organic vapor pressure of
    a hazardous waste.
     

     
    650
    A) Sampling. A sufficient number of samples must be collected to be
    representative of the waste contained in the tank. All samples
    must be conducted and handled in accordance with written
    procedures prepared by the owner or operator and documented in a
    site sampling plan. This plan must describe the procedure by
    which representative samples of the hazardous waste are collected
    so that a minimum loss of organics occurs throughout the sample
    collection and handling process and by which sample integrity is
    maintained. A copy of the written sampling plan must be
    maintained on-site in the facility operating records. An example of
    an acceptable sampling plan includes a plan incorporating sample
    collection and handling procedures in accordance with the
    requirements specified in “Test Methods for Evaluating Solid
    Waste, Physical/Chemical Methods,” USEPA Publication No. SW-
    846, incorporated by reference in 35 Ill. Adm. Code 720.111(a), or
    may be found in Method 25D in 40 CFR 60, appendix A,
    incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    B) Analysis. Any appropriate one of the following methods may be
    used to analyze the samples and compute the maximum organic
    vapor pressure of the hazardous waste:
     
    i) Method 25E (Determination of Vapor Phase Organic
    Concentration in Waste Samples) in appendix A to 40 CFR
    60, appendix A (Test Methods), incorporated by reference
    in 35 Ill. Adm. Code 720.111(b);
     
    ii) Methods described in American Petroleum Institute
    Publication API publication 2517 (Evaporative Loss from
    External Floating-Roof Tanks), incorporated by reference
    in 35 Ill. Adm. Code 720.111(a);
     
    iii) Methods obtained from standard reference texts;
     
    iv) ASTM Method D 2879-92 (Standard Test Method for
    Vapor Pressure-Temperature Relationship and Initial
    Decomposition Temperature of Liquids by Isoteniscope),
    incorporated by reference in 35 Ill. Adm. Code 720.111(a);
    or
     
    v) Any other method approved by the Agency.
     
    4) Use of knowledge to determine the maximum organic vapor pressure of
    the hazardous waste. Documentation must be prepared and recorded that
    presents the information used as the basis for the owner’s or operator’s
    knowledge that the maximum organic vapor pressure of the hazardous

     
    651
    waste is less than the maximum vapor pressure limit listed in Section
    725.985(b)(1)(A) for the applicable tank design capacity category. An
    example of information that may be used is documentation that the
    hazardous waste is generated by a process for which at other locations it
    previously has been determined by direct measurement that the waste
    maximum organic vapor pressure is less than the maximum vapor pressure
    limit for the appropriate tank design capacity category.
     
    d) The procedure for determining no detectable organic emissions for the purpose of
    complying with this Subpart CC is as follows:
     
    1) The test must be conducted in accordance with the procedures specified in
    Method 21 (Determination of Volatile Organic Compound Leaks) of
    appendix A to 40 CFR 60, appendix A (Test Methods), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b). Each potential leak interface
    (i.e., a location where organic vapor leakage could occur) on the cover and
    associated closure devices must be checked. Potential leak interfaces that
    are associated with covers and closure devices include, but are not limited
    to, any of the following: the interface of the cover and its foundation
    mounting, the periphery of any opening on the cover and its associated
    closure device, and the sealing seat interface on a spring-loaded pressure
    relief valve.
     
    2) The test must be performed when the unit contains a hazardous waste
    having an organic concentration representative of the range of
    concentrations for the hazardous waste expected to be managed in the
    unit. During the test, the cover and closure devices must be secured in the
    closed position.
     
    3) The detection instrument must meet the performance criteria of Method 21
    of 40 CFR 60, appendix A, incorporated by reference in 35 Ill. Adm. Code
    720.111(b), except the instrument response factor criteria in Section
    3.1.2(a) of Method 21 must be for the average composition of the organic
    constituents in the hazardous waste placed in the waste management unit,
    not for each individual organic constituent.
     
    4) The detection instrument must be calibrated before use on each day of its
    use by the procedures specified in Method 21 of 40 CFR 60, appendix A,
    incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    5) Calibration gases must be as follows:
     
    A) Zero air (less than 10 ppmv hydrocarbon in air), and
     
    B) A mixture of methane or n-hexane in air at a concentration of
    approximately, but less than, 10,000 ppmv methane or n-hexane.

     
    652
     
    6) The background level must be determined according to the procedures in
    Method 21 of 40 CFR 60, appendix A, incorporated by reference in 35 Ill.
    Adm. Code 720.111(b).
     
    7) Each potential leak interface must be checked by traversing the instrument
    probe around the potential leak interface as close to the interface as
    possible, as described in Method 21 of 40 CFR 60, appendix A,
    incorporated by reference in 35 Ill. Adm. Code 720.111(b). In the case
    when the configuration of the cover or closure device prevents a complete
    traverse of the interface, all accessible portions of the interface must be
    sampled. In the case when the configuration of the closure device
    prevents any sampling at the interface and the device is equipped with an
    enclosed extension or horn (e.g., some pressure relief devices), the
    instrument probe inlet must be placed at approximately the center of the
    exhaust area to the atmosphere.
     
    8) The arithmetic difference between the maximum organic concentration
    indicated by the instrument and the background level must be compared
    with the value of 500 ppmv except when monitoring a seal around a
    rotating shaft that passes through a cover opening, in which case the
    comparison must be as specified in subsection (d)(9) of this Section. If
    the difference is less than 500 ppmv, then the potential leak interface is
    determined to operate with no detectable organic emissions.
     
    9) For the seals around a rotating shaft that passes through a cover opening,
    the arithmetic difference between the maximum organic concentration
    indicated by the instrument and the background level must be compared
    with the value of 10,000 ppmw. If the difference is less than 10,000
    ppmw, then the potential leak interface is determined to operate with no
    detectable organic emissions.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.985 Standards: Tanks
     
    a) The provisions of this Section apply to the control of air pollutant emissions from
    tanks for which Section 725.983(b) references the use of this Section for such air
    emission control.
     
    b) The owner or operator must control air pollutant emissions from each tank subject
    to this Section in accordance with the following requirements, as applicable:
     
    1) For a tank that manages hazardous waste that meets all of the conditions
    specified in subsections (b)(1)(A) through (b)(1)(C) of this Section, the
    owner or operator must control air pollutant emissions from the tank in

     
    653
    accordance with the Tank Level 1 controls specified in subsection (c) of
    this Section or the Tank Level 2 controls specified in subsection (d) of this
    Section.
     
    A) The hazardous waste in the tank has a maximum organic vapor
    pressure that is less than the maximum organic vapor pressure
    limit for the tank’s design capacity category, as follows:
     
    i) For a tank design capacity equal to or greater than 151 m
    3
     
    (5333 ft
    3
    or 39,887 gal), the maximum organic vapor
    pressure limit for the tank is 5.2 kPa (0.75 psia or 39 mm
    Hg);
     
    ii) For a tank design capacity equal to or greater than 75 m
    3
     
    (2649 ft
    3
    or 19,810 gal) but less than 151 m
    3
    (5333 ft
    3
    or
    39,887 gal), the maximum organic vapor pressure limit for
    the tank is 27.6 kPa (4.0 psia or 207 mm Hg); or
     
    iii) For a tank design capacity less than 75 m
    3
    (2649 ft
    3
    or
    19,810 gal), the maximum organic vapor pressure limit for
    the tank is 76.6 kPa (11.1 psia or 574 mm Hg).
     
    B) The hazardous waste in the tank is not heated by the owner or
    operator to a temperature that is greater than the temperature at
    which the maximum organic vapor pressure of the hazardous waste
    is determined for the purpose of complying with subsection
    (b)(1)(A) of this Section.
     
    C) The hazardous waste in the tank is not treated by the owner or
    operator using a waste stabilization process, as defined in Section
    725.981.
     
    2) For a tank that manages hazardous waste that does not meet all of the
    conditions specified in subsections (b)(1)(A) through (b)(1)(C) of this
    Section, the owner or operator must control air pollutant emissions from
    the tank by using Tank Level 2 controls in accordance with the
    requirements of subsection (d) of this Section. Examples of tanks required
    to use Tank Level 2 controls include the following: a tank used for a
    waste stabilization process and a tank for which the hazardous waste in the
    tank has a maximum organic vapor pressure that is equal to or greater than
    the maximum organic vapor pressure limit for the tank’s design capacity
    category, as specified in subsection (b)(1)(A) of this Section.
     
    c) An owner or operator controlling air pollutant emissions from a tank using Tank
    Level 1 controls must meet the requirements specified in subsections (c)(1)
    through (c)(4) of this Section:

     
    654
     
    1) The owner or operator must determine the maximum organic vapor
    pressure for a hazardous waste to be managed in the tank using Tank
    Level 1 controls before the first time the hazardous waste is placed in the
    tank. The maximum organic vapor pressure must be determined using the
    procedures specified in Section 725.984(c). Thereafter, the owner or
    operator must perform a new determination whenever changes to the
    hazardous waste managed in the tank could potentially cause the
    maximum organic vapor pressure to increase to a level that is equal to or
    greater than the maximum organic vapor pressure limit for the tank design
    capacity category specified in subsection (b)(1)(A) of this Section, as
    applicable to the tank.
     
    2) The tank must be equipped with a fixed roof designed to meet the
    following specifications:
     
    A) The fixed roof and its closure devices must be designed to form a
    continuous barrier over the entire surface area of the hazardous
    waste in the tank. The fixed roof may be a separate cover installed
    on the tank (e.g., a removable cover mounted on an open-top tank)
    or may be an integral part of the tank structural design (e.g., a
    horizontal cylindrical tank equipped with a hatch).
     
    B) The fixed roof must be installed in such a manner that there are no
    visible cracks, holes, gaps, or other open spaces between roof
    section joints or between the interface of the roof edge and the tank
    wall.
     
    C) Either of the following must be true of each opening in the fixed
    roof and of any manifold system associated with the fixed roof
    must be either:
     
    i) The opening or manifold system is equipped with a closure
    device designed to operate so that when the closure device
    is secured in the closed position there are no visible cracks,
    holes, gaps, or other open spaces in the closure device or
    between the perimeter of the opening and the closure
    device; or
     
    ii) The opening or manifold system is connected by a closed-
    vent system that is vented to a control device. The control
    device must remove or destroy organics in the vent stream,
    and it must be operating whenever hazardous waste is
    managed in the tank, except as provided for in subsection
    (c)(2)(E).
     

     
    655
    D) The fixed roof and its closure devices must be made of suitable
    materials that will minimize exposure of the hazardous waste to
    the atmosphere, to the extent practical, and which will maintain the
    integrity of the fixed roof and closure devices throughout their
    intended service life. Factors to be considered when selecting the
    materials for and designing the fixed roof and closure devices must
    include the following: organic vapor permeability; the effects of
    any contact with the hazardous waste or its vapors managed in the
    tank; the effects of outdoor exposure to wind, moisture, and
    sunlight; and the operating practices used for the tank on which the
    fixed roof is installed.
     
    E) The control device operated pursuant to subsection (c)(2)(C) of
    this Section needs not remove or destroy organics in the vent
    stream under the following conditions:
     
    i) During periods when it is necessary to provide access to the
    tank for performing the activities of subsection (c)(2)(E)(ii)
    of this Section, venting of the vapor headspace underneath
    the fixed roof to the control device is not required, opening
    of closure devices is allowed, and removal of the fixed roof
    is allowed. Following completion of the activity, the owner
    or operator must promptly secure the closure device in the
    closed position or reinstall the cover, as applicable, and
    resume operation of the control device; and
     
    ii) During periods of routine inspection, maintenance, or other
    activities needed for normal operations, and for the removal
    of accumulated sludge or other residues from the bottom of
    the tank.
     
    BOARD NOTE: Subsections (c)(2)(E)(i) and (c)(2)(E)(ii) are
    derived from 40 CFR 265.985(c)(2)(iii)(B)(1) and (c)(2)(iii)(B)(2),
    which the Board has codified here to comport with Illinois
    Administrative Code format requirements.
     
    3) Whenever a hazardous waste is in the tank, the fixed roof must be
    installed with each closure device secured in the closed position, except as
    follows:
     
    A) Opening of closure devices or removal of the fixed roof is allowed
    at the following times:
     
    i) To provide access to the tank for performing routine
    inspection, maintenance, or other activities needed for
    normal operations. Examples of such activities include

     
    656
    those times when a worker needs to open a port to sample
    the liquid in the tank, or when a worker needs to open a
    hatch to maintain or repair equipment. Following
    completion of the activity, the owner or operator must
    promptly secure the closure device in the closed position or
    reinstall the cover, as applicable, to the tank.
     
    ii) To remove accumulated sludge or other residues from the
    bottom of tank.
     
    B) Opening of a spring-loaded pressure-vacuum relief valve,
    conservation vent, or similar type of pressure relief device that
    vents to the atmosphere is allowed during normal operations for
    the purpose of maintaining the tank internal pressure in accordance
    with the tank design specifications. The device must be designed
    to operate with no detectable organic emissions when the device is
    secured in the closed position. The settings at which the device
    opens must be established so that the device remains in the closed
    position whenever the tank internal pressure is within the internal
    pressure operating range determined by the owner or operator
    based on the tank manufacturer recommendations; applicable
    regulations; fire protection and prevention codes; standard
    engineering codes and practices; or other requirements for the safe
    handling of flammable, ignitable, explosive, reactive, or hazardous
    materials. Examples of normal operating conditions that may
    require these devices to open are during those times when the tank
    internal pressure exceeds the internal pressure operating range for
    the tank as a result of loading operations or diurnal ambient
    temperature fluctuations.
     
    C) Opening of a safety device, as defined in Section 725.981, is
    allowed at any time conditions require doing so to avoid an unsafe
    condition.
     
    4) The owner or operator must inspect the air emission control equipment in
    accordance with the following requirements.
     
    A) The fixed roof and its closure devices must be visually inspected
    by the owner or operator to check for defects that could result in
    air pollutant emissions. Defects include, but are not limited to,
    visible cracks, holes, or gaps in the roof sections or between the
    roof and the tank wall; broken, cracked, or otherwise damaged
    seals or gaskets on closure devices; and broken or missing hatches,
    access covers, caps, or other closure devices.
     
    B) The owner or operator must perform an initial inspection of the

     
    657
    fixed roof and its closure devices on or before the date that the
    tank becomes subject to this Section. Thereafter, the owner or
    operator must perform the inspections at least once every year,
    except under the special conditions provided for in subsection (l)
    of this Section.
     
    C) In the event that a defect is detected, the owner or operator must
    repair the defect in accordance with the requirements of subsection
    (k) of this Section.
     
    D) The owner or operator must maintain a record of the inspection in
    accordance with the requirements specified in Section 725.990(b).
     
    d) An owner or operator controlling air pollutant emissions from a tank using Tank
    Level 2 controls must use one of the following tanks:
     
    1) A fixed-roof tank equipped with an internal floating roof in accordance
    with the requirements specified in subsection (e) of this Section;
     
    2) A tank equipped with an external floating roof in accordance with the
    requirements specified in subsection (f) of this Section;
     
    3) A tank vented through a closed-vent system to a control device in
    accordance with the requirements specified in subsection (g) of this
    Section;
     
    4) A pressure tank designed and operated in accordance with the
    requirements specified in subsection (h) of this Section; or
     
    5) A tank located inside an enclosure that is vented through a closed-vent
    system to an enclosed combustion control device in accordance with the
    requirements specified in subsection (i) of this Section.
     
    e) The owner or operator that controls air pollutant emissions from a tank using a
    fixed roof with an internal floating roof must meet the requirements specified in
    subsections (e)(1) through (e)(3) of this Section.
     
    1) The tank must be equipped with a fixed roof and an internal floating roof
    in accordance with the following requirements:
     
    A) The internal floating roof must be designed to float on the liquid
    surface except when the floating roof must be supported by the leg
    supports.
     
    B) The internal floating roof must be equipped with a continuous seal
    between the wall of the tank and the floating roof edge that meets

     
    658
    either of the following requirements:
     
    i) A single continuous seal that is either a liquid-mounted seal
    or a metallic shoe seal, as defined in Section 725.981; or
     
    ii) Two continuous seals mounted one above the other. The
    lower seal may be a vapor-mounted seal.
     
    C) The internal floating roof must meet the following specifications:
     
    i) Each opening in a noncontact internal floating roof except
    for automatic bleeder vents (vacuum breaker vents) and the
    rim space vents is to provide a projection below the liquid
    surface;
     
    ii) Each opening in the internal floating roof must be equipped
    with a gasketed cover or a gasketed lid except for leg
    sleeves, automatic bleeder vents, rim space vents, column
    wells, ladder wells, sample wells, and stub drains;
     
    iii) Each penetration of the internal floating roof for the
    purpose of sampling must have a slit fabric cover that
    covers at least 90 percent of the opening;
     
    iv) Each automatic bleeder vent and rim space vent must be
    gasketed;
     
    v) Each penetration of the internal floating roof that allows for
    passage of a ladder must have a gasketed sliding cover; and
     
    vi) Each penetration of the internal floating roof that allows for
    passage of a column supporting the fixed roof must have a
    flexible fabric sleeve seal or a gasketed sliding cover.
     
    2) The owner or operator must operate the tank in accordance with the
    following requirements:
     
    A) When the floating roof is resting on the leg supports, the process of
    filling, emptying, or refilling must be continuous and must be
    completed as soon as practical;
     
    B) Automatic bleeder vents are to be set closed at all times when the
    roof is floating, except when the roof is being floated off or is
    being landed on the leg supports; and
     
    C) Prior to filling the tank, each cover, access hatch, gauge float well

     
    659
    or lid on any opening in the internal floating roof must be bolted or
    fastened closed (i.e., no visible gaps). Rim space vents are to be
    set to open only when the internal floating roof is not floating or
    when the pressure beneath the rim exceeds the manufacturer’s
    recommended setting.
     
    3) The owner or operator must inspect the internal floating roof in
    accordance with the procedures specified as follows:
     
    A) The floating roof and its closure devices must be visually inspected
    by the owner or operator to check for defects that could result in
    air pollutant emissions. Defects include, but are not limited to, the
    following: when the internal floating roof is not floating on the
    surface of the liquid inside the tank; when liquid has accumulated
    on top of the internal floating roof; when any portion of the roof
    seals have detached from the roof rim; when holes, tears, or other
    openings are visible in the seal fabric; when the gaskets no longer
    close off the hazardous waste surface from the atmosphere; or
    when the slotted membrane has more than 10 percent open area;
     
    B) The owner or operator must inspect the internal floating roof
    components as follows, except as provided in subsection (e)(3)(C)
    of this Section:
     
    i) Visually inspect the internal floating roof components
    through openings on the fixed roof (e.g., manholes and roof
    hatches) at least once every 12 months after initial fill, and
     
    ii) Visually inspect the internal floating roof, primary seal,
    secondary seal (if one is in service), gaskets, slotted
    membranes, and sleeve seals (if any) each time the tank is
    emptied and degassed and at least once every 10 years;
     
    C) As an alternative to performing the inspections specified in
    subsection (e)(3)(B) of this Section for an internal floating roof
    equipped with two continuous seals mounted one above the other,
    the owner or operator may visually inspect the internal floating
    roof, primary and secondary seals, gaskets, slotted membranes, and
    sleeve seals (if any) each time the tank is emptied and degassed
    and at least every five years;
     
    D) Prior to each inspection required by subsection (e)(3)(B) or
    (e)(3)(C) of this Section, the owner or operator must notify the
    Agency in advance of each inspection to provide the Agency with
    the opportunity to have an observer present during the inspection.
    The owner or operator must notify the Agency of the date and

     
    660
    location of the inspection as follows:
     
    i) Prior to each visual inspection of an internal floating roof
    in a tank that has been emptied and degassed, written
    notification must be prepared and sent by the owner or
    operator so that it is received by the Agency at least 30
    calendar days before refilling the tank, except when an
    inspection is not planned, as provided for in subsection
    (e)(3)(D)(ii) of this Section; and
     
    ii) When a visual inspection is not planned and the owner or
    operator could not have known about the inspection 30
    calendar days before refilling the tank, the owner or
    operator must notify the Agency as soon as possible, but no
    later than seven calendar days before refilling of the tank.
    This notification may be made by telephone and
    immediately followed by a written explanation for why the
    inspection is unplanned. Alternatively, written notification,
    including the explanation for the unplanned inspection,
    may be sent so that it is received by the Regional
    Administrator at least seven calendar days before refilling
    the tank;
     
    E) In the event that a defect is detected, the owner or operator must
    repair the defect in accordance with the requirements of subsection
    (k) of this Section; and
     
    F) The owner or operator must maintain a record of the inspection in
    accordance with the requirements specified in Section 725.990(b).
     
    4) Safety devices, as defined in Section 725.981, may be installed and
    operated as necessary on any tank complying with the requirements of this
    subsection (e).
     
    f) The owner or operator that controls air pollutant emissions from a tank using an
    external floating roof must meet the requirements specified in subsections (f)(1)
    through (f)(3) of this Section.
     
    1) The owner or operator must design the external floating roof in
    accordance with the following requirements:
     
    A) The external floating roof must be designed to float on the liquid
    surface except when the floating roof must be supported by the leg
    supports;
     
    B) The floating roof must be equipped with two continuous seals, one

     
    661
    above the other, between the wall of the tank and the roof edge.
    The lower seal is referred to as the primary seal, and the upper seal
    is referred to as the secondary seal.
     
    i) The primary seal must be a liquid-mounted seal or a
    metallic shoe seal, as defined in Section 725.981. The total
    area of the gaps between the tank wall and the primary seal
    must not exceed 212 square centimeters (cm
    2
    ) per meter
    (10.0 in
    2
    per foot) of tank diameter, and the width of any
    portion of these gaps must not exceed 3.8 centimeters (cm)
    (1.5 inches). If a metallic shoe seal is used for the primary
    seal, the metallic shoe seal must be designed so that one
    end extends into the liquid in the tank and the other end
    extends a vertical distance of at least 61 centimeters (24
    inches) above the liquid surface.
     
    ii) The secondary seal must be mounted above the primary
    seal and cover the annular space between the floating roof
    and the wall of the tank. The total area of the gaps between
    the tank wall and the secondary seal must not exceed 21.2
    cm
    2
    per meter (1.0 in
    2
    per foot) of tank diameter, and the
    width of any portion of these gaps must not exceed 1.3 cm
    (0.5 inch); and
     
    C) The external floating roof must meet the following specifications:
     
    i) Except for automatic bleeder vents (vacuum breaker vents)
    and rim space vents, each opening in a noncontact external
    floating roof must provide a projection below the liquid
    surface;
     
    ii) Except for automatic bleeder vents, rim space vents, roof
    drains, and leg sleeves, each opening in the roof must be
    equipped with a gasketed cover, seal, or lid;
     
    iii) Each access hatch and each gauge float well must be
    equipped with a cover designed to be bolted or fastened
    when the cover is secured in the closed position;
     
    iv) Each automatic bleeder vent and each rim space vent must
    be equipped with a gasket;
     
    v) Each roof drain that empties into the liquid managed in the
    tank must be equipped with a slotted membrane fabric
    cover that covers at least 90 percent of the area of the
    opening;

     
    662
     
    vi) Each unslotted and slotted guide pole well must be
    equipped with a gasketed sliding cover or a flexible fabric
    sleeve seal;
     
    vii) Each unslotted guide pole must be equipped with a
    gasketed cap on the end of the pole;
     
    viii) Each slotted guide pole must be equipped with a gasketed
    float or other device that closes off the liquid surface from
    the atmosphere; and
     
    ix) Each gauge hatch and each sample well must be equipped
    with a gasketed cover.
     
    2) The owner or operator must operate the tank in accordance with the
    following requirements:
     
    A) When the floating roof is resting on the leg supports, the process of
    filling, emptying, or refilling must be continuous and must be
    completed as soon as practical;
     
    B) Except for automatic bleeder vents, rim space vents, roof drains,
    and leg sleeves, each opening in the roof must be secured and
    maintained in a closed position at all times except when the
    closure device must be open for access;
     
    C) Covers on each access hatch and each gauge float well must be
    bolted or fastened when secured in the closed position;
     
    D) Automatic bleeder vents must be set closed at all times when the
    roof is floating, except when the roof is being floated off or is
    being landed on the leg supports;
     
    E) Rim space vents must be set to open only at those times that the
    roof is being floated off the roof leg supports or when the pressure
    beneath the rim seal exceeds the manufacturer’s recommended
    setting;
     
    F) The cap on the end of each unslotted guide pole must be secured in
    the closed position at all times except when measuring the level or
    collecting samples of the liquid in the tank;
     
    G) The cover on each gauge hatch or sample well must be secured in
    the closed position at all times except when the hatch or well must
    be opened for access; and

     
    663
     
    H) Both the primary seal and the secondary seal must completely
    cover the annular space between the external floating roof and the
    wall of the tank in a continuous fashion except during inspections.
     
    3) The owner or operator must inspect the external floating roof in
    accordance with the procedures specified as follows:
     
    A) The owner or operator must measure the external floating roof seal
    gaps in accordance with the following requirements:
     
    i) The owner or operator must perform measurements of gaps
    between the tank wall and the primary seal within 60
    calendar days after initial operation of the tank following
    installation of the floating roof and, thereafter, at least once
    every five years;
     
    ii) The owner or operator must perform measurements of gaps
    between the tank wall and the secondary seal within 60
    calendar days after initial operation of the tank following
    installation of the floating roof and, thereafter, at least once
    every year;
     
    iii) If a tank ceases to hold hazardous waste for a period of one
    year or more, subsequent introduction of hazardous waste
    into the tank must be considered an initial operation for the
    purposes of subsections (f)(3)(A)(i) and (f)(3)(A)(ii) of this
    Section;
     
    iv) The owner or operator must determine the total surface area
    of gaps in the primary seal and in the secondary seal
    individually using the procedure set forth in subsection
    (f)(4)(D) of this Section;
     
    v) In the event that the seal gap measurements do not conform
    to the specifications in subsection (f)(1)(B) of this Section,
    the owner or operator must repair the defect in accordance
    with the requirements of subsection (k) of this Section; and
     
    vi) The owner or operator must maintain a record of the
    inspection in accordance with the requirements specified in
    Section 725.990(b);
     
    B) The owner or operator must visually inspect the external floating
    roof in accordance with the following requirements:
     

     
    664
    i) The floating roof and its closure devices must be visually
    inspected by the owner or operator to check for defects that
    could result in air pollutant emissions. Defects include, but
    are not limited to any of the following: holes, tears, or
    other openings in the rim seal or seal fabric of the floating
    roof; a rim seal detached from the floating roof; all or a
    portion of the floating roof deck being submerged below
    the surface of the liquid in the tank; broken, cracked, or
    otherwise damaged seals or gaskets on closure devices; and
    broken or missing hatches, access covers, caps, or other
    closure devices;
     
    ii) The owner or operator must perform an initial inspection of
    the external floating roof and its closure devices on or
    before the date that the tank becomes subject to this
    Section. Thereafter, the owner or operator must perform
    the inspections at least once every year except for the
    special conditions provided for in subsection (l) of this
    Section;
     
    iii) In the event that a defect is detected, the owner or operator
    must repair the defect in accordance with the requirements
    of subsection (k) of this Section; and
     
    iv) The owner or operator must maintain a record of the
    inspection in accordance with the requirements specified in
    Section 725.990(b);
     
    C) Prior to each inspection required by subsection (f)(3)(A) or
    (f)(3)(B) of this Section, the owner or operator must notify the
    Agency in advance of each inspection to provide the Agency with
    the opportunity to have an observer present during the inspection.
    The owner or operator must notify the Agency of the date and
    location of the inspection as follows:
     
    i) Prior to each inspection to measure external floating roof
    seal gaps as required under subsection (f)(3)(A) of this
    Section, written notification must be prepared and sent by
    the owner or operator so that it is received by the Agency at
    least 30 calendar days before the date the measurements are
    scheduled to be performed;
     
    ii) Prior to each visual inspection of an external floating roof
    in a tank that has been emptied and degassed, written
    notification must be prepared and sent by the owner or
    operator so that it is received by the Agency at least 30

     
    665
    calendar days before refilling the tank except when an
    inspection is not planned, as provided for in subsection
    (f)(3)(C)(iii) of this Section; and
     
    iii) When a visual inspection is not planned and the owner or
    operator could not have known about the inspection 30
    calendar days before refilling the tank, the owner or
    operator must notify the Agency as soon as possible, but no
    later than seven calendar days before refilling of the tank.
    This notification may be made by telephone and
    immediately followed by a written explanation for why the
    inspection is unplanned. Alternatively, written notification,
    including the explanation for the unplanned inspection,
    may be sent so that it is received by the Regional
    Administrator at least seven calendar days before refilling
    the tank; and
     
    D) Procedure for determining gaps in the primary seal and in the
    secondary seal for the purposes of subsection (f)(3)(A)(iv) of this
    Section:
     
    i) The seal gap measurements must be performed at one or
    more floating roof levels when the roof is floating off the
    roof supports;
     
    ii) Seal gaps, if any, must be measured around the entire
    perimeter of the floating roof in each place where a 0.32-
    cm (¼-inch) diameter uniform probe passes freely (without
    forcing or binding against the seal) between the seal and
    the wall of the tank and measure the circumferential
    distance of each such location;
     
    iii) For a seal gap measured under this subsection (f)(3), the
    gap surface area must be determined by using probes of
    various widths to measure accurately the actual distance
    from the tank wall to the seal and multiplying each such
    width by its respective circumferential distance; and
     
    iv) The total gap area must be calculated by adding the gap
    surface areas determined for each identified gap location
    for the primary seal and the secondary seal individually,
    and then dividing the sum for each seal type by the nominal
    diameter of the tank. These total gap areas for the primary
    seal and secondary seal are then compared to the respective
    standards for the seal type, as specified in subsection
    (f)(1)(B) of this Section; and

     
    666
     
    BOARD NOTE: Subsections (f)(3)(D)(i) through (f)(3)(D)(iv) are
    derived from 40 CFR 265.1085(f)(3)(i)(D)(1) through
    (f)(3)(i)(D)(4), which the Board has codified here to comport with
    Illinois Administrative Code format requirements.
     
    4) Safety devices, as defined in Section 725.981, may be installed and
    operated as necessary on any tank complying with the requirements of this
    subsection (f).
     
    g) The owner or operator that controls air pollutant emissions from a tank by venting
    the tank to a control device must meet the requirements specified in subsections
    (g)(1) through (g)(3) of this Section.
     
    1) The tank must be covered by a fixed roof and vented directly through a
    closed-vent system to a control device in accordance with the following
    requirements:
     
    A) The fixed roof and its closure devices must be designed to form a
    continuous barrier over the entire surface area of the liquid in the
    tank;
     
    B) Each opening in the fixed roof not vented to the control device
    must be equipped with a closure device. If the pressure in the
    vapor headspace underneath the fixed roof is less than atmospheric
    pressure when the control device is operating, the closure devices
    must be designed to operate so that when the closure device is
    secured in the closed position there are no visible cracks, holes,
    gaps, or other open spaces in the closure device or between the
    perimeter of the cover opening and the closure device. If the
    pressure in the vapor headspace underneath the fixed roof is equal
    to or greater than atmospheric pressure when the control device is
    operating, the closure device must be designed to operate with no
    detectable organic emissions;
     
    C) The fixed roof and its closure devices must be made of suitable
    materials that will minimize exposure of the hazardous waste to
    the atmosphere, to the extent practical, and will maintain the
    integrity of the fixed roof and closure devices throughout their
    intended service life. Factors to be considered when selecting the
    materials for and designing the fixed roof and closure devices must
    include the following: organic vapor permeability; the effects of
    any contact with the liquid and its vapor managed in the tank; the
    effects of outdoor exposure to wind, moisture, and sunlight; and
    the operating practices used for the tank on which the fixed roof is
    installed; and

     
    667
     
    D) The closed-vent system and control device must be designed and
    operated in accordance with the requirements of Section 725.988.
     
    2) Whenever a hazardous waste is in the tank, the fixed roof must be
    installed with each closure device secured in the closed position and the
    vapor headspace underneath the fixed roof vented to the control device
    except as follows:
     
    A) Venting to the control device is not required, and opening of
    closure devices or removal of the fixed roof is allowed at the
    following times:
     
    i) To provide access to the tank for performing routine
    inspection, maintenance, or other activities needed for
    normal operations. Examples of such activities include
    those times when a worker needs to open a port to sample
    liquid in the tank, or when a worker needs to open a hatch
    to maintain or repair equipment. Following completion of
    the activity, the owner or operator must promptly secure
    the closure device in the closed position or reinstall the
    cover, as applicable, to the tank; and
     
    ii) To remove accumulated sludge or other residues from the
    bottom of a tank; and
     
    B) Opening of a safety device, as defined in Section 725.981, is
    allowed at any time conditions require doing so to avoid an unsafe
    condition.
     
    3) The owner or operator must inspect and monitor the air emission control
    equipment in accordance with the following procedures:
     
    A) The fixed roof and its closure devices must be visually inspected
    by the owner or operator to check for defects that could result in
    air pollutant emissions. Defects include, but are not limited to any
    of the following: visible cracks, holes, or gaps in the roof sections
    or between the roof and the tank wall; broken, cracked, or
    otherwise damaged seals or gaskets on closure devices; and broken
    or missing hatches, access covers, caps, or other closure devices;
     
    B) The closed-vent system and control device must be inspected and
    monitored by the owner or operator in accordance with the
    procedures specified in Section 725.988;
     
    C) The owner or operator must perform an initial inspection of the air

     
    668
    emission control equipment on or before the date that the tank
    becomes subject to this Section. Thereafter, the owner or operator
    must perform the inspections at least once every year except for
    the special conditions provided for in subsection (l) of this Section;
     
    D) In the event that a defect is detected, the owner or operator must
    repair the defect in accordance with the requirements of subsection
    (k) of this Section; and
     
    E) The owner or operator must maintain a record of the inspection in
    accordance with the requirements specified in Section 725.990(b).
     
    h) The owner or operator that controls air pollutant emissions by using a pressure
    tank must meet the following requirements:
     
    1) The tank must be designed not to vent to the atmosphere as a result of
    compression of the vapor headspace in the tank during filling of the tank
    to its design capacity;
     
    2) All tank openings must be equipped with closure devices designed to
    operate with no detectable organic emissions as determined using the
    procedure specified in Section 725.984(d); and
     
    3) Whenever a hazardous waste is in the tank, the tank must be operated as a
    closed-vent system that does not vent to the atmosphere, except under
    either of the following two conditions:
     
    A) The tank does not need to be operated as a closed-vent system at
    those times when the opening of a safety device, as defined in
    Section 725.981, is required to avoid an unsafe condition; and
     
    B) The tank does not need to be operated as a closed-vent system at
    those times when the purging of inerts from the tank is required and
    the purge stream is routed to a closed-vent system and control device
    designed and operated in accordance with the requirements of
    Section 724.987.
     
    i) The owner or operator that controls air pollutant emissions by using an enclosure
    vented through a closed-vent system to an enclosed combustion control device
    must meet the requirements specified in subsections (i)(1) through (i)(4) of this
    Section.
     
    1) The tank must be located inside an enclosure. The enclosure must be
    designed and operated in accordance with the criteria for a permanent total
    enclosure, as specified in “Procedure T—Criteria for and Verification of a
    Permanent or Temporary Total Enclosure” under appendix B to 40 CFR

     
    669
    52.741, appendix B (VOM Measurement Techniques for Capture
    Efficiency), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
    The enclosure may have permanent or temporary openings to allow
    worker access; passage of material into or out of the enclosure by
    conveyor, vehicles, or other mechanical means; entry of permanent
    mechanical or electrical equipment; or direct airflow into the enclosure.
    The owner or operator must perform the verification procedure for the
    enclosure as specified in Section 5.0 to “Procedure T—Criteria for and
    Verification of a Permanent or Temporary Total Enclosure” initially when
    the enclosure is first installed and, thereafter, annually;
     
    2) The enclosure must be vented through a closed-vent system to an enclosed
    combustion control device that is designed and operated in accordance
    with the standards for either a vapor incinerator, boiler, or process heater
    specified in Section 725.988;
     
    3) Safety devices, as defined in Section 725.981, may be installed and
    operated as necessary on any enclosure, closed-vent system, or control
    device used to comply with the requirements of subsections (i)(1) and
    (i)(2) of this Section; and
     
    4) The owner or operator must inspect and monitor the closed-vent system
    and control device, as specified in Section 725.988.
     
    j) The owner or operator must transfer hazardous waste to a tank subject to this
    Section in accordance with the following requirements:
     
    1) Transfer of hazardous waste, except as provided in subsection (j)(2) of this
    Section, to the tank from another tank subject to this Section or from a
    surface impoundment subject to Section 725.986 must be conducted using
    continuous hard-piping or another closed system that does not allow
    exposure of the hazardous waste to the atmosphere. For the purpose of
    complying with this provision, an individual drain system is considered to
    be a closed system when it meets the requirements of subpart RR of 40
    CFR 63, “(National Emission Standards for Individual Drain Systems),”
    incorporated by reference in 35 Ill. Adm. Code 720.111(b); and
     
    2) The requirements of subsection (j)(1) of this Section do not apply when
    transferring a hazardous waste to the tank under any of the following
    conditions:
     
    A) The hazardous waste meets the average VO concentration
    conditions specified in Section 725.983(c)(1) at the point of waste
    origination;
     
    B) The hazardous waste has been treated by an organic destruction or

     
    670
    removal process to meet the requirements in Section
    725.983(c)(2); and
     
    C) The hazardous waste meets the requirements of Section
    725.983(c)(4).
     
    k) The owner or operator must repair each defect detected during an inspection
    performed in accordance with the requirements of subsection (c)(4), (e)(3), (f)(3),
    or (g)(3) of this Section as follows:
     
    1) The owner or operator must make first efforts at repair of the defect no
    later than five calendar days after detection, and repair must be completed
    as soon as possible but no later than 45 calendar days after detection
    except as provided in subsection (k)(2) of this Section; and
     
    2) Repair of a defect may be delayed beyond 45 calendar days if the owner
    or operator determines that repair of the defect requires emptying or
    temporary removal from service of the tank and no alternative tank
    capacity is available at the site to accept the hazardous waste normally
    managed in the tank. In this case, the owner or operator must repair the
    defect the next time the process or unit that is generating the hazardous
    waste managed in the tank stops operation. Repair of the defect must be
    completed before the process or unit resumes operation.
     
    l) Following the initial inspection and monitoring of the cover as required by the
    applicable provisions of this Subpart CC, subsequent inspection and monitoring
    may be performed at intervals longer than one year under the following special
    conditions:
     
    1) Where inspecting or monitoring the cover would expose a worker to
    dangerous, hazardous, or other unsafe conditions, then the owner or
    operator may designate a cover as an “unsafe to inspect and monitor
    cover” and comply with all of the following requirements:
     
    A) Prepare a written explanation for the cover stating the reasons why
    the cover is unsafe to visually inspect or to monitor, if required;
    and
     
    B) Develop and implement a written plan and schedule to inspect and
    monitor the cover, using the procedures specified in the applicable
    Section of this Subpart CC, as frequently as practicable during
    those times when a worker can safely access the cover; and
     
    2) In the case when a tank is buried partially or entirely underground, an
    owner or operator is required to inspect and monitor, as required by the
    applicable provisions of this Section, only those portions of the tank cover

     
    671
    and those connections to the tank (e.g., fill ports, access hatches, gauge
    wells, etc.) that are located on or above the ground surface.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.986 Standards: Surface Impoundments
     
    a) The provisions of this Section apply to the control of air pollutant emissions from
    surface impoundments for which Section 725.983(b) of this Subpart CC
    references the use of this Section for such air emission control.
     
    b) The owner or operator must control air pollutant emissions from the surface
    impoundment by installing and operating either of the following:
     
    1) A floating membrane cover in accordance with the provisions specified in
    subsection (c) of this Section; or
     
    2) A cover that is vented through a closed-vent system to a control device in
    accordance with the requirements specified in subsection (d) of this
    Section.
     
    c) The owner or operator that controls air pollutant emissions from a surface
    impoundment using a floating membrane cover must meet the requirements
    specified in subsections (c)(1) through (c)(3) of this Section.
     
    1) The surface impoundment must be equipped with a floating membrane
    cover designed to meet the following specifications:
     
    A) The floating membrane cover must be designed to float on the
    liquid surface during normal operations and form a continuous
    barrier over the entire surface area of the liquid;
     
    B) The cover must be fabricated from a synthetic membrane material
    that is either of the following:
     
    i) High density polyethylene (HDPE) with a thickness no less
    than 2.5 millimeters (mm) (0.10 inch); or
     
    ii) A material or a composite of different materials determined
    to have both organic permeability properties that are
    equivalent to those of the material listed in subsection
    (c)(1)(B)(i) of this Section and chemical and physical
    properties that maintain the material integrity for the
    intended service life of the material;
     
    C) The cover must be installed in a manner such that there are no

     
    672
    visible cracks, holes, gaps, or other open spaces between cover
    section seams or between the interface of the cover edge and its
    foundation mountings;
     
    D) Except as provided for in subsection (c)(1)(E) of this Section, each
    opening in the floating membrane cover must be equipped with a
    closure device so designed as to operate that when the closure
    device is secured in the closed position there are no visible cracks,
    holes, gaps, or other open spaces in the closure device or between
    the perimeter of the cover opening and the closure device;
     
    E) The floating membrane cover may be equipped with one or more
    emergency cover drains for removal of stormwater. Each
    emergency cover drain must be equipped with a slotted membrane
    fabric cover that covers at least 90 percent of the area of the
    opening or a flexible fabric sleeve seal; and
     
    F) The closure devices must be made of suitable materials that will
    minimize exposure of the hazardous waste to the atmosphere, to
    the extent practical, and will maintain the integrity of the closure
    devices throughout their intended service life. Factors to be
    considered when selecting the materials of construction and
    designing the cover and closure devices must include the
    following: the organic vapor permeability; the effects of any
    contact with the liquid and its vapor managed in the surface
    impoundment; the effects of outdoor exposure to wind, moisture,
    and sunlight; and the operating practices used for the surface
    impoundment on which the floating membrane cover is installed.
     
    2) Whenever a hazardous waste is in the surface impoundment, the floating
    membrane cover must float on the liquid and each closure device must be
    secured in the closed position, except as follows:
     
    A) Opening of closure devices or removal of the cover is allowed at
    the following times:
     
    i) To provide access to the surface impoundment for
    performing routine inspection, maintenance, or other
    activities needed for normal operations. Examples of such
    activities include those times when a worker needs to open
    a port to sample the liquid in the surface impoundment, or
    when a worker needs to open a hatch to maintain or repair
    equipment. Following completion of the activity, the
    owner or operator must promptly replace the cover and
    secure the closure device in the closed position, as
    applicable; or

     
    673
     
    ii) To remove accumulated sludge or other residues from the
    bottom of surface impoundment; and
     
    B) Opening of a safety device, as defined in Section 725.981, is
    allowed at any time conditions require doing so to avoid an unsafe
    condition.
     
    3) The owner or operator must inspect the floating membrane cover in
    accordance with the following procedures:
     
    A) The floating membrane cover and its closure devices must be
    visually inspected by the owner or operator to check for defects
    that could result in air pollutant emissions. Defects include, but
    are not limited to, visible cracks, holes, or gaps in the cover section
    seams or between the interface of the cover edge and its foundation
    mountings; broken, cracked, or otherwise damaged seals or gaskets
    on closure devices; and broken or missing hatches, access covers,
    caps, or other closure devices;
     
    B) The owner or operator must perform an initial inspection of the
    floating membrane cover and its closure devices on or before the
    date that the surface impoundment becomes subject to this Section.
    Thereafter, the owner or operator must perform the inspections at
    least once every year except for the special conditions provided for
    in subsection (g) of this Section;
     
    C) In the event that a defect is detected, the owner or operator must
    repair the defect in accordance with the requirements of subsection
    (f) of this Section; and
     
    D) The owner or operator must maintain a record of the inspection in
    accordance with the requirements specified in Section 725.990(c).
     
    d) The owner or operator that controls air pollutant emissions from a surface
    impoundment using a cover vented to a control device must meet the
    requirements specified in subsections (d)(1) through (d)(3) of this Section.
     
    1) The surface impoundment must be covered by a cover and vented directly
    through a closed-vent system to a control device in accordance with the
    following requirements:
     
    A) The cover and its closure devices must be designed to form a
    continuous barrier over the entire surface area of the liquid in the
    surface impoundment;
     

     
    674
    B) Each opening in the cover not vented to the control device must be
    equipped with a closure device. If the pressure in the vapor
    headspace underneath the cover is less than atmospheric pressure
    when the control device is operating, the closure devices must be
    designed to operate such that when the closure device is secured in
    the closed position there are no visible cracks, holes, gaps, or other
    open spaces in the closure device or between the perimeter of the
    cover opening and the closure device. If the pressure in the vapor
    headspace underneath the cover is equal to or greater than
    atmospheric pressure when the control device is operating, the
    closure device must be designed to operate with no detectable
    organic emissions using the procedure specified in Section
    725.984(d);
     
    C) The cover and its closure devices must be made of suitable
    materials that will minimize exposure of the hazardous waste to
    the atmosphere to the extent practical and which will maintain the
    integrity of the cover and closure devices throughout their intended
    service life. Factors to be considered when selecting the materials
    of construction and designing the cover and closure devices must
    include the following: the organic vapor permeability; the effects
    of any contact with the liquid or its vapors managed in the surface
    impoundment; the effects of outdoor exposure to wind, moisture,
    and sunlight; and the operating practices used for the surface
    impoundment on which the cover is installed; and
     
    D) The closed-vent system and control device must be designed and
    operated in accordance with the requirements of Section 725.988.
     
    2) Whenever a hazardous waste is in the surface impoundment, the cover
    must be installed with each closure device secured in the closed position
    and the vapor headspace underneath the cover vented to the control
    device, except as follows:
     
    A) Venting to the control device is not required, and opening of
    closure devices or removal of the cover is allowed at the following
    times:
     
    i) To provide access to the surface impoundment for
    performing routine inspection, maintenance, or other
    activities needed for normal operations. Examples of such
    activities include those times when a worker needs to open
    a port to sample liquid in the surface impoundment, or
    when a worker needs to open a hatch to maintain or repair
    equipment. Following completion of the activity, the
    owner or operator must promptly secure the closure device

     
    675
    in the closed position or reinstall the cover, as applicable,
    to the surface impoundment; or
     
    ii) To remove accumulated sludge or other residues from the
    bottom of the surface impoundment; and
     
    B) Opening of a safety device, as defined in Section 725.981, is
    allowed at any time conditions require doing so to avoid an unsafe
    condition.
     
    3) The owner or operator must inspect and monitor the air emission control
    equipment in accordance with the following procedures:
     
    A) The surface impoundment cover and its closure devices must be
    visually inspected by the owner or operator to check for defects
    that could result in air pollutant emissions. Defects include, but
    are not limited to, visible cracks, holes, or gaps in the cover section
    seams or between the interface of the cover edge and its foundation
    mountings; broken, cracked, or otherwise damaged seals or gaskets
    on closure devices; and broken or missing hatches, access covers,
    caps, or other closure devices;
     
    B) The closed-vent system and control device must be inspected and
    monitored by the owner or operator in accordance with the
    procedures specified in Section 725.988;
     
    C) The owner or operator must perform an initial inspection of the air
    emission control equipment on or before the date that the surface
    impoundment becomes subject to this Section. Thereafter, the
    owner or operator must perform the inspections at least once every
    year except for the special conditions provided for in subsection
    (g) of this Section;
     
    D) In the event that a defect is detected, the owner or operator must
    repair the defect in accordance with the requirements of subsection
    (f) of this Section; and
     
    E) The owner or operator must maintain a record of the inspection in
    accordance with the requirements specified in Section 725.990(c).
     
    e) The owner or operator must transfer hazardous waste to a surface impoundment
    subject to this Section in accordance with the following requirements:
     
    1) Transfer of hazardous waste, except as provided in subsection (e)(2) of
    this Section, to the surface impoundment from another surface
    impoundment subject to this Section or from a tank subject to Section

     
    676
    725.985 must be conducted using continuous hard-piping or another
    closed system that does not allow exposure of the waste to the atmosphere.
    For the purpose of complying with this provision, an individual drain
    system is considered to be a closed system when it meets the requirements
    of subpart RR of 40 CFR 63, “(National Emission Standards for
    Individual Drain Systems),” incorporated by reference in 35 Ill. Adm.
    Code 720.111(b); and
     
    2) The requirements of subsection (e)(1) of this Section do not apply when
    transferring a hazardous waste to the surface impoundment under any of
    the following conditions:
     
    A) The hazardous waste meets the average VO concentration
    conditions specified in Section 725.983(c)(1) at the point of waste
    origination;
     
    B) The hazardous waste has been treated by an organic destruction or
    removal process to meet the requirements in Section
    725.983(c)(2); or
     
    C) The hazardous waste meets the requirements of Section
    725.983(c)(4).
     
    f) The owner or operator must repair each defect detected during an inspection
    performed in accordance with the requirements of subsection (c)(3) or (d)(3) of
    this Section as follows:
     
    1) The owner or operator must make first efforts at repair of the defect no
    later than five calendar days after detection, and repair must be completed
    as soon as possible but no later than 45 calendar days after detection
    except as provided in subsection (f)(2) of this Section; and
     
    2) Repair of a defect may be delayed beyond 45 calendar days if the owner
    or operator determines that repair of the defect requires emptying or
    temporary removal from service of the surface impoundment and no
    alternative capacity is available at the site to accept the hazardous waste
    normally managed in the surface impoundment. In this case, the owner or
    operator must repair the defect the next time the process or unit that is
    generating the hazardous waste managed in the tank stops operation.
    Repair of the defect must be completed before the process or unit resumes
    operation.
     
    g) Following the initial inspection and monitoring of the cover as required by the
    applicable provisions of this Subpart CC, subsequent inspection and monitoring
    may be performed at intervals longer than one year in the case when inspecting or
    monitoring the cover would expose a worker to dangerous, hazardous, or other

     
    677
    unsafe conditions. In this case, the owner or operator may designate the cover as
    an “unsafe to inspect and monitor cover” and comply with all of the following
    requirements:
     
    1) Prepare a written explanation for the cover stating the reasons why the
    cover is unsafe to visually inspect or to monitor, if required; and
     
    2) Develop and implement a written plan and schedule to inspect and
    monitor the cover using the procedures specified in the applicable Section
    of this Subpart CC as frequently as practicable during those times when a
    worker can safely access the cover.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.987 Standards: Containers
     
    a) The provisions of this Section apply to the control of air pollutant emissions from
    containers for which Section 725.983(b) references the use of this Section for
    such air emission control.
     
    b) General requirements.
     
    1) The owner or operator must control air pollutant emissions from each
    container subject to this Section in accordance with the following
    requirements, as applicable to the container, except when the following
    special provisions for waste stabilization processes specified in subsection
    (b)(2) of this Section apply to the container:
     
    A) For a container having a design capacity greater than 0.1 m
    3
    (26
    gal) and less than or equal to 0.46 m
    3
    (120 gal), the owner or
    operator must control air pollutant emissions from the container in
    accordance with the Container Level 1 standards specified in
    subsection (c) of this Section;
     
    B) For a container having a design capacity greater than 0.46 m
    3
    (120
    gal) that is not in light material service, the owner or operator must
    control air pollutant emissions from the container in accordance
    with the Container Level 1 standards specified in subsection (c) of
    this Section; and
     
    C) For a container having a design capacity greater than 0.46 m
    3
    (120
    gal) that is in light material service, the owner or operator must
    control air pollutant emissions from the container in accordance
    with the Container Level 2 standards specified in subsection (d) of
    this Section.
     

     
    678
    2) When a container having a design capacity greater than 0.1 m
    3
    (26 gal) is
    used for treatment of a hazardous waste by a waste stabilization process,
    the owner or operator must control air pollutant emissions from the
    container in accordance with the Container Level 3 standards specified in
    subsection (e) of this Section at those times during the waste stabilization
    process when the hazardous waste in the container is exposed to the
    atmosphere.
     
    c) Container Level 1 standards.
     
    1) A container using Container Level 1 controls is one of the following:
     
    A) A container that meets the applicable USDOT regulations on
    packaging hazardous materials for transportation, as specified in
    subsection (f) of this Section;
     
    B) A container equipped with a cover and closure devices that form a
    continuous barrier over the container openings so that when the
    cover and closure devices are secured in the closed position there
    are no visible holes, gaps, or other open spaces into the interior of
    the container. The cover may be a separate cover installed on the
    container (e.g., a lid on a drum or a suitably secured tarp on a roll-
    off box) or may be an integral part of the container structural
    design (e.g., a “portable tank” or bulk cargo container equipped
    with a screw-type cap); and
     
    C) An open-top container in which an organic-vapor suppressing
    barrier is placed on or over the hazardous waste in the container so
    that no hazardous waste is exposed to the atmosphere. One
    example of such a barrier is application of a suitable organic-vapor
    suppressing foam.
     
    2) A container used to meet the requirements of subsection (c)(1)(B) or
    (c)(1)(C) of this Section must be equipped with covers and closure
    devices, as applicable to the container, that are composed of suitable
    materials to minimize exposure of the hazardous waste to the atmosphere
    and to maintain the equipment integrity for as long as it is in service.
    Factors to be considered in selecting the materials of construction and
    designing the cover and closure devices must include the following: the
    organic vapor permeability; the effects of contact with the hazardous
    waste or its vapor managed in the container; the effects of outdoor
    exposure of the closure device or cover material to wind, moisture, and
    sunlight; and the operating practices for which the container is intended to
    be used.
     
    3) Whenever a hazardous waste is in a container using Container Level 1

     
    679
    controls, the owner or operator must install all covers and closure devices
    for the container, as applicable to the container, and secure and maintain
    each closure device in the closed position except as follows:
     
    A) Opening of a closure device or cover is allowed for the purpose of
    adding hazardous waste or other material to the container as
    follows:
     
    i) In the case when the container is filled to the intended final
    level in one continuous operation, the owner or operator
    must promptly secure the closure devices in the closed
    position and install the covers, as applicable to the
    container, upon conclusion of the filling operation; and
     
    ii) In the case when discrete quantities or batches of material
    intermittently are added to the container over a period of
    time, the owner or operator must promptly secure the
    closure devices in the closed position and install covers, as
    applicable to the container, upon either the container being
    filled to the intended final level; the completion of a batch
    loading after which no additional material will be added to
    the container within 15 minutes; the person performing the
    loading operation leaving the immediate vicinity of the
    container; or the shutdown of the process generating the
    material being added to the container, whichever condition
    occurs first;
     
    B) Opening of a closure device or cover is allowed for the purpose of
    removing hazardous waste from the container as follows:
     
    i) For the purpose of meeting the requirements of this
    Section, an empty container, as defined in 35 Ill. Adm.
    Code 721.107(b), may be open to the atmosphere at any
    time (i.e., covers and closure devices are not required to be
    secured in the closed position on an empty container); and
     
    ii) In the case when discrete quantities or batches of material
    are removed from the container but the container does not
    meet the conditions to be an empty container, as defined in
    35 Ill. Adm. Code 721.107(b), the owner or operator must
    promptly secure the closure devices in the closed position
    and install covers, as applicable to the container, upon the
    completion of a batch removal after which no additional
    material will be removed from the container within 15
    minutes or the person performing the unloading operation
    leaves the immediate vicinity of the container, whichever

     
    680
    condition occurs first;
     
    C) Opening of a closure device or cover is allowed when access inside
    the container is needed to perform routine activities other than
    transfer of hazardous waste. Examples of such activities include
    those times when a worker needs to open a port to measure the
    depth of or sample the material in the container, or when a worker
    needs to open a manhole hatch to access equipment inside the
    container. Following completion of the activity, the owner or
    operator must promptly secure the closure device in the closed
    position or reinstall the cover, as applicable to the container;
     
    D) Opening of a spring-loaded, pressure-vacuum relief valve,
    conservation vent, or similar type of pressure relief device that
    vents to the atmosphere is allowed during normal operations for
    the purpose of maintaining the container internal pressure in
    accordance with the design specifications of the container. The
    device must be designed to operate with no detectable organic
    emissions when the device is secured in the closed position. The
    settings at which the device opens must be established so that the
    device remains in the closed position whenever the internal
    pressure of the container is within the internal pressure operating
    range determined by the owner or operator based on container
    manufacturer recommendations, applicable regulations, fire
    protection and prevention codes, standard engineering codes and
    practices, or other requirements for the safe handling of
    flammable, ignitable, explosive, reactive, or hazardous materials.
    Examples of normal operating conditions that may require these
    devices to open are during those times when the internal pressure
    of the container exceeds the internal pressure operating range for
    the container as a result of loading operations or diurnal ambient
    temperature fluctuations; and
     
    E) Opening of a safety device, as defined in Section 725.981, is
    allowed at any time conditions require doing so to avoid an unsafe
    condition.
     
    4) The owner or operator of containers using Container Level 1 controls must
    inspect the containers and their covers and closure devices as follows:
     
    A) In the case when a hazardous waste already is in the container at
    the time the owner or operator first accepts possession of the
    container at the facility and the container is not emptied within 24
    hours after the container is accepted at the facility (i.e., it does not
    meet the conditions for an empty container as specified in 35 Ill.
    Adm. Code 721.107(b)), the owner or operator must visually

     
    681
    inspect the container and its cover and closure devices to check for
    visible cracks, holes, gaps, or other open spaces into the interior of
    the container when the cover and closure devices are secured in the
    closed position. The container visual inspection must be
    conducted on or before the date on which the container is accepted
    at the facility (i.e., the date when the container becomes subject to
    the Subpart CC container standards). For the purposes of this
    requirement, the date of acceptance is the date of signature that the
    facility owner or operator enters on Item 20 of the Uniform
    Hazardous Waste Manifest incorporated by reference in Appendix
    A to 35 Ill. Adm. Code 722, as set forth in the appendix to 40 CFR
    262 (USEPA Uniform Hazardous Waste Manifest and Instructions
    (EPA Forms 8700-22 and 8700-22A 8700–22a and Their
    Instructions)), incorporated by reference in 35 Ill. Adm. Code
    720.111(b), as required under Section 725.171. If a defect is
    detected, the owner or operator must repair the defect in
    accordance with the requirements of subsection (c)(4)(C) of this
    Section;
     
    B) In the case when a container used for managing hazardous waste
    remains at the facility for a period of one year or more, the owner
    or operator must visually inspect the container and its cover and
    closure devices initially and thereafter, at least once every 12
    months, to check for visible cracks, holes, gaps, or other open
    spaces into the interior of the container when the cover and closure
    devices are secured in the closed position. If a defect is detected,
    the owner or operator must repair the defect in accordance with the
    requirements of subsection (c)(4)(C) of this Section; and
     
    C) When a defect is detected in the container, cover, or closure
    devices, the owner or operator must make first efforts at repair of
    the defect no later than 24 hours after detection, and repair must be
    completed as soon as possible but no later than five calendar days
    after detection. If repair of a defect cannot be completed within
    five calendar days, then the hazardous waste must be removed
    from the container and the container must not be used to manage
    hazardous waste until the defect is repaired.
     
    5) The owner or operator must maintain at the facility a copy of the
    procedure used to determine that containers with capacity of 0.46 m
    3
    (120
    gal) or greater which do not meet applicable USDOT regulations, as
    specified in subsection (f) of this Section, are not managing hazardous
    waste in light material service.
     
    d) Container Level 2 standards.
     

     
    682
    1) A container using Container Level 2 controls is one of the following:
     
    A) A container that meets the applicable USDOT regulations on
    packaging hazardous materials for transportation as specified in
    subsection (f) of this Section;
     
    B) A container that operates with no detectable organic emissions, as
    defined in Section 725.981, and determined in accordance with the
    procedure specified in subsection (g) of this Section; and
     
    C) A container that has been demonstrated within the preceding 12
    months to be vapor-tight by using Method 27 (Determination of
    Vapor Tightness of Gasoline Delivery Tank Using Pressure-
    Vacuum Test) in appendix A to 40 CFR 60, appendix A, Method
    27 (Test Methods), incorporated by reference in 35 Ill. Adm. Code
    720.111(b), in accordance with the procedure specified in
    subsection (h) of this Section.
     
    2) Transfer of hazardous waste into or out of a container using Container
    Level 2 controls must be conducted in such a manner as to minimize
    exposure of the hazardous waste to the atmosphere, to the extent practical,
    considering the physical properties of the hazardous waste and good
    engineering and safety practices for handling flammable, ignitable,
    explosive, reactive or other hazardous materials. Examples of container
    loading procedures that the USEPA considers to meet the requirements of
    this subsection (d)(2) include using any one of the following: a
    submerged-fill pipe or other submerged-fill method to load liquids into the
    container; a vapor-balancing system or a vapor-recovery system to collect
    and control the vapors displaced from the container during filling
    operations; or a fitted opening in the top of a container through which the
    hazardous waste is filled and subsequently purging the transfer line before
    removing it from the container opening.
     
    3) Whenever a hazardous waste is in a container using Container Level 2
    controls, the owner or operator must install all covers and closure devices
    for the container, and secure and maintain each closure device in the
    closed position, except as follows:
     
    A) Opening of a closure device or cover is allowed for the purpose of
    adding hazardous waste or other material to the container as
    follows:
     
    i) In the case when the container is filled to the intended final
    level in one continuous operation, the owner or operator
    must promptly secure the closure devices in the closed
    position and install the covers, as applicable to the

     
    683
    container, upon conclusion of the filling operation; and
     
    ii) In the case when discrete quantities or batches of material
    intermittently are added to the container over a period of
    time, the owner or operator must promptly secure the
    closure devices in the closed position and install covers, as
    applicable to the container, upon either the container being
    filled to the intended final level; the completion of a batch
    loading after which no additional material will be added to
    the container within 15 minutes; the person performing the
    loading operation leaving the immediate vicinity of the
    container; or the shutdown of the process generating the
    material being added to the container, whichever condition
    occurs first;
     
    B) Opening of a closure device or cover is allowed for the purpose of
    removing hazardous waste from the container as follows:
     
    i) For the purpose of meeting the requirements of this
    Section, an empty container as defined in 35 Ill. Adm.
    Code 721.107(b) may be open to the atmosphere at any
    time (i.e., covers and closure devices are not required to be
    secured in the closed position on an empty container); and
     
    ii) In the case when discrete quantities or batches of material
    are removed from the container but the container does not
    meet the conditions to be an empty container as defined in
    35 Ill. Adm. Code 721.107(b), the owner or operator must
    promptly secure the closure devices in the closed position
    and install covers, as applicable to the container, upon the
    completion of a batch removal after which no additional
    material will be removed from the container within 15
    minutes or the person performing the unloading operation
    leaves the immediate vicinity of the container, whichever
    condition occurs first;
     
    C) Opening of a closure device or cover is allowed when access inside
    the container is needed to perform routine activities other than
    transfer of hazardous waste. Examples of such activities include
    those times when a worker needs to open a port to measure the
    depth of or sample the material in the container, or when a worker
    needs to open a manhole hatch to access equipment inside the
    container. Following completion of the activity, the owner or
    operator must promptly secure the closure device in the closed
    position or reinstall the cover, as applicable to the container;
     

     
    684
    D) Opening of a spring-loaded, pressure-vacuum relief valve,
    conservation vent, or similar type of pressure relief device that
    vents to the atmosphere is allowed during normal operations for
    the purpose of maintaining the internal pressure of the container in
    accordance with the container design specifications. The device
    must be designed to operate with no detectable organic emission
    when the device is secured in the closed position. The settings at
    which the device opens must be established so that the device
    remains in the closed position whenever the internal pressure of
    the container is within the internal pressure operating range
    determined by the owner or operator based on container
    manufacturer recommendations, applicable regulations, fire
    protection and prevention codes, standard engineering codes and
    practices, or other requirements for the safe handling of
    flammable, ignitable, explosive, reactive, or hazardous materials.
    Examples of normal operating conditions that may require these
    devices to open are during those times when the internal pressure
    of the container exceeds the internal pressure operating range for
    the container as a result of loading operations or diurnal ambient
    temperature fluctuations; and
     
    E) Opening of a safety device, as defined in Section 725.981, is
    allowed at any time conditions require doing so to avoid an unsafe
    condition.
     
    4) The owner or operator of containers using Container Level 2 controls must
    inspect the containers and their covers and closure devices as follows:
     
    A) In the case when a hazardous waste already is in the container at
    the time the owner or operator first accepts possession of the
    container at the facility and the container is not emptied within 24
    hours after the container is accepted at the facility (i.e., it does not
    meet the conditions for an empty container as specified in 35 Ill.
    Adm. Code 721.107(b)), the owner or operator must visually
    inspect the container and its cover and closure devices to check for
    visible cracks, holes, gaps, or other open spaces into the interior of
    the container when the cover and closure devices are secured in the
    closed position. The container visual inspection must be
    conducted on or before the date on which the container is accepted
    at the facility (i.e., the date when the container becomes subject to
    the Subpart CC container standards). For the purposes of this
    requirement, the date of acceptance is the date of signature that the
    facility owner or operator enters on Item 20 of the Uniform
    Hazardous Waste Manifest, in the appendix to 40 CFR 262
    incorporated by reference in Appendix A to 35 Ill. Adm. Code 722
    (Uniform Hazardous Waste Manifest and Instructions (USEPA

     
    685
    Forms 8700-22 and 8700-22A 8700-22a and Their Instructions)),
    as required under Section 725.171. If a defect is detected, the
    owner or operator must repair the defect in accordance with the
    requirements of subsection (d)(4)(C) of this Section;
     
    B) In the case when a container used for managing hazardous waste
    remains at the facility for a period of one year or more, the owner
    or operator must visually inspect the container and its cover and
    closure devices initially and thereafter, at least once every 12
    months, to check for visible cracks, holes, gaps, or other open
    spaces into the interior of the container when the cover and closure
    devices are secured in the closed position. If a defect is detected,
    the owner or operator must repair the defect in accordance with the
    requirements of subsection (d)(4)(C) of this Section; and
     
    C) When a defect is detected in the container, cover, or closure
    devices, the owner or operator must make first efforts at repair of
    the defect no later than 24 hours after detection, and repair must be
    completed as soon as possible but no later than five calendar days
    after detection. If repair of a defect cannot be completed within
    five calendar days, then the hazardous waste must be removed
    from the container and the container must not be used to manage
    hazardous waste until the defect is repaired.
     
    e) Container Level 3 standards.
     
    1) A container using Container Level 3 controls is one of the following:
     
    A) A container that is vented directly through a closed-vent system to
    a control device in accordance with the requirements of subsection
    (e)(2)(B) of this Section; or
     
    B) A container that is vented inside an enclosure that is exhausted
    through a closed-vent system to a control device in accordance
    with the requirements of subsections (e)(2)(A) and (e)(2)(B) of this
    Section.
     
    2) The owner or operator must meet the following requirements, as
    applicable to the type of air emission control equipment selected by the
    owner or operator:
     
    A) The container enclosure must be designed and operated in
    accordance with the criteria for a permanent total enclosure as
    specified in “Procedure T—Criteria for and Verification of a
    Permanent or Temporary Total Enclosure” under appendix B to 40
    CFR 52.741, appendix B, incorporated by reference in 35 Ill. Adm.

     
    686
    Code 720.111(b) (VOM Measurement Techniques for Capture
    Efficiency). The enclosure may have permanent or temporary
    openings to allow worker access; passage of containers through the
    enclosure by conveyor or other mechanical means; entry of
    permanent mechanical or electrical equipment; or direct airflow
    into the enclosure. The owner or operator must perform the
    verification procedure for the enclosure as specified in Section 5.0
    to “Procedure T—Criteria for and Verification of a Permanent or
    Temporary Total Enclosure” initially when the enclosure is first
    installed and, thereafter, annually; and
     
    B) The closed-vent system and control device must be designed and
    operated in accordance with the requirements of Section 725.988.
     
    3) Safety devices, as defined in Section 725.981, may be installed and
    operated as necessary on any container, enclosure, closed-vent system, or
    control device used to comply with the requirements of subsection (e)(1)
    of this Section.
     
    4) Owners and operators using Container Level 3 controls in accordance with
    the provisions of this Subpart CC must inspect and monitor the closed-
    vent systems and control devices, as specified in Section 725.988.
     
    5) Owners and operators that use Container Level 3 controls in accordance
    with the provisions of this Subpart CC must prepare and maintain the
    records specified in Section 725.990(d).
     
    6) The transfer of hazardous waste into or out of a container using Container
    Level 3 controls must be conducted in such a manner as to minimize
    exposure of the hazardous waste to the atmosphere, to the extent practical
    considering the physical properties of the hazardous waste and good
    engineering and safety practices for handling flammable, ignitable,
    explosive, reactive, or other hazardous materials. Examples of container
    loading procedures that USEPA considers to meet the requirements of this
    subsection (e)(6) include using any one of the following: the use of a
    submerged-fill pipe or other submerged-fill method to load liquids into the
    container; the use of a vapor-balancing system or a vapor-recovery system
    to collect and control the vapors displaced from the container during filling
    operations; or the use of a fitted opening in the top of a container through
    which the hazardous waste is filled and subsequently purging the transfer
    line before removing it from the container opening.
     
    f) For the purpose of compliance with subsection (c)(1)(A) or (d)(1)(A) of this
    Section, containers must be used that meet the applicable USDOT regulations on
    packaging hazardous materials for transportation as follows:
     

     
    687
    1) The container meets the applicable requirements specified by USDOT in
    49 CFR 178, “(Specifications for Packaging),” or 49 CFR 179,
    “(Specifications for Tank Cars),” both each incorporated by reference in
    35 Ill. Adm. Code 720.111(b);
     
    2) Hazardous waste is managed in the container in accordance with the
    applicable requirements specified by USDOT in subpart B of 49 CFR 107,
    “(Exemptions”;), 49 CFR 172, “(Hazardous Materials Table, Special
    Provisions, Hazardous Materials Communications, Emergency Response
    Information, and Training Requirements”;), 49 CFR 173, “(Shippers—
    General Requirements for Shipments and Packages”;), and 49 CFR 180,
    “(Continuing Qualification and Maintenance of Packagings),” each
    incorporated by reference in 35 Ill. Adm. Code 720.111(b);
     
    3) For the purpose of complying with this Subpart CC, no exceptions to the
    federal 49 CFR 178 or 179 regulations are allowed, except as provided for
    in subsection (f)(4) of this Section; and
     
    4) For a lab pack that is managed in accordance with the USDOT
    requirements of 49 CFR 178 (Specifications for Packagings) for the
    purpose of complying with this Subpart CC, an owner or operator may
    comply with the exceptions for combination packagings specified by
    USDOT in 49 CFR 173.12(b) (Exceptions for Shipments of Waste
    Materials), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    g) To determine compliance with the no detectable organic emissions requirements
    of subsection (d)(1)(B) of this Section, the procedure specified in Section
    725.984(d) must be used.
     
    1) Each potential leak interface (i.e., a location where organic vapor leakage
    could occur) on the container, its cover, and associated closure devices, as
    applicable to the container, must be checked. Potential leak interfaces that
    are associated with containers include, but are not limited to: the interface
    of the cover rim and the container wall; the periphery of any opening on
    the container or container cover and its associated closure device; and the
    sealing seat interface on a spring-loaded pressure-relief valve.
     
    2) The test must be performed when the container is filled with a material
    having a volatile organic concentration representative of the range of
    volatile organic concentrations for the hazardous wastes expected to be
    managed in this type of container. During the test, the container cover and
    closure devices must be secured in the closed position.
     
    h) The procedure for determining a container to be vapor-tight using Method 27 of
    40 CFR 60, appendix A for the purpose of complying with subsection (d)(1)(C) of
    this Section is as follows:

     
    688
     
    1) The test must be performed in accordance with Method 27 of 40 CFR 60,
    appendix A, incorporated by reference in 35 Ill. Adm. Code 720.111(b);
     
    2) A pressure measurement device must be used that has a precision of ±2.5
    mm (0.10 inch) water and that is capable of measuring above the pressure
    at which the container is to be tested for vapor tightness; and
     
    3) If the test results determined by Method 27 indicate that the container
    sustains a pressure change less than or equal to 750 Pascals (0.11 psig)
    within five minutes after it is pressurized to a minimum of 4,500 Pascals
    (0.65 psig), then the container is determined to be vapor-tight.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.990 Recordkeeping Requirements
     
    a) Each owner or operator of a facility subject to the requirements in this Subpart
    CC must record and maintain the information specified in subsections (b) through
    (j) of this Section, as applicable to the facility. Except for air emission control
    equipment design documentation and information required by subsection (j) of
    this Section, records required by this Section must be maintained in the operating
    record for a minimum of three years. Air emission control equipment design
    documentation must be maintained in the operating record until the air emission
    control equipment is replaced or is otherwise no longer in service. Information
    required by subsections (i) and (j) of this Section must be maintained in the
    operating record for as long as the waste management unit is not using air
    emission controls specified in Sections 725.985 through 725.988, in accordance
    with the conditions specified in Section 725.980(d) or (b)(7), respectively.
     
    b) The owner or operator of a tank using air emission controls in accordance with
    the requirements of Section 725.985 must prepare and maintain records for the
    tank that include the following information:
     
    1) For each tank using air emission controls in accordance with the
    requirements of Section 725.985 of this Subpart CC, the owner or operator
    must record the following information:
     
    A) A tank identification number (or other unique identification
    description as selected by the owner or operator); and
     
    B) A record for each inspection required by Section 725.985 that
    includes the following information:
     
    i) Date inspection was conducted; and
     

     
    689
    ii) For each defect detected during the inspection, the location
    of the defect, a description of the defect, the date of
    detection, and corrective action taken to repair the defect.
    In the event that repair of the defect is delayed in
    accordance with the provisions of Section 725.985, the
    owner or operator must also record the reason for the delay
    and the date that completion of repair of the defect is
    expected; and
     
    2) In addition to the information required by subsection (b)(1) of this
    Section, the owner or operator must record the following information, as
    applicable to the tank:
     
    A) The owner or operator using a fixed roof to comply with the Tank
    Level 1 control requirements specified in Section 725.985(c) must
    prepare and maintain records for each determination for the
    maximum organic vapor pressure of the hazardous waste in the
    tank performed in accordance with the requirements of Section
    725.985(c). The records must include the date and time the
    samples were collected, the analysis method used, and the analysis
    results;
     
    B) The owner or operator using an internal floating roof to comply
    with the Tank Level 2 control requirements specified in Section
    725.985(e) must prepare and maintain documentation describing
    the floating roof design;
     
    C) Owners and operators using an external floating roof to comply
    with the Tank Level 2 control requirements specified in Section
    725.985(f) must prepare and maintain the following records:
     
    i) Documentation describing the floating roof design and the
    dimensions of the tank; and
     
    ii) Records for each seal gap inspection required by Section
    725.985(f)(3) describing the results of the seal gap
    measurements. The records must include the date that the
    measurements were performed, the raw data obtained for
    the measurements, and the calculations of the total gap
    surface area. In the event that the seal gap measurements
    do not conform to the specifications in Section
    725.985(f)(1), the records must include a description of the
    repairs that were made, the date the repairs were made, and
    the date the tank was emptied, if necessary.
     
    D) Each owner or operator using an enclosure to comply with the

     
    690
    Tank Level 2 control requirements specified in Section 725.985(i)
    must prepare and maintain the following records:
     
    i) Records for the most recent set of calculations and
    measurements performed by the owner or operator to verify
    that the enclosure meets the criteria of a permanent total
    enclosure as specified in “Procedure T--Criteria for and
    Verification of a Permanent or Temporary Total Enclosure”
    under appendix B to 40 CFR 52.741, appendix B (VOM
    Measurement Techniques for Capture Efficiency),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b);
    and
     
    ii) Records required for the closed-vent system and control
    device in accordance with the requirements of subsection
    (e) of this Section.
     
    c) The owner or operator of a surface impoundment using air emission controls in
    accordance with the requirements of Section 725.986 must prepare and maintain
    records for the surface impoundment that include the following information:
     
    1) A surface impoundment identification number (or other unique
    identification description as selected by the owner or operator);
     
    2) Documentation describing the floating membrane cover or cover design,
    as applicable to the surface impoundment, that includes information
    prepared by the owner or operator or provided by the cover manufacturer
    or vendor describing the cover design, and certification by the owner or
    operator that the cover meets the specifications listed in Section
    725.986(c);
     
    3) A record for each inspection required by Section 725.986 that includes the
    following information:
     
    A) Date inspection was conducted; and
     
    B) For each defect detected during the inspection the following
    information: the location of the defect, a description of the defect,
    the date of detection, and corrective action taken to repair the
    defect. In the event that repair of the defect is delayed in
    accordance with the provisions of Section 725.986(f), the owner or
    operator must also record the reason for the delay and the date that
    completion of repair of the defect is expected; and
     
    4) For a surface impoundment equipped with a cover and vented through a
    closed-vent system to a control device, the owner or operator must prepare

     
    691
    and maintain the records specified in subsection (e) of this Section.
     
    d) The owner or operator of containers using Container Level 3 air emission controls
    in accordance with the requirements of Section 725.987 must prepare and
    maintain records that include the following information:
     
    1) Records for the most recent set of calculations and measurements
    performed by the owner or operator to verify that the enclosure meets the
    criteria of a permanent total enclosure as specified in “Procedure T--
    Criteria for and Verification of a Permanent or Temporary Total
    Enclosure” under appendix B to 40 CFR 52.741, appendix B, incorporated
    by reference in 35 Ill. Adm. Code 720.111(b) (VOM Measurement
    Techniques for Capture Efficiency); and
     
    2) Records required for the closed-vent system and control device in
    accordance with the requirements of subsection (e) of this Section.
     
    e) The owner or operator using a closed-vent system and control device in
    accordance with the requirements of Section 725.988 must prepare and maintain
    records that include the following information:
     
    1) Documentation for the closed-vent system and control device that includes
    the following documentation:
     
    A) Certification that is signed and dated by the owner or operator
    stating that the control device is designed to operate at the
    performance level documented by a design analysis as specified in
    subsection (e)(1)(B) of this Section or by performance tests as
    specified in subsection (e)(1)(C) of this Section when the tank,
    surface impoundment, or container is or would be operating at
    capacity or the highest level reasonably expected to occur;
     
    B) If a design analysis is used, then design documentation, as
    specified in Section 725.935(b)(4). The documentation must
    include information prepared by the owner or operator or provided
    by the control device manufacturer or vendor that describes the
    control device design in accordance with Section 725.935(b)(4)(C)
    and certification by the owner or operator that the control
    equipment meets the applicable specifications;
     
    C) If performance tests are used, then a performance test plan as
    specified in Section 725.935(b)(3) and all test results;
     
    D) Information as required by Section 725.935(c)(1) and (c)(2), as
    applicable;
     

     
    692
    E) An owner or operator must record, on a semiannual basis, the
    following information for those planned routine maintenance
    operations that would require the control device not to meet the
    requirements of Section 725.988(c)(1)(A), (c)(1)(B), or (c)(1)(C),
    as applicable:
     
    i) A description of the planned routine maintenance that is
    anticipated to be performed for the control device during
    the next six-month period. This description must include
    the type of maintenance necessary, planned frequency of
    maintenance, and lengths of maintenance periods; and
     
    ii) A description of the planned routine maintenance that was
    performed for the control device during the previous six-
    month period. This description must include the type of
    maintenance performed and the total number of hours
    during those six months that the control device did not
    meet the requirements of Section 725.988(c)(1)(A),
    (c)(1)(B), or (c)(1)(C), as applicable, due to planned
    routine maintenance;
     
    F) An owner or operator must record the following information for
    those unexpected control device system malfunctions that would
    require the control device not to meet the requirements of Section
    725.988(c)(1)(A), (c)(1)(B), or (c)(1)(C), as applicable:
     
    i) The occurrence and duration of each malfunction of the
    control device system;
     
    ii) The duration of each period during a malfunction when
    gases, vapors, or fumes are vented from the waste
    management unit through the closed-vent system to the
    control device while the control device is not properly
    functioning; and
     
    iii) Actions taken during periods of malfunction to restore a
    malfunctioning control device to its normal or usual
    manner of operation; and
     
    G) Records of the management of carbon removed from a carbon
    adsorption system conducted in accordance with Section
    725.988(c)(3)(B).
     
    f) The owner or operator of a tank, surface impoundment, or container exempted
    from standards in accordance with the provisions of Section 725.983(c) must
    prepare and maintain the following records, as applicable:

     
    693
     
    1) For tanks, surface impoundments, or containers exempted under the
    hazardous waste organic concentration conditions specified in Section
    725.983 (c)(1) or 725.984(c)(2)(A) through (c)(2)(F), the owner or
    operator must record the information used for each waste determination
    (e.g., test results, measurements, calculations, and other documentation) in
    the facility operating log. If analysis results for waste samples are used
    for the waste determination, then the owner or operator must record the
    date, time, and location that each waste sample is collected in accordance
    with the applicable requirements of Section 725.984; and
     
    2) For tanks, surface impoundments, or containers exempted under the
    provisions of Section 725.983(c)(2)(G) or (c)(2)(H), the owner or operator
    must record the identification number for the incinerator, boiler, or
    industrial furnace in which the hazardous waste is treated.
     
    g) An owner or operator designating a cover as “unsafe to inspect and monitor”
    pursuant to Section 725.985(l) must record in a log that is kept in the facility
    operating record the following information: the identification numbers for waste
    management units with covers that are designated as “unsafe to inspect and
    monitor,” the explanation for each cover stating why the cover is unsafe to inspect
    and monitor, and the plan and schedule for inspecting and monitoring each cover.
     
    h) The owner or operator of a facility that is subject to this Subpart CC and to the
    control device standards in federal subpart VV of 40 CFR 60 (Standards of
    Performance for Equipment Leaks of VOC in the Synthetic Organic Chemicals
    Manufacturing Industry), or subpart V of 40 CFR 61 (National Emission Standard
    for Equipment Leaks (Fugitive Emission Sources), each incorporated by reference
    in 35 Ill. Adm. Code 270.111, may elect to demonstrate compliance with the
    applicable Sections of this Subpart by documentation either pursuant to this
    Subpart CC, or pursuant to the provisions of subpart VV of 40 CFR 60 or subpart
    V of 40 CFR 61, to the extent that the documentation required by 40 CFR 60 or
    61 duplicates the documentation required by this Section.
     
    i) For each tank or container not using air emission controls specified in Sections
    725.985 through 725.988 in accordance with the conditions specified in Section
    725.980(d), the owner or operator must record and maintain the following
    information:
     
    1) A list of the individual organic peroxide compounds manufactured at the
    facility that meet the conditions specified in Section 725.980(d)(1);
     
    2) A description of how the hazardous waste containing the organic peroxide
    compounds identified pursuant to subsection (i)(1) are managed at the
    facility in tanks and containers. This description must include the
    following information:

     
    694
     
    A) For the tanks used at the facility to manage this hazardous waste,
    sufficient information must be provided to describe each tank: a
    facility identification number for the tank, the purpose and
    placement of this tank in the management train of this hazardous
    waste, and the procedures used to ultimately dispose of the
    hazardous waste managed in the tanks; and
     
    B) For containers used at the facility to manage this hazardous waste,
    sufficient information must be provided to describe the following
    for each container: a facility identification number for the
    container or group of containers; the purpose and placement of this
    container or group of containers in the management train of this
    hazardous waste; and the procedures used to ultimately dispose of
    the hazardous waste handled in the containers; and
     
    3) An explanation of why managing the hazardous waste containing the
    organic peroxide compounds identified pursuant to subsection (i)(1) of
    this Section in the tanks or containers identified pursuant to subsection
    (i)(2) of this Section would create an undue safety hazard if the air
    emission controls specified in Sections 725.985 through 725.988 were
    installed and operated on these waste management units. This explanation
    must include the following information:
     
    A) For tanks used at the facility to manage this hazardous waste,
    sufficient information must be provided to explain: how use of the
    required air emission controls on the tanks would affect the tank
    design features and facility operating procedures currently used to
    prevent an undue safety hazard during the management of this
    hazardous waste in the tanks; and why installation of safety
    devices on the required air emission controls, as allowed under this
    Subpart CC, would not address those situations in which
    evacuation of tanks equipped with these air emission controls is
    necessary and consistent with good engineering and safety
    practices for handling organic peroxides; and
     
    B) For containers used at the facility to manage this hazardous waste,
    sufficient information must be provided to explain: how use of the
    required air emission controls on the containers would affect the
    container design features and handling procedures currently used
    to prevent an undue safety hazard during management of this
    hazardous waste in the containers; and why installation of safety
    devices on the required air emission controls, as allowed under this
    Subpart CC, would not address those situations in which
    evacuation of containers equipped with these air emission controls
    is necessary and consistent with good engineering and safety

     
    695
    practices for handling organic peroxides.
     
    j) For each hazardous waste management unit not using air emission controls
    specified in Sections 725.985 through 725.988 in accordance with the provisions
    of Section 725.980(b)(7), the owner and operator must record and maintain the
    following information:
     
    1) The certification that the waste management unit is equipped with and
    operating air emission controls in accordance with the requirements of an
    applicable federal Clean Air Act regulation codified under 40 CFR 60, 61,
    or 63; and
     
    2) An identification of the specific federal requirements codified under 40
    CFR 60, 61, or 63 with which the waste management unit is in
    compliance.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART DD: CONTAINMENT BUILDINGS
     
    Section 725.1101 Design and Operating Standards
     
    a) All containment buildings must comply with the following design and operating
    standards:
     
    1) The containment building must be completely enclosed with a floor, walls,
    and a roof to prevent exposure to the elements (e.g. precipitation, wind,
    run on) and to assure containment of managed wastes;
     
    2) The floor and containment walls of the unit, including the secondary
    containment system if required under subsection (b) of this Section, must
    be designed and constructed of materials of sufficient strength and
    thickness to support themselves, the waste contents, and any personnel
    and heavy equipment that operate within the unit, and to prevent failure
    due to pressure gradients, settlement, compression, or uplift, physical
    contact with the hazardous wastes to which they are exposed; climatic
    conditions; and the stresses of daily operation, including the movement of
    heavy equipment within the unit and contact of such equipment with
    containment walls. The unit must be designed so that it has sufficient
    structural strength to prevent collapse or other failure. All surfaces to be
    in contact with hazardous wastes must be chemically compatible with
    those wastes. The containment building must meet the structural integrity
    requirements established by professional organizations generally
    recognized by the industry such as the American Concrete Institute [ACI]
    and the American Society of Testing Materials [ASTM]. If appropriate to
    the nature of the waste management operation to take place in the unit, an

     
    696
    exception to the structural strength requirement may be made for light-
    weight doors and windows that meet these criteria:
     
    A) They provide an effective barrier against fugitive dust emissions
    under subsection (c)(1)(D) of this Section; and
     
    B) The unit is designed and operated in a fashion that assures that
    wastes will not actually come in contact with these openings;
     
    3) Incompatible hazardous wastes or treatment reagents must not be placed
    in the unit or its secondary containment system if they could cause the unit
    or secondary containment system to leak, corrode, or otherwise fail; and
     
    4) A containment building must have a primary barrier designed to withstand
    the movement of personnel, waste, and handling equipment in the unit
    during the operating life of the unit and appropriate for the physical and
    chemical characteristics of the waste to be managed.
     
    b) For a containment building used to manage hazardous wastes containing free
    liquids or treated with free liquids (the presence of which is determined by the
    paint filter test, a visual examination, or other appropriate means), the owner or
    operator must include the following design features:
     
    1) A primary barrier designed and constructed of materials to prevent the
    migration of hazardous constituents into the barrier (e.g., a geomembrane
    covered by a concrete wear surface).
     
    2) A liquid collection and removal system to minimize the accumulation of
    liquid on the primary barrier of the containment building:
     
    A) The primary barrier must be sloped to drain liquids to the
    associated collection system; and
     
    B) Liquids and waste must be collected and removed to minimize
    hydraulic head on the containment system at the earliest
    practicable time.
     
    3) A secondary containment system including a secondary barrier designed
    and constructed to prevent migration of hazardous constituents into the
    barrier, and a leak detection system that is capable of detecting failure of
    the primary barrier and collecting accumulated hazardous wastes and
    liquids at the earliest practicable time.
     
    A) The requirements of the leak detection component of the secondary
    containment system are satisfied by installation of a system that is,
    at a minimum, as follows:

     
    697
     
    i) It is constructed with a bottom slope of 1 percent or more;
    and
     
    ii) It is constructed of a granular drainage material with a
    hydraulic conductivity of 1 x 10
    -2
    cm/sec or more and a
    thickness of 12 inches (30.5 cm) or more, or constructed of
    synthetic or geonet drainage materials with a transmissivity
    of 3 x 10
    -5
    m
    2
    /sec or more.
     
    B) If treatment is to be conducted in the building, an area in which
    such treatment will be conducted must be designed to prevent the
    release of liquids, wet materials, or liquid aerosols to other
    portions of the building.
     
    C) The secondary containment system must be constructed of
    materials that are chemically resistant to the waste and liquids
    managed in the containment building and of sufficient strength and
    thickness to prevent collapse under the pressure exerted by
    overlaying materials and by any equipment used in the
    containment building. (Containment buildings can serve as
    secondary containment systems for tanks placed within the
    building under certain conditions. A containment building can
    serve as an external liner system for a tank, provided it meets the
    requirements of Section 725.293(d)(1). In addition, the
    containment building must meet the requirements of subsections
    725.293(b) and (c) to be an acceptable secondary containment
    system for a tank.)
     
    4) For existing units other than 90-day generator units, USEPA may delay
    the secondary containment requirement for up to two years, based on a
    demonstration by the owner or operator that the unit substantially meets
    the standards of this Subpart DD. In making this demonstration, the
    owner or operator must do each of the following:
     
    A) Provide written notice to USEPA of their request by November 16,
    1992. This notification must describe the unit and its operating
    practices with specific reference to the performance of existing
    systems, and specific plans for retrofitting the unit with secondary
    containment;
     
    B) Respond to any comments from USEPA on these plans within 30
    days; and
     
    C) Fulfill the terms of the revised plans, if such plans are approved by
    USEPA.

     
    698
     
    c) Owners or operators of all containment buildings must do each of the following:
     
    1) Use controls and practice to ensure containment of the hazardous waste
    within the unit, and at a minimum do each of the following:
     
    A) Maintain the primary barrier to be free of significant cracks, gaps,
    corrosion, or other deterioration that could cause hazardous waste
    to be released from the primary barrier;
     
    B) Maintain the level of the stored or treated hazardous waste within
    the containment walls of the unit so that the height of any
    containment wall is not exceeded;
     
    C) Take measures to prevent the tracking of hazardous waste out of
    the unit by personnel or by equipment used in handling the waste.
    An area must be designated to decontaminate equipment and any
    rinsate must be collected and properly managed; and
     
    D) Take measures to control fugitive dust emissions such that any
    openings (doors, windows, vents, cracks, etc.) exhibit no visible
    emissions (see Method 22 (Visual Determination of Fugitive
    Emissions from Material Sources and Smoke Emissions from
    Flares) in appendix A to 40 CFR 60, appendix A, Method 22 (Test
    Methods) - Visual Determination of Fugitive Emissions from
    Material Sources and Smoke Emissions from Flares), incorporated
    by reference in 35 Ill. Adm. Code 720.111(b). In addition, all
    associated particulate collection devices (e.g., fabric filter,
    electrostatic precipitator) must be operated and maintained with
    sound air pollution control practices (see 40 CFR 60 for guidance).
    This state of no visible emissions must be maintained effectively at
    all times during routine operating and maintenance conditions,
    including when vehicles and personnel are entering and exiting the
    unit;
     
    BOARD NOTE: At 40 CFR 265.1101(c)(1)(iv) (2004), USEPA
    cites “40 CFR part 60, subpart 292.” At 57 Fed. Reg. 37217
    (August 18, 1992), USEPA repeats this citation in the preamble
    discussion of adoption of the rules. No such provision exists in the
    Code of Federal Regulations. The Board has chosen to use the
    more general citation: “40 CFR 60.”
     
    2) Obtain certification by a qualified registered professional engineer (PE)
    that the containment building design meets the requirements of
    subsections (a) through (c) of this Section. For units placed into operation
    prior to February 18, 1993, this certification must be placed in the

     
    699
    facility’s operating record (on-site files for generators that are not formally
    required to have operating records) no later than 60 days after the date of
    initial operation of the unit. After February 18, 1993, PE certification will
    be required prior to operation of the unit;
     
    3) Throughout the active life of the containment building, if the owner or
    operator detects a condition that could lead to or has caused a release of
    hazardous waste, must repair the condition promptly. In addition,
    however, the owner or operator must do the following:
     
    A) Upon detection of a condition that has caused to a release of
    hazardous wastes (e.g., upon detection of leakage from the primary
    barrier) the owner or operator must do the following:
     
    i) Enter a record of the discovery in the facility operating
    record;
     
    ii) Immediately remove the portion of the containment
    building affected by the condition from service;
     
    iii) Determine what steps must be taken to repair the
    containment building, remove any leakage from the
    secondary collection system, and establish a schedule for
    accomplishing the cleanup and repairs; and
     
    iv) Within seven days after the discovery of the condition,
    notify the Agency in writing of the condition, and within 14
    working days, provide a written notice to the Agency with
    a description of the steps taken to repair the containment
    building, and the schedule for accomplishing the work;
     
    B) The Agency must review the information submitted, make a
    determination regarding whether the containment building must be
    removed from service completely or partially until repairs and
    cleanup are complete, and notify the owner or operator of the
    determination and the underlying rationale in writing; and
     
    C) Upon completing all repairs and cleanup the owner and operator
    must notify the Agency in writing and provide a verification,
    signed by a qualified, registered professional engineer, that the
    repairs and cleanup have been completed according to the written
    plan submitted in accordance with subsection (c)(3)(A)(iv) of this
    Section; and
     
    4) Inspect and record in the facility’s operating record, at least once every
    seven days, data gathered from monitoring equipment and leak detection

     
    700
    equipment as well as the containment building and the area immediately
    surrounding the containment building to detect signs of releases of
    hazardous waste.
     
    d) For containment buildings that contain areas both with and without secondary
    containment, the owner or operator must do the following:
     
    1) Design and operate each area in accordance with the requirements
    enumerated in subsections (a) through (c) of this Section;
     
    2) Take measures to prevent the release of liquids or wet materials into areas
    without secondary containment; and
     
    3) Maintain in the facility’s operating log a written description of the
    operating procedures used to maintain the integrity of areas without
    secondary containment.
     
    e) Notwithstanding any other provision of this Subpart DD, the Agency must not
    require secondary containment for a permitted containment building where the
    owner operator demonstrates that the only free liquids in the unit are limited
    amounts of dust suppression liquids required to meet occupational health and
    safety requirements, and where containment of managed wastes and liquids can
    be assured without a secondary containment system.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.Appendix A Recordkeeping Instructions
     
    See appendix I to 40 CFR 265 (Recordkeeping Instructions), incorporated by reference in 35 Ill.
    Adm. Code 720.111(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.Appendix C USEPA Interim Primary Drinking Water Standards
     
    See appendix III to 40 CFR 265 (EPA Interim Primary Drinking Water Standards), incorporated
    by reference in 35 Ill. Adm. Code 720.111(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 725.Appendix D Tests for Significance
     
    See appendix IV to 40 CFR 265 (Tests for Significance), incorporated by reference in 35 Ill.
    Adm. Code 720.111(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)

     
    701
     
    Section 725.Appendix E Examples of Potentially Incompatible Wastes
     
    See appendix V to 40 CFR 265 (Examples of Potentially Incompatible Waste), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
     
    PART 726
    STANDARDS FOR THE MANAGEMENT OF SPECIFIC HAZARDOUS
    WASTE AND SPECIFIC TYPES OF HAZARDOUS WASTE MANAGEMENT
    FACILITIES
     
    SUBPART C: RECYCLABLE MATERIALS USED IN A MANNER
    CONSTITUTING DISPOSAL
    Section
    726.120 Applicability
    726.121 Standards Applicable to Generators and Transporters of Materials Used in a
    Manner that Constitutes Disposal
    726.122 Standards Applicable to Storers, Who Are Not the Ultimate Users, of Materials
    that Are To Be Used in a manner that Constitutes Disposal
    726.123 Standards Applicable to Users of Materials that Are Used in a Manner that
    Constitutes Disposal
     
    SUBPART D: HAZARDOUS WASTE BURNED FOR ENERGY RECOVERY
    Section
    726.130 Applicability (Repealed)
    726.131 Prohibitions (Repealed)
    726.132 Standards applicable to generators of hazardous waste fuel (Repealed)
    726.133 Standards applicable to transporters of hazardous waste fuel (Repealed)
    726.134 Standards applicable to marketers of hazardous waste fuel (Repealed)
    726.135 Standards applicable to burners of hazardous waste fuel (Repealed)
    726.136 Conditional exemption for spent materials and by-products exhibiting a
    characteristic of hazardous waste (Repealed)
     
    SUBPART E: USED OIL BURNED FOR ENERGY RECOVERY
    Section
    726.140 Applicability (Repealed)
    726.141 Prohibitions (Repealed)
    726.142 Standards applicable to generators of used oil burned for energy recovery
    (Repealed)

     
    702
    726.143 Standards applicable to marketers of used oil burned for energy recovery
    (Repealed)
    726.144 Standards applicable to burners of used oil burned for energy recovery
    (Repealed)
     
    SUBPART F: RECYCLABLE MATERIALS UTILIZED FOR PRECIOUS
    METAL RECOVERY
    Section
    726.170 Applicability and Requirements
     
    SUBPART G: SPENT LEAD-ACID BATTERIES BEING RECLAIMED
    Section
    726.180 Applicability and Requirements
     
    SUBPART H: HAZARDOUS WASTE BURNED IN BOILERS AND
    INDUSTRIAL FURNACES
    Section
    726.200 Applicability
    726.201 Management Prior to Burning
    726.202 Permit Standards for Burners
    726.203 Interim Status Standards for Burners
    726.204 Standards to Control Organic Emissions
    726.205 Standards to Control PM
    726.206 Standards to Control Metals Emissions
    726.207 Standards to Control HCl and Chlorine Gas Emissions
    726.208 Small Quantity On-Site Burner Exemption
    726.209 Low Risk Waste Exemption
    726.210 Waiver of DRE Trial Burn for Boilers
    726.211 Standards for Direct Transfer
    726.212 Regulation of Residues
    726.219 Extensions of Time
     
    SUBPART M: MILITARY MUNITIONS
    Section
    726.300 Applicability
    726.301 Definitions
    726.302 Definition of Solid Waste
    726.303 Standards Applicable to the Transportation of Solid Waste Military Munitions
    726.304 Standards Applicable to Emergency Responses
    726.305 Standards Applicable to the Storage of Solid Waste Military Munitions
    726.306 Standards Applicable to the Treatment and Disposal of Waste Military Munitions
     
    SUBPART N: CONDITIONAL EXEMPTION FOR LOW-LEVEL MIXED
    WASTE STORAGE, TREATMENT, TRANSPORTATION AND DISPOSAL
    Section
    726.310 Definitions

     
    703
    726.320 Storage and Treatment Conditional Exemption
    726.325 Wastes Eligible for a Storage and Treatment Conditional Exemption for Low-
    Level Mixed Waste
    726.330 Conditions to Qualify for and Maintain a Storage and Treatment Conditional
    Exemption
    726.335 Treatment Allowed by a Storage and Treatment Conditional Exemption
    726.340 Loss of a Storage and Treatment Conditional Exemption and Required Action
    726.345 Reclaiming a Lost Storage and Treatment Conditional Exemption
    726.350 Recordkeeping for a Storage and Treatment Conditional Exemption
    726.355 Waste No Longer Eligible for a Storage and Treatment Conditional Exemption
    726.360 Applicability of Closure Requirements to Storage Units
    726.405 Transportation and Disposal Conditional Exemption
    726.410 Wastes Eligible for a Transportation and Disposal Conditional Exemption
    726.415 Conditions to Qualify for and Maintain a Transportation and Disposal Conditional
    Exemption
    726.420 Treatment Standards for Eligible Waste
    726.425 Applicability of the Manifest and Transportation Condition
    726.430 Effectiveness of a Transportation and Disposal Exemption
    726.435 Disposal of Exempted Waste
    726.440 Containers Used for Disposal of Exempted Waste
    726.445 Notification
    726.450 Recordkeeping for a Transportation and Disposal Conditional Exemption
    726.455 Loss of a Transportation and Disposal Conditional Exemption and Required
    Action
    726.460 Reclaiming a Lost Transportation and Disposal Conditional Exemption
     
    726.Appendix A Tier I and Tier II Feed Rate and Emissions Screening Limits for Metals
    726.Appendix B Tier I Feed Rate Screening Limits for Total Chlorine
    726.Appendix C Tier II Emission Rate Screening Limits for Free Chlorine and Hydrogen
    Chloride
    726.Appendix D Reference Air Concentrations
    726.Appendix E Risk-Specific Doses
    726.Appendix F Stack Plume Rise
    726.Appendix G Health-Based Limits for Exclusion of Waste-Derived Residues
    726.Appendix H Potential PICs for Determination of Exclusion of Waste-Derived Residues
    726.Appendix I Methods Manual for Compliance with BIF Regulations
    726.Appendix J Guideline on Air Quality Models (Repealed)
    726.Appendix K Lead-Bearing Materials that May be Processed in Exempt Lead Smelters
    726.Appendix L Nickel or Chromium-Bearing Materials that May Be Processed in Exempt
    Nickel-Chromium Recovery Furnaces
    726.Appendix M Mercury-Bearing Wastes that May Be Processed in Exempt Mercury
    Recovery Units
    726.Table A Exempt Quantities for Small Quantity Burner Exemption
     
    AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the
    Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].

     
    704
     
    SOURCE: Adopted in R85-22 at 10 Ill. Reg. 1162, effective January 2, 1986; amended in R86-1
    at 10 Ill. Reg. 14156, effective August 12, 1986; amended in R87-26 at 12 Ill. Reg. 2900,
    effective January 15, 1988; amended in R89-1 at 13 Ill. Reg. 18606, effective November 13,
    1989; amended in R90-2 at 14 Ill. Reg. 14533, effective August 22, 1990; amended in R90-11 at
    15 Ill. Reg. 9727, effective June 17, 1991; amended in R91-13 at 16 Ill. Reg. 9858, effective
    June 9, 1992; amended in R92-10 at 17 Ill. Reg. 5865, effective March 26, 1993; amended in
    R93-4 at 17 Ill. Reg. 20904, effective November 22, 1993; amended in R94-7 at 18 Ill. Reg.
    12500, effective July 29, 1994; amended in R95-6 at 19 Ill. Reg. 10006, effective June 27, 1995;
    amended in R95-20 at 20 Ill. Reg. 11263, effective August 1, 1996; amended in R96-10/R97-
    3/R97-5 at 22 Ill. Reg. 754, effective December 16, 1997; amended in R97-21/R98-3/R98-5 at
    22 Ill. Reg. 18042, effective September 28, 1998; amended in R99-15 at 23 Ill. Reg. 9482,
    effective July 26, 1999; amended in R00-13 at 24 Ill. Reg. 9853, effective June 20, 2000;
    amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. 6667, effective April 22, 2002; amended in
    R03-7 at 27 Ill. Reg. 4200, effective February 14, 2003; amended in R03-18 at 27 Ill. Reg.
    12916, effective July 17, 2003; amended in R06-5/R06-6/R06-7 at 30 Ill. Reg. ________,
    effective ______________________.
     
    SUBPART C: RECYCLABLE MATERIALS USED IN A MANNER
    CONSTITUTING DISPOSAL
     
    Section 726.120 Applicability
     
    a) The regulations of this Subpart C apply to recyclable materials that are applied to or
    placed on the land in either of the following ways:
     
    1) Without mixing with any other substances; or
     
    2) After mixing or combination with any other substances. These materials will
    be referred to throughout this Subpart C as “materials used in a manner that
    constitutes disposal.”
     
    b) A product produced for the general public’s use that is used in a manner that
    constitutes disposal and which contains recyclable material is not presently subject to
    regulation under this Subpart C if the recyclable materials have undergone a
    chemical reaction in the course of producing the products so as to become
    inseparable by physical means and if such products meet the applicable treatment
    standards in Subpart D of 35 Ill. Adm. Code 728 (or applicable prohibition levels in
    35 Ill. Adm. Code 728.132 or 728.139, where no treatment standards have been
    established) for each recycable recyclable material (i.e., hazardous waste) that it
    contains.
     
    c) Anti-skid and deicing uses of slags that are generated from high temperature metals
    recovery (HTMR) processing of hazardous wastes K061, K062, and F006 in a
    manner constituting disposal are not covered by the exemption in subsection (b) of
    this Section, and such uses of these materials remain subject to regulation.

     
    705
     
    d) Fertilizers that contain recyclable materials are not subject to regulation provided
    that the following conditions are fulfilled:
     
    1) They are zinc fertilizers excluded from the definition of solid waste
    according to 35 Ill. Adm. Code 721.104(a)(21); or
     
    2) They meet the applicable treatment standards in Subpart D of 35 Ill. Adm.
    Code 728 for each hazardous waste that they contain.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART H: HAZARDOUS WASTE BURNED IN BOILERS AND
    INDUSTRIAL FURNACES
     
    Section 726.200 Applicability
     
    a) The regulations of this Subpart H apply to hazardous waste burned or processed in a
    boiler or industrial furnace (BIF) (as defined in 35 Ill. Adm. Code 720.110)
    irrespective of the purpose of burning or processing, except as provided by
    subsections (b), (c), (d), (g), and (h) of this Section. In this Subpart H, the term
    “burn” means burning for energy recovery or destruction or processing for materials
    recovery or as an ingredient. The emissions standards of Sections 726.204, 726.205,
    726.206, and 726.207 apply to facilities operating under interim status or under a
    RCRA permit, as specified in Sections 726.202 and 726.203.
     
    b) Integration of the MACT standards.
     
    1) Except as provided by subsection (b)(2) of this Section, the standards of
    this Part no longer apply when an affected source demonstrates
    compliance with the maximum achievable control technology (MACT)
    requirements of federal subpart EEE of 40 CFR 63, subpart EEE (National
    Emission Standards for Hazardous Air Pollutants from Hazardous Waste
    Combustors), incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(b), by conducting a comprehensive performance test and
    submitting to the Agency a Notification of Compliance, under 40 CFR
    63.1207(j) (What are the performance testing requirements?) and
    63.1210(b) (What are the notification requirements?), documenting
    compliance with the requirements of federal subpart EEE of 40 CFR 63,
    subpart EEE. Nevertheless, even after this demonstration of compliance
    with the MACT standards, RCRA permit conditions that were based on
    the standards of this Part will continue to be in effect until they are
    removed from the permit or the permit is terminated or revoked, unless the
    permit expressly provides otherwise.
     
    2) The following standards continue to apply:

     
    706
     
    A) If an owner or operator elects to comply with 35 Ill. Adm. Code
    703.320(a)(1)(A) to minimize emissions of toxic compounds from
    startup, shutdown, and malfunction events, Section 726.202(e)(1),
    requiring operations in accordance with the operating requirements
    specified in the permit at all times that hazardous waste is in the
    unit, and Section 726.202(e)(2)(C), requiring compliance with the
    emission standards and operating requirements, during startup and
    shutdown if hazardous waste is in the combustion chamber, except
    for particular hazardous wastes. These provisions apply only
    during startup, shutdown, and malfunction events;
     
    B) The closure requirements of Sections 726.202(e)(11) and
    726.203(l);
     
    C) The standards for direct transfer of Section 726.211;
     
    D) The standards for regulation of residues of Section 726.312; and
     
    E) The applicable requirements of Subparts A through H, BB, and CC
    of 35 Ill. Adm. Code 724 and 725.
     
    BOARD NOTE: Sections 9.1 and 39.5 of the Environmental Protection Act [415
    ILCS 5/9.1 and 39.5] make the federal MACT standards directly applicable to
    entities in Illinois and authorize the Agency to issue permits based on the federal
    standards. In adopting this subsection (b), USEPA stated as follows (at 64 Fed
    Reg. 52828, 52975 (September 30,1999)):
     
    Under [the approach adopted by USEPA as a] final rule, MACT
    air emissions and related operating requirements are to be included
    in title V permits; RCRA permits will continue to be required for
    all other aspects of the combustion unit and the facility that are
    governed by RCRA (e.g., corrective action, general facility
    standards, other combustor-specific concerns such as materials
    handling, risk-based emissions limits and operating requirements,
    as appropriate, and other hazardous waste management units).
     
    c) The following hazardous wastes and facilities are not subject to regulation under this
    Subpart H:
     
    1) Used oil burned for energy recovery that is also a hazardous waste solely
    because it exhibits a characteristic of hazardous waste identified in Subpart C
    of 35 Ill. Adm. Code 721. Such used oil is subject to regulation under 35 Ill.
    Adm. Code 739, rather than this Subpart;
     
    2) Gas recovered from hazardous or solid waste landfills, when such gas is

     
    707
    burned for energy recovery;
     
    3) Hazardous wastes that are exempt from regulation under 35 Ill. Adm. Code
    721.104 and 721.106(a)(3)(C) and (a)(3)(D) and hazardous wastes that are
    subject to the special requirements for conditionally exempt small quantity
    generators under 35 Ill. Adm. Code 721.105; and
     
    4) Coke ovens, if the only hazardous waste burned is USEPA hazardous waste
    no. K087 decanter tank tar sludge from coking operations.
     
    d) Owners and operators of smelting, melting, and refining furnaces (including
    pyrometallurgical devices, such as cupolas, sintering machines, roasters, and foundry
    furnaces, but not including cement kilns, aggregate kilns, or halogen acid furnaces
    burning hazardous waste) that process hazardous waste solely for metal recovery are
    conditionally exempt from regulation under this Subpart H, except for Sections
    726.201 and 726.212.
     
    1) To be exempt from Sections 726.202 through 726.211, an owner or operator
    of a metal recovery furnace or mercury recovery furnace must comply with
    the following requirements, except that an owner or operator of a lead or a
    nickel-chromium recovery furnace or a metal recovery furnace that burns
    baghouse bags used to capture metallic dust emitted by steel manufacturing
    must comply with the requirements of subsection (d)(3) of this Section, and
    an owner or operator of a lead recovery furnace that is subject to
    regulation under the Secondary Lead Smelting NESHAP of federal
    subpart X of 40 CFR 63, subpart X (National Emission Standards for
    Hazardous Air Pollutants from Secondary Lead Smelting) must comply
    with the requirements of subsection (h) of this Section:
     
    A) Provide a one-time written notice to the Agency indicating the
    following:
     
    i) The owner or operator claims exemption under this
    subsection;
     
    ii) The hazardous waste is burned solely for metal recovery
    consistent with the provisions of subsection (d)(2) of this
    Section;
     
    iii) The hazardous waste contains recoverable levels of metals;
    and
     
    iv) The owner or operator will comply with the sampling and
    analysis and recordkeeping requirements of this subsection
    (d);
     

     
    708
    B) Sample and analyze the hazardous waste and other feedstocks as
    necessary to comply with the requirements of this subsection (d)
    under procedures specified by “Test Methods for Evaluating Solid
    Waste, Physical/Chemical Methods,” SW-846, incorporated by
    reference in 35 Ill. Adm. Code 720.111, or alternative methods that
    meet or exceed the SW-846 method performance capabilities. If SW-
    846 does not prescribe a method for a particular determination, the
    owner or operator must use the best available method using
    appropriate methods; and
     
    C) Maintain at the facility for at least three years records to document
    compliance with the provisions of this subsection (d), including limits
    on levels of toxic organic constituents and Btu value of the waste and
    levels of recoverable metals in the hazardous waste compared to
    normal non-hazardous waste feedstocks.
     
    2) A hazardous waste meeting either of the following criteria is not processed
    solely for metal recovery:
     
    A) The hazardous waste has a total concentration of organic compounds
    listed in Appendix H to 35 Ill. Adm. Code 721 exceeding 500 ppm by
    weight, as fired, and so is considered to be burned for destruction.
    The concentration of organic compounds in a waste as-generated may
    be reduced to the 500 ppm limit by bona fide treatment that removes
    or destroys organic constituents. Blending for dilution to meet the
    500 ppm limit is prohibited, and documentation that the waste has not
    been impermissibly diluted must be retained in the records required
    by subsection (d)(1)(C) of this Section; or
     
    B) The hazardous waste has a heating value of 5,000 Btu/lb or more, as-
    fired, and is so considered to be burned as fuel. The heating value of
    a waste as-generated may be reduced to below the 5,000 Btu/lb limit
    by bona fide treatment that removes or destroys organic constituents.
    Blending for dilution to meet the 5,000 Btu/lb limit is prohibited and
    documentation that the waste has not been impermissibly diluted
    must be retained in the records required by subsection (d)(1)(C) of
    this Section.
     
    3) To be exempt from Sections 726.202 through 726.211, an owner or operator
    of a lead, nickel-chromium, or mercury recovery furnace, except for an
    owner or operator of a lead recovery furnace that is subject to regulation
    under the Secondary Lead Smelting NESHAP of subpart X of 40 CFR 63,
    subpart X, or a metal recovery furnace that burns baghouse bags used to
    capture metallic dusts emitted by steel manufacturing must provide a one-
    time written notice to the Agency identifying each hazardous waste burned
    and specifying whether the owner or operator claims an exemption for each

     
    709
    waste under this subsection (d)(3) or subsection (d)(1) of this Section. The
    owner or operator must comply with the requirements of subsection (d)(1) of
    this Section for those wastes claimed to be exempt under that subsection and
    must comply with the following requirements for those wastes claimed to be
    exempt under this subsection (d)(3):
     
    A) The hazardous wastes listed in Appendices K, L, and M of this Part
    and baghouse bags used to capture metallic dusts emitted by steel
    manufacturing are exempt from the requirements of subsection (d)(1)
    of this Section, provided the following are true:
     
    i) A waste listed in Appendix K of this Part must contain
    recoverable levels of lead, a waste listed in Appendix L of
    this Part must contain recoverable levels of nickel or
    chromium, a waste listed in Appendix M of this Part must
    contain recoverable levels of mercury and contain less than
    500 ppm of Appendix H to 35 Ill. Adm. Code 721 organic
    constituents, and baghouse bags used to capture metallic
    dusts emitted by steel manufacturing must contain
    recoverable levels of metal;
     
    ii) The waste does not exhibit the toxicity characteristic of 35 Ill.
    Adm. Code 721.124 for an organic constituent;
     
    iii) The waste is not a hazardous waste listed in Subpart D of 35
    Ill. Adm. Code 721 because it is listed for an organic
    constituent, as identified in Appendix G of 35 Ill. Adm. Code
    721; and
     
    iv) The owner or operator certifies in the one-time notice that
    hazardous waste is burned under the provisions of subsection
    (d)(3) of this Section and that sampling and analysis will be
    conducted or other information will be obtained as necessary
    to ensure continued compliance with these requirements.
    Sampling and analysis must be conducted according to
    subsection (d)(1)(B) of this Section, and records to document
    compliance with subsection (d)(3) of this Section must be
    kept for at least three years.
     
    B) The Agency may decide, on a case-by-case basis, that the toxic
    organic constituents in a material listed in Appendix K, Appendix L,
    or Appendix M of this Part that contains a total concentration of more
    than 500 ppm toxic organic compounds listed in Appendix H to 35
    Ill. Adm. Code 721 may pose a hazard to human health and the
    environment when burned in a metal recovery furnace exempt from
    the requirements of this Subpart H. Under these circumstances, after

     
    710
    adequate notice and opportunity for comment, the metal recovery
    furnace will become subject to the requirements of this Subpart H
    when burning that material. In making the hazard determination, the
    Agency must consider the following factors:
     
    i) The concentration and toxicity of organic constituents in the
    material;
     
    ii) The level of destruction of toxic organic constituents
    provided by the furnace; and
     
    iii) Whether the acceptable ambient levels established in
    Appendix D or E of this Part will be exceeded for any toxic
    organic compound that may be emitted based on dispersion
    modeling to predict the maximum annual average off-site
    ground level concentration.
     
    e) The standards for direct transfer operations under Section 726.211 apply only to
    facilities subject to the permit standards of Section 726.202 or the interim status
    standards of Section 726.203.
     
    f) The management standards for residues under Section 726.212 apply to any BIF
    burning hazardous waste.
     
    g) Owners and operators of smelting, melting, and refining furnaces (including
    pyrometallurgical devices such as cupolas, sintering machines, roasters, and foundry
    furnaces) that process hazardous waste for recovery of economically significant
    amounts of the precious metals gold, silver, platinum, palladium, iridium, osmium,
    rhodium, ruthenium, or any combination of these metals are conditionally exempt
    from regulation under this Subpart H, except for Section 726.212. To be exempt
    from Sections 726.202 through 726.211, an owner or operator must do the following:
     
    1) Provide a one-time written notice to the Agency indicating the following:
     
    A) The owner or operator claims exemption under this Section,
     
    B) The hazardous waste is burned for legitimate recovery of precious
    metal, and
     
    C) The owner or operator will comply with the sampling and analysis
    and recordkeeping requirements of this Section;
     
    2) Sample and analyze the hazardous waste, as necessary, to document that the
    waste is burned for recovery of economically significant amounts of the
    metals and that the treatment recovers economically significant amounts of
    precious metal, using procedures specified by Test Methods for Evaluating

     
    711
    Solid Waste, Physical/Chemical Methods, SW-846, incorporated by
    reference in 35 Ill. Adm. Code 720.111, or alternative methods that meet or
    exceed the SW-846 method performance capabilities. If SW-846 does not
    prescribe a method for a particular determination, the owner or operator must
    use the best available method; and
     
    3) Maintain, at the facility for at least three years, records to document that all
    hazardous wastes burned are burned for recovery of economically significant
    amounts of precious metal.
     
    h) An owner or operator of a lead recovery furnace that processes hazardous waste
    for recovery of lead and which is subject to regulation under the Secondary Lead
    Smelting NESHAP of subpart X of 40 CFR 63, subpart X, is conditionally
    exempt from regulation under this Subpart, except for Section 726.201. To
    become exempt, an owner or operator must provide a one-time notice to the
    Agency identifying each hazardous waste burned and specifying that the owner or
    operator claims an exemption under this subsection (h). The notice also must
    state that the waste burned has a total concentration of non-metal compounds
    listed in Appendix H to 35 Ill. Adm. Code 721 of less than 500 ppm by weight, as
    fired and as provided in subsection (d)(2)(A) of this Section, or is listed in
    Appendix K to this Part.
     
    i) Abbreviations and definitions. The following definitions and abbreviations are used
    in this Subpart H:
     
    “APCS” means air pollution control system.
     
    “BIF” means boiler or industrial furnace.
     
    “Carcinogenic metals” means arsenic, beryllium, cadmium, and chromium.
     
    “CO” means carbon monoxide.
     
    “Continuous monitor” is a monitor that continuously samples the regulated
    parameter without interruption, that evaluates the detector response at least
    once each 15 seconds, and that computes and records the average value at
    least every 60 seconds.
     
    “DRE” means destruction or removal efficiency.
     
    “cu m” or “m
    3
    ” means cubic meters.
     
    “E” means “ten to the power.” For example, “XE-Y” means “X times ten to
    the -Y power.”
     
    “Feed rates” are measured as specified in Section 726.202(e)(6).

     
    712
     
    “Good engineering practice stack height” is as defined by federal 40 CFR
    51.100(ii) (Definitions), incorporated by reference in 35 Ill. Adm. Code
    720.111 720.111(b).
     
    “HC” means hydrocarbon.
     
    “HCl” means hydrogen chloride gas.
     
    “Hourly rolling average” means the arithmetic mean of the 60 most recent
    one-minute average values recorded by the continuous monitoring system.
     
    “K” means Kelvin.
     
    “kVA” means kilovolt amperes.
     
    “MEI” means maximum exposed individual.
     
    “MEI location” means the point with the maximum annual average off-site
    (unless on-site is required) ground level concentration.
     
    “Noncarcinogenic metals” means antimony, barium, lead, mercury, thallium,
    and silver.
     
    “One hour block average” means the arithmetic mean of the one minute
    averages recorded during the 60-minute period beginning at one minute after
    the beginning of the preceding clock hour.
     
    “PIC” means product of incomplete combustion.
     
    “PM” means particulate matter.
     
    “POHC” means principal organic hazardous constituent.
     
    “ppmv” means parts per million by volume.
     
    “QA/QC” means quality assurance and quality control.
     
    “Rolling average for the selected averaging period” means the arithmetic
    mean of one hour block averages for the averaging period.
     
    “RAC” means reference air concentration, the acceptable ambient level for
    the noncarcinogenic metals for purposes of this Subpart. RACs are specified
    in Appendix D of this Part.
     
    “RSD” means risk-specific dose, the acceptable ambient level for the

     
    713
    carcinogenic metals for purposes of this Subpart. RSDs are specified in
    Appendix E of this Part.
     
    “SSU” means “Saybolt Seconds Universal,” a unit of viscosity measured by
    ASTM D 88-87 (Standard Test Method for Saybolt Viscosity) or D 2161-
    87 (Standard Practice for Conversion of Kinematic Viscosity to Saybolt
    Universal or to Saybolt Furol Viscosity), each incorporated by reference in
    35 Ill. Adm. Code 720.111 720.111(a).
     
    “TCLP test” means the toxicity characteristic leaching procedure Method
    1311 (Toxicity Characteristic Leaching Procedure) in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    publication number EPA-530/SW-846, incorporated by reference in 35 Ill.
    Adm. Code 720.111(a), as used for the purposes of 35 Ill. Adm. Code
    721.124.
     
    “TESH” means terrain-adjusted effective stack height (in meters).
     
    “Tier I.” See Section 726.206(b).
     
    “Tier II.” See Section 726.206(c).
     
    “Tier III.” See Section 726.206(d).
     
    “Toxicity equivalence” is estimated, pursuant to Section 726.204(e), using
    “section 4.0 (Procedures for Estimating the Toxicity Equivalence of
    Chlorinated Dibenzo-p-Dioxin and Dibenzofuran Congeners) in federal
    appendix IX to 40 CFR 266 (Methods Manual for Compliance with the
    BIF Regulations),” incorporated by reference in 35 Ill. Adm. Code
    720.111(b) (see Appendix I of this Part).
     
    “mg” means microgram.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.202 Permit Standards for Burners
     
    a) Applicability.
     
    1) General. An owner or operator of a BIF that burns hazardous waste and
    which does not operate under interim status must comply with the
    requirements of this Section and 35 Ill. Adm. Code 703.208 and 703.232,
    unless exempt under the small quantity burner exemption of Section 726.208.
     
    2) Applicability of 35 Ill. Adm. Code 724 standards. An owner or operator of a
    BIF that burns hazardous waste is subject to the following provisions of 35

     
    714
    Ill. Adm. Code 724, except as provided otherwise by this Subpart H:
     
    A) In Subpart A (General), 35 Ill. Adm. Code 724.104;
     
    B) In Subpart B (General facility standards), 35 Ill. Adm. Code 724.111
    through 724.118;
     
    C) In Subpart C (Preparedness and prevention), 35 Ill. Adm. Code
    724.131 through 724.137;
     
    D) In Subpart D (Contingency plan and emergency procedures), 35 Ill.
    Adm. Code 724.151 through 724.156;
     
    E) In Subpart E (Manifest system, recordkeeping and reporting), the
    applicable provisions of 35 Ill. Adm. Code 724.171 through 724.177;
     
    F) In Subpart F (Corrective Action), 35 Ill. Adm. Code 724.190 and
    724.201;
     
    G) In Subpart G (Closure and post-closure), 35 Ill. Adm. Code 724.211
    through 724.215;
     
    H) In Subpart H (Financial requirements), 35 Ill. Adm. Code 724.241,
    724.242, 724.243, and 724.247 through 724.251, except that the State
    of Illinois and the federal government are exempt from the
    requirements of Subpart H of 35 Ill. Adm. Code 724; and
     
    I) Subpart BB (Air emission standards for equipment leaks), except 35
    Ill. Adm. Code 724.950(a).
     
    b) Hazardous waste analysis.
     
    1) The owner or operator must provide an analysis of the hazardous waste that
    quantifies the concentration of any constituent identified in Appendix H of 35
    Ill. Adm. Code 721 that is reasonably expected to be in the waste. Such
    constituents must be identified and quantified if present, at levels detectable
    by using appropriate analytical procedures prescribed by Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods (incorporated by
    reference, see 35 Ill. Adm. Code 720.111). Alternative methods that meet
    or exceed the method performance capabilities of SW-846 methods may be
    used. If SW-846 does not prescribe a method for a particular determination,
    the owner or operator must use the best available method. The constituents
    listed in Appendix H of 35 Ill. Adm. Code 721 constituents that are
    excluded from this analysis must be identified and the basis for their
    exclusion explained. This analysis must provide all information required by
    this Subpart H and 35 Ill. Adm. Code 703.208 and 703.232 and must enable

     
    715
    the Agency to prescribe such permit conditions as are necessary to protect
    human health and the environment. Such analysis must be included as a
    portion of the Part B permit application, or, for facilities operating under the
    interim status standards of this Subpart H, as a portion of the trial burn plan
    that may be submitted before the Part B application under provisions of 35
    Ill. Adm. Code 703.232(g), as well as any other analysis required by the
    Agency. Owners and operators The owner or operator of BIFs a BIF not
    operating under the interim status standards must provide the information
    required by 35 Ill. Adm. Code 703.208 and 703.232 in the Part B application
    to the greatest extent possible.
     
    2) Throughout normal operation, the owner or operator must conduct sampling
    and analysis as necessary to ensure that the hazardous waste, other fuels, and
    industrial furnace feedstocks fired into the BIF are within the physical and
    chemical composition limits specified in the permit.
     
    c) Emissions standards. Owners and operators An owner or operator must comply
    with emissions standards provided by Sections 726.204 through 726.207.
     
    d) Permits.
     
    1) The owner or operator must burn only hazardous wastes specified in the
    facility permit and only under the operating conditions specified under
    subsection (e) of this Section, except in approved trial burns under the
    conditions specified in 35 Ill. Adm. Code 703.232.
     
    2) Hazardous wastes not specified in the permit must not be burned until
    operating conditions have been specified under a new permit or permit
    modification, as applicable. Operating requirements for new wastes must be
    based on either trial burn results or alternative data included with Part B of a
    permit application under 35 Ill. Adm. Code 703.208.
     
    3) BIFs operating under the interim status standards of Section 726.203 are
    permitted under procedures provided by 35 Ill. Adm. Code 703.232(g).
     
    4) A permit for a new BIF (those BIFs not operating under the interim status
    standards) must establish appropriate conditions for each of the applicable
    requirements of this Section, including but not limited to allowable
    hazardous waste firing rates and operating conditions necessary to meet the
    requirements of subsection (e) of this Section, in order to comply with the
    following standards:
     
    A) For the period beginning with initial introduction of hazardous waste
    and ending with initiation of the trial burn, and only for the minimum
    time required to bring the device to a point of operational readiness to
    conduct a trial burn, not to exceed a duration of 720 hours operating

     
    716
    time when burning hazardous waste, the operating requirements must
    be those most likely to ensure compliance with the emission
    standards of Sections 726.204 through 726.207, based on the
    Agency’s engineering judgment. If the applicant is seeking a waiver
    from a trial burn to demonstrate conformance with a particular
    emission standard, the operating requirements during this initial
    period of operation must include those specified by the applicable
    provisions of Section 726.204, Section 726.205, Section 726.206, or
    Section 726.207. The Agency must extend the duration of this period
    for up to 720 additional hours when good cause for the extension is
    demonstrated by the applicant.
     
    B) For the duration of the trial burn, the operating requirements must be
    sufficient to demonstrate compliance with the emissions standards of
    Sections 726.204 through 726.207 and must be in accordance with
    the approved trial burn plan;
     
    C) For the period immediately following completion of the trial burn,
    and only for the minimum period sufficient to allow sample analysis,
    data computation, submission of the trial burn results by the
    applicant, review of the trial burn results, and modification of the
    facility permit by the Agency to reflect the trial burn results, the
    operating requirements must be those most likely to ensure
    compliance with the emission standards Sections 726.204 through
    726.207 based on the Agency’s engineering judgment.
     
    D) For the remaining duration of the permit, the operating requirements
    must be those demonstrated in a trial burn or by alternative data
    specified in 35 Ill. Adm. Code 703.208, as sufficient to ensure
    compliance with the emissions standards of Sections 726.204 through
    726.207.
     
    e) Operating requirements.
     
    1) General. A BIF burning hazardous waste must be operated in accordance
    with the operating requirements specified in the permit at all times when
    there is hazardous waste in the unit.
     
    2) Requirements to ensure compliance with the organic emissions standards.
     
    A) DRE (destruction or removal efficiency) standard. Operating
    conditions must be specified in either of the following ways: on a
    case-by-case basis for each hazardous waste burned, which
    conditions must be demonstrated (in a trial burn or by alternative
    data, as specified in 35 Ill. Adm. Code 703.208) to be sufficient to
    comply with the DRE performance standard of Section 726.204(a), or

     
    717
    as special operating requirements provided by Section 726.204(a)(4)
    for the waiver of the DRE trial burn. When the DRE trial burn is not
    waived under Section 726.204(a)(4), each set of operating
    requirements must specify the composition of the hazardous waste
    (including acceptable variations in the physical and chemical
    properties of the hazardous waste that will not affect compliance with
    the DRE performance standard) to which the operating requirements
    apply. For each such hazardous waste, the permit must specify
    acceptable operating limits including, but not limited to, the
    following conditions, as appropriate:
     
    i) Feed rate of hazardous waste and other fuels measured and
    specified as prescribed in subsection (e)(6) of this Section;
     
    ii) Minimum and maximum device production rate when
    producing normal product expressed in appropriate units,
    measured and specified as prescribed in subsection (e)(6) of
    this Section;
     
    iii) Appropriate controls of the hazardous waste firing system;
     
    iv) Allowable variation in BIF system design or operating
    procedures;
     
    v) Minimum combustion gas temperature measured at a location
    indicative of combustion chamber temperature, measured,
    and specified as prescribed in subsection (e)(6) of this
    Section;
     
    vi) An appropriate indicator of combustion gas velocity,
    measured and specified as prescribed in subsection (e)(6) of
    this Section, unless documentation is provided under 35 Ill.
    Adm. Code 703.232 demonstrating adequate combustion gas
    residence time; and
     
    vii) Such other operating requirements as are necessary to ensure
    that the DRE performance standard of Section 726.204(a) is
    met.
     
    B) CO and hydrocarbon (HC) standards. The permit must incorporate a
    CO limit and, as appropriate, a HC limit as provided by Section
    726.204(b), (c), (d), (e), and (f). The permit limits must be specified
    as follows:
     
    i) When complying with the CO standard of Section
    726.204(b)(1), the permit limit is 100 ppmv;

     
    718
     
    ii) When complying with the alternative CO standard under
    Section 726.204(c), the permit limit for CO is based on the
    trial burn and is established as the average over all valid runs
    of the highest hourly rolling average CO level of each run;
    and, the permit limit for HC is 20 ppmv (as defined in Section
    726.204(c)(1)), except as provided in Section 726.204(f); or
     
    iii) When complying with the alternative HC limit for industrial
    furnaces under Section 726.204(f), the permit limit for HC
    and CO is the baseline level when hazardous waste is not
    burned as specified by that subsection.
     
    C) Start-up and shut-down. During start-up and shut-down of the BIF,
    hazardous waste (except waste fed solely as an ingredient under the
    Tier I (or adjusted Tier I) feed rate screening limits for metals and
    chloride/chlorine, and except low risk waste exempt from the trial
    burn requirements under Sections 726.204(a)(5), 726.205, 726.206,
    and 726.207) must not be fed into the device, unless the device is
    operating within the conditions of operation specified in the permit.
     
    3) Requirements to ensure conformance with the particulate matter (PM)
    standard.
     
    A) Except as provided in subsections (e)(3)(B) and (e)(3)(C) of this
    Section, the permit must specify the following operating
    requirements to ensure conformance with the PM standard specified
    in Section 726.205:
     
    i) Total ash feed rate to the device from hazardous waste, other
    fuels, and industrial furnace feedstocks, measured and
    specified as prescribed in subsection (e)(6) of this Section;
     
    ii) Maximum device production rate when producing normal
    product expressed in appropriate units, and measured and
    specified as prescribed in subsection (e)(6) of this Section;
     
    iii) Appropriate controls on operation and maintenance of the
    hazardous waste firing system and any air pollution control
    system (APCS);
     
    iv) Allowable variation in BIF system design including any
    APCS or operating procedures; and
     
    v) Such other operating requirements as are necessary to ensure
    that the PM standard in Section 726.211(b) is met.

     
    719
     
    B) Permit conditions to ensure conformance with the PM standard must
    not be provided for facilities exempt from the PM standard under
    Section 726.205(b);
     
    C) For cement kilns and light-weight aggregate kilns, permit conditions
    to ensure compliance with the PM standard must not limit the ash
    content of hazardous waste or other feed materials.
     
    4) Requirements to ensure conformance with the metals emissions standard.
     
    A) For conformance with the Tier I (or adjusted Tier I) metals feed rate
    screening limits of Section 726.206(b) or (e), the permit must specify
    the following operating requirements:
     
    i) Total feed rate of each metal in hazardous waste, other fuels
    and industrial furnace feedstocks measured and specified
    under provisions of subsection (e)(6) of this Section;
     
    ii) Total feed rate of hazardous waste measured and specified as
    prescribed in subsection (e)(6) of this Section; and
     
    iii) A sampling and metals analysis program for the hazardous
    waste, other fuels and industrial furnace feedstocks;
     
    B) For conformance with the Tier II metals emission rate screening
    limits under Section 726.206(c) and the Tier III metals controls under
    Section 726.206(d), the permit must specify the following operating
    requirements:
     
    i) Maximum emission rate for each metal specified as the
    average emission rate during the trial burn;
     
    ii) Feed rate of total hazardous waste and pumpable hazardous
    waste, each measured and specified as prescribed in
    subsection (e)(6)(A) of this Section;
     
    iii) Feed rate of each metal in the following feedstreams,
    measured and specified as prescribed in subsections (e)(6) of
    this Section: total feed streams; total hazardous waste feed;
    and total pumpable hazardous waste feed;
     
    iv) Total feed rate of chlorine and chloride in total feed streams
    measured and specified as prescribed in subsection (e)(6) of
    this Section;
     

     
    720
    v) Maximum combustion gas temperature measured at a
    location indicative of combustion chamber temperature, and
    measured and specified as prescribed in subsection (e)(6) of
    this Section;
     
    vi) Maximum flue gas temperature at the inlet to the PM APCS
    measured and specified as prescribed in subsection (e)(6) of
    this Section;
     
    vii) Maximum device production rate when producing normal
    product expressed in appropriate units and measured and
    specified as prescribed in subsection (e)(6) of this Section;
     
    viii) Appropriate controls on operation and maintenance of the
    hazardous waste firing system and any APCS;
     
    ix) Allowable variation in BIF system design including any
    APCS or operating procedures; and
     
    x) Such other operating requirements as are necessary to ensure
    that the metals standards under Sections 726.206(c) or (d) are
    met.
     
    C) For conformance with an alternative implementation approach
    approved by the Agency under Section 726.206(f), the permit must
    specify the following operating requirements:
     
    i) Maximum emission rate for each metal specified as the
    average emission rate during the trial burn;
     
    ii) Feed rate of total hazardous waste and pumpable hazardous
    waste, each measured and specified as prescribed in
    subsection (e)(6)(A) of this Section;
     
    iii) Feed rate of each metal in the following feedstreams,
    measured and specified as prescribed in subsection (e)(6) of
    this Section: total hazardous waste feed; and total pumpable
    hazardous waste feed;
     
    iv) Total feed rate of chlorine and chloride in total feed streams
    measured and specified prescribed in subsection (e)(6) of this
    Section;
     
    v) Maximum combustion gas temperature measured at a
    location indicative of combustion chamber temperature, and
    measured and specified as prescribed in subsection (e)(6) of

     
    721
    this Section;
     
    vi) Maximum flue gas temperature at the inlet to the PM APCS
    measured and specified as prescribed in subsection (e)(6) of
    this Section;
     
    vii) Maximum device production rate when producing normal
    product expressed in appropriate units and measured and
    specified as prescribed in subsection (e)(6) of this Section;
     
    viii) Appropriate controls on operation and maintenance of the
    hazardous waste firing system and any APCS;
     
    ix) Allowable variation in BIF system design including any
    APCS or operating procedures; and
     
    x) Such other operating requirements as are necessary to ensure
    that the metals standards under Sections 726.206(c) or (d) are
    met.
     
    5) Requirements to ensure conformance with the HCl and chlorine gas
    standards.
     
    A) For conformance with the Tier I total chlorine and chloride feed rate
    screening limits of Section 726.207(b)(1), the permit must specify the
    following operating requirements:
     
    i) Feed rate of total chlorine and chloride in hazardous waste,
    other fuels and industrial furnace feedstocks measured and
    specified as prescribed in subsection (e)(6) of this Section;
     
    ii) Feed rate of total hazardous waste measured and specified as
    prescribed in subsection (e)(6) of this Section; and
     
    iii) A sampling and analysis program for total chlorine and
    chloride for the hazardous waste, other fuels and industrial
    furnace feedstocks;
     
    B) For conformance with the Tier II HCl and chlorine gas emission rate
    screening limits under Section 726.207(b)(2) and the Tier III HCl and
    chlorine gas controls under Section 726.207(c), the permit must
    specify the following operating requirements:
     
    i) Maximum emission rate for HCl and for chlorine gas
    specified as the average emission rate during the trial burn;
     

     
    722
    ii) Feed rate of total hazardous waste measured and specified as
    prescribed in subsection (e)(6) of this Section;
     
    iii) Total feed rate of chlorine and chloride in total feed streams,
    measured and specified as prescribed in subsection (e)(6) of
    this Section;
     
    iv) Maximum device production rate when producing normal
    product expressed in appropriate units, measured and
    specified as prescribed in subsection (e)(6) of this Section;
     
    v) Appropriate controls on operation and maintenance of the
    hazardous waste firing system and any APCS;
     
    vi) Allowable variation in BIF system design including any
    APCS or operating procedures; and
     
    vii) Such other operating requirements as are necessary to ensure
    that the HCl and chlorine gas standards under Section
    726.207(b)(2) or (c) are met.
     
    6) Measuring parameters and establishing limits based on trial burn data.
     
    A) General requirements. As specified in subsections (e)(2) through
    (e)(5) of this Section, each operating parameter must be measured,
    and permit limits on the parameter must be established, according to
    either of the following procedures:
     
    i) Instantaneous limits. A parameter is measured and recorded
    on an instantaneous basis (i.e., the value that occurs at any
    time) and the permit limit specified as the time-weighted
    average during all valid runs of the trial burn; or
     
    ii) Hourly rolling average. The limit for a parameter must be
    established and continuously monitored on an hourly rolling
    average basis, as defined in Section 726.200(i). The permit
    limit for the parameter must be established based on trial burn
    data as the average over all valid test runs of the highest
    hourly rolling average value for each run.
     
    B) Rolling average limits for carcinogenic metals and lead. Feed rate
    limits for the carcinogenic metals (as defined in Section 726.200(i))
    and lead must be established either on an hourly rolling average
    basis, as prescribed by subsection (e)(6)(A) of this Section, or on (up
    to) a 24 hour rolling average basis. If the owner or operator elects to
    use an average period from 2 to 24 hours, the following

     
    723
    requirements apply:
     
    i) The feed rate of each metal must be limited at any time to ten
    times the feed rate that would be allowed on an hourly rolling
    average basis;
     
    ii) Terms are as defined in Section 726.200(i); and
     
    iii) The permit limit for the feed rate of each metal must be
    established based on trial burn data as the average over all
    valid test runs of the highest hourly rolling average feed rate
    for each run.
     
    C) Feed rate limits for metals, total chlorine and chloride, and ash. Feed
    rate limits for metals, total chlorine and chloride, and ash are
    established and monitored by knowing the concentration of the
    substance (i.e., metals, chloride/chlorine and ash) in each feedstream
    and the flow rate of the feedstream. To monitor the feed rate of these
    substances, the flow rate of each feedstream must be monitored under
    the continuous monitoring requirements of subsections (e)(6)(A) and
    (e)(6)(B) of this Section.
     
    D) Conduct of trial burn testing.
     
    i) If compliance with all applicable emissions standards of
    Sections 726.204 through 726.207 is not demonstrated
    simultaneously during a set of test runs, the operating
    conditions of additional test runs required to demonstrate
    compliance with remaining emissions standards must be as
    close as possible to the original operating conditions.
     
    ii) Prior to obtaining test data for purposes of demonstrating
    compliance with the emissions standards of Sections 726.204
    through 726.207 or establishing limits on operating
    parameters under this Section, the unit must operate under
    trial burn conditions for a sufficient period to reach steady-
    state operations. However, industrial furnaces that recycle
    collected PM back into the furnace and that comply with an
    alternative implementation approach for metals under Section
    726.206(f) need not reach steady state conditions with respect
    to the flow of metals in the system prior to beginning
    compliance testing for metals emissions.
     
    iii) Trial burn data on the level of an operating parameter for
    which a limit must be established in the permit must be
    obtained during emissions sampling for the pollutants (i.e.,

     
    724
    metals, PM, HCl/chlorine gas, organic compounds) for which
    the parameter must be established as specified by this
    subsection (e).
     
    7) General requirements.
     
    A) Fugitive emissions. Fugitive emissions must be controlled in one of
    the following ways:
     
    i) By keeping the combustion zone totally sealed against
    fugitive emissions; or
     
    ii) By maintaining the combustion zone pressure lower than
    atmospheric pressure; or
     
    iii) By an alternative means of control demonstrated (with Part B
    of the permit application) to provide fugitive emissions
    control equivalent to maintenance of combustion zone
    pressure lower than atmospheric pressure.
     
    B) Automatic waste feed cutoff. A BIF must be operated with a
    functioning system that automatically cuts off the hazardous waste
    feed when operating conditions deviate from those established under
    this Section. In addition, the following requirements apply:
     
    i) The permit limit for (the indicator of) minimum combustion
    chamber temperature must be maintained while hazardous
    waste or hazardous waste residues remain in the combustion
    chamber,;
     
    ii) Exhaust gases must be ducted to the APCS operated in
    accordance with the permit requirements while hazardous
    waste or hazardous waste residues remain in the combustion
    chamber; and
     
    iii) Operating parameters for which permit limits are established
    must continue to be monitored during the cutoff, and the
    hazardous waste feed must not be restarted until the levels of
    those parameters comply with the permit limits. For
    parameters that are monitored on an instantaneous basis, the
    Agency must establish a minimum period of time after a
    waste feed cutoff during which the parameter must not
    exceed the permit limit before the hazardous waste feed is
    restarted.
     
    C) Changes. A BIF must cease burning hazardous waste when

     
    725
    combustion properties or feed rates of the hazardous waste, other
    fuels or industrial furnace feedstocks, or the BIF design or operating
    conditions deviate from the limits as specified in the permit.
     
    8) Monitoring and Inspections.
     
    A) The owner or operator must monitor and record the following, at a
    minimum, while burning hazardous waste:
     
    i) If specified by the permit, feed rates and composition of
    hazardous waste, other fuels, and industrial furnace
    feedstocks and feed rates of ash, metals, and total chlorine
    and chloride;
     
    ii) If specified by the permit, CO, HCs, and oxygen on a
    continuous basis at a common point in the BIF downstream
    of the combustion zone and prior to release of stack gases to
    the atmosphere in accordance with operating requirements
    specified in subsection (e)(2)(B) of this Section. CO, HC,
    and oxygen monitors must be installed, operated, and
    maintained in accordance with methods specified in
    Appendix I of this Part.; and
     
    iii) Upon the request of the Agency, sampling and analysis of the
    hazardous waste (and other fuels and industrial furnace
    feedstocks as appropriate), residues, and exhaust emissions
    must be conducted to verify that the operating requirements
    established in the permit achieve the applicable standards of
    Sections 726.204, 726.205, 726.206, and 726.207.
     
    B) All monitors must record data in units corresponding to the permit
    limit unless otherwise specified in the permit.
     
    C) The BIF and associated equipment (pumps, values, pipes, fuel storage
    tanks, etc.) must be subjected to thorough visual inspection when it
    contains hazardous waste, at least daily for leaks, spills, fugitive
    emissions, and signs of tampering.
     
    D) The automatic hazardous waste feed cutoff system and associated
    alarms must be tested at least once every seven days when hazardous
    waste is burned to verify operability, unless the applicant
    demonstrates to the Agency that weekly inspections will unduly
    restrict or upset operations and that less frequent inspections will be
    adequate. At a minimum, operational testing must be conducted at
    least once every 30 days.
     

     
    726
    E) These monitoring and inspection data must be recorded and the
    records must be placed in the operating record required by 35 Ill.
    Adm. Code 724.173.
     
    9) Direct transfer to the burner. If hazardous waste is directly transferred from a
    transport vehicle to a BIF without the use of a storage unit, the owner and
    operator must comply with Section 726.211.
     
    10) Recordkeeping. The owner or operator must keep in the operating record of
    the facility all information and data required by this Section until closure of
    the facility.
     
    11) Closure. At closure, the owner or operator must remove all hazardous waste
    and hazardous waste residues (including, but not limited to, ash, scrubber
    waters, and scrubber sludges) from the BIF.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.203 Interim Status Standards for Burners
     
    a) Purpose, scope, and applicability.
     
    1) General.
     
    A) The purpose of this Section is to establish minimum national
    standards for owners and operators of “existing” BIFs that burn
    hazardous waste where such standards define the acceptable
    management of hazardous waste during the period of interim status.
    The standards of this Section apply to owners and operators of
    existing facilities until either a permit is issued under Section
    726.202(d) or until closure responsibilities identified in this Section
    are fulfilled.
     
    B) “Existing” or “in existence” means a BIF for which the owner or
    operator filed a certification of precompliance with USEPA pursuant
    to federal 40 CFR 266.103(b), incorporated by reference in
    subsection (b) of this Section; provided, however, that USEPA has
    not determined that the certification is invalid.
     
    C) If a BIF is located at a facility that already has a RCRA permit or
    interim status, then the owner or operator must comply with the
    applicable regulations dealing with permit modifications in 35 Ill.
    Adm. Code 703.280 or changes in interim status in 35 Ill. Adm. Code
    703.155.
     
    2) Exemptions. The requirements of this Section do not apply to hazardous

     
    727
    waste and facilities exempt under Section 726.200(b) or 726.208.
     
    3) Prohibition on burning dioxin-listed wastes. The following hazardous waste
    listed for dioxin and hazardous waste derived from any of these wastes must
    not be burned in a BIF operating under interim status: USEPA hazardous
    waste numbers F020, F021, F022, F023, F026, and F027.
     
    4) Applicability of 35 Ill. Adm. Code 725 standards. An owner or operator of a
    BIF that burns hazardous waste and which is operating under interim status is
    subject to the following provisions of 35 Ill. Adm. Code 725, except as
    provided otherwise by this Section:
     
    A) In Subpart A of 35 Ill. Adm. Code 725 (General), 35 Ill. Adm. Code
    725.104;
     
    B) In Subpart B of 35 Ill. Adm. Code 725 (General facility standards),
    35 Ill. Adm. Code 725.111 through 725.117;
     
    C) In Subpart C of 35 Ill. Adm. Code 725 (Preparedness and
    prevention), 35 Ill. Adm. Code 725.131 through 725.137;
     
    D) In Subpart D of 35 Ill. Adm. Code 725 (Contingency plan and
    emergency procedures), 35 Ill. Adm. Code 725.151 through 725.156;
     
    E) In Subpart E of 35 Ill. Adm. Code 725 (Manifest system,
    recordkeeping and reporting), 35 Ill. Adm. Code 725.171 through
    725.177, except that 35 Ill. Adm. Code 725.171, 725.172 and
    725.176 do not apply to owners and operators of on-site facilities that
    do not receive any hazardous waste from off-site sources;
     
    F) In Subpart G of 35 Ill. Adm. Code 725 (Closure and post-closure),
    35 Ill. Adm. Code 725.211 through 725.215;
     
    G) In Subpart H of 35 Ill. Adm. Code 725 (Financial requirements), 35
    Ill. Adm. Code 725.241, 725.242, 725.243, and 725.247 through
    725.251, except that the State of Illinois and the Federal federal
    government are exempt from the requirements of Subpart H of 35 Ill.
    Adm. Code 725; and
     
    H) In Subpart BB of 35 Ill. Adm. Code 725 (Air emission standards for
    equipment leaks), except 35 Ill. Adm. Code 725.950(a).
     
    5) Special requirements for furnaces. The following controls apply during
    interim status to industrial furnaces (e.g., kilns, cupolas) that feed hazardous
    waste for a purpose other than solely as an ingredient (see subsection
    (a)(5)(B) of this Section) at any location other than the hot end where

     
    728
    products are normally discharged or where fuels are normally fired:
     
    A) Controls.
     
    i) The hazardous waste must be fed at a location where
    combustion gas temperature is at least 1800° F;
     
    ii) The owner or operator must determine that adequate oxygen
    is present in combustion gases to combust organic
    constituents in the waste and retain documentation of such
    determination in the facility record;
     
    iii) For cement kiln systems, the hazardous waste must be fed
    into the kiln; and
     
    iv) The HC controls of Section 726.204(f) or subsection (c)(5) of
    this Section apply upon certification of compliance under
    subsection (c) of this Section, irrespective of the CO level
    achieved during the compliance test.
     
    B) Burning hazardous waste solely as an ingredient. A hazardous waste
    is burned for a purpose other than “solely as an ingredient” if it meets
    either of the following criteria:
     
    i) The hazardous waste has a total concentration of nonmetal
    compounds listed in Appendix H of 35 Ill. Adm. Code 721,
    exceeding 500 ppm by weight, as fired and so is considered to
    be burned for destruction. The concentration of nonmetal
    compounds in a waste as-generated may be reduced to the
    500 ppm limit by bona fide treatment that removes or
    destroys nonmetal constituents. Blending for dilution to meet
    the 500 ppm limit is prohibited and documentation that the
    waste has not been impermissibly diluted must be retained in
    the facility record; or
     
    ii) The hazardous waste has a heating value of 5,000 Btu/lb or
    more, as fired, and so is considered to be burned as fuel. The
    heating value of a waste as-generated may be reduced to
    below the 5,000 Btu/lb limit by bona fide treatment that
    removes or destroys organic constituents. The heating value
    of a waste as-generated may be reduced to below the 5,000
    Btu/lb limit by bona fide treatment that removes or destroys
    organic constituents. Blending to augment the heating value
    to meet the 5,000 Btu/lb limit is prohibited and
    documentation that the waste has not been impermissibly
    blended must be retained in the facility record.

     
    729
     
    6) Restrictions on burning hazardous waste that is not a fuel. Prior to
    certification of compliance under subsection (c) of this Section, an owner or
    operator must not feed hazardous waste that has a heating value less than
    5000 Btu/lb, as generated, (except that the heating value of a waste as-
    generated may be increased to above the 5,000 Btu/lb limit by bona fide
    treatment; however blending to augment the heating value to meet the 5,000
    Btu/lb limit is prohibited and records must be kept to document that
    impermissible blending has not occurred) in a BIF, except that the following
    may occur:
     
    A) Hazardous waste may be burned solely as an ingredient;
     
    B) Hazardous waste may be burned for purposes of compliance testing
    (or testing prior to compliance testing) for a total period of time not to
    exceed 720 hours;
     
    C) Such waste may be burned if the Agency has documentation to show
    that the following was true prior to August 21, 1991:
     
    i) The BIF was operating under the interim status standards for
    incinerators or thermal treatment units, Subparts O or P of 35
    Ill. Adm. Code 725;
     
    ii) The BIF met the interim status eligibility requirements under
    35 Ill. Adm. Code 703.153 for Subparts O or P of 35 Ill.
    Adm. Code 725; and
     
    iii) Hazardous waste with a heating value less than 5,000 Btu/lb
    was burned prior to that date; or
     
    D) Such waste may be burned in a halogen acid furnace if the waste was
    burned as an excluded ingredient under 35 Ill. Adm. Code 721.102(e)
    prior to February 21, 1991, and documentation is kept on file
    supporting this claim.
     
    7) Direct transfer to the burner. If hazardous waste is directly transferred from a
    transport vehicle to a BIF without the use of a storage unit, the owner or
    operator must comply with Section 726.211.
     
    b) Certification of precompliance. This subsection corresponds with 40 CFR
    266.103(b), under which USEPA required certain owners and operators to file a
    certification of precompliance by August 21, 1991. No similar filing with the
    Agency was required, so the Board did not incorporate the federal filing
    requirement into the Illinois regulations. This statement maintains structural
    parity with the federal regulations.

     
    730
     
    c) Certification of compliance. The owner or operator must conduct emissions testing
    to document compliance with the emissions standards of Sections 726.204(b)
    through (e), 726.205, 726.206, and 726.207 and subsection (a)(5)(A)(iv) of this
    Section under the procedures prescribed by this subsection (c), except under
    extensions of time provided by subsection (c)(7) of this Section. Based on the
    compliance test, the owner or operator must submit to the Agency, on or before
    August 21, 1992, a complete and accurate “certification of compliance” (under
    subsection (c)(4) of this Section) with those emission standards establishing limits on
    the operating parameters specified in subsection (c)(1) of this Section.
     
    1) Limits on operating conditions. The owner or operator must establish limits
    on the following parameters based on operations during the compliance test
    (under procedures prescribed in subsection (c)(4)(D) of this Section) or as
    otherwise specified and include these limits with the certification of
    compliance. The BIF must be operated in accordance with these operating
    limits and the applicable emissions standards of Sections 726.204(b) through
    (e), 726.205, 726.206, and 726.207 and subsection (a)(5)(A)(iv) of this
    Section at all times when there is hazardous waste in the unit.
     
    A) Feed rate of total hazardous waste and (unless complying the Tier I or
    adjusted Tier I metals feed rate screening limits under Section
    726.206(b) or (e)), pumpable hazardous waste;
     
    B) Feed rate of each metal in the following feedstreams:
     
    i) Total feedstreams, except that industrial furnaces which must
    comply with the alternative metals implementation approach
    under subsection (c)(3)(B) of this Section must specify limits
    on the concentration of each metal in collected PM in lieu of
    feed rate limits for total feedstreams; and facilities that
    comply with Tier I or Adjusted Tier I metals feed rate
    screening limits may set their operating limits at the metal
    feed rate screening limits determined under subsection
    726.206(b) or (e) of this Section;
     
    BOARD NOTE: Federal subsections 266.103(c)(1)(ii)(A)(1)
    and (c)(1)(ii)(A)(2) are condensed into subsection
    (c)(1)(B)(i).
     
    ii) Total hazardous waste feed (unless complying with the Tier I
    or adjusted Tier I metals feed rate screening limits under
    Section 726.206(b) or (e)); and
     
    iii) Total pumpable hazardous waste feed (unless complying with
    Tier I or Adjusted Tier I metals feed rate screening limits

     
    731
    under Section 726.206(b) or (e));
     
    C) Total feed rate of total chlorine and chloride in total feed streams,
    except that facilities that comply with Tier I or Adjusted Tier I feed
    rate screening limits may set their operating limits at the total
    chlorine and chloride feed rate screening limits determined under
    Section 726.207(b)(1) or (e);
     
    D) Total feed rate of ash in total feed streams, except that the ash feed
    rate for cement kilns and light-weight aggregate kilns is not limited;
     
    E) CO concentration, and where required, HC concentration in stack
    gas. When complying with the CO controls of Section 726.204(b),
    the CO limit is 100 ppmv, and when complying with the HC controls
    of Section 726.204(c), the HC limit is 20 ppmv. When complying
    with the CO controls of Section 726.204(c), the CO limit is
    established based on the compliance test;
     
    F) Maximum production rate of the device in appropriate units when
    producing normal product unless complying with Tier I or Adjusted
    Tier I feed rate screening limits for chlorine under Section
    726.207(b)(1) or (e) and for all metals under Section 726.207(b) or
    (e), and the uncontrolled particulate emissions do not exceed the
    standard under Section 726.205;
     
    G) Maximum combustion chamber temperature where the temperature
    measurement is as close to the combustion zone as possible and is
    upstream of any quench water injection, (unless complying with the
    Tier I adjusted Tier I metals feed rate screening limits under Section
    726.206(b) or (e));
     
    H) Maximum flue gas temperature entering a PM control device (unless
    complying with Tier I or adjusted Tier I metals feed rate screening
    limits under Section 726.206(b) or (e));
     
    I) For systems using wet scrubbers, including wet ionizing scrubbers
    (unless complying with the Tier I or adjusted Tier I metals feed rate
    screening limits under Section 726.206(b) or (e) and the total chlorine
    and chloride feed rate screening limits under Section 726.207(b)(1) or
    (e)):
     
    i) Minimum liquid to flue gas ratio;
     
    ii) Minimum scrubber blowdown from the system or maximum
    suspended solids content of scrubber water; and
     

     
    732
    iii) Minimum pH level of the scrubber water;
     
    J) For systems using venturi scrubbers, the minimum differential gas
    pressure across the venturi (unless complying the Tier I or adjusted
    Tier I metals feed rate screening limits under Section 726.206(b) or
    (e) and the total chlorine and chloride feed rate screening limits under
    Section 726.207(b)(1) or (e));
     
    K) For systems using dry scrubbers (unless complying with the Tier I or
    adjusted Tier I metals feed rate screening limits under Section
    726.206(b) or (e) and the total chlorine and chloride feed rate
    screening limits under Section 726.207(b)(1) or (e)):
     
    i) Minimum caustic feed rate; and
     
    ii) Maximum flue gas flow rate;
     
    L) For systems using wet ionizing scrubbers or electrostatic precipitators
    (unless complying with the Tier I or adjusted Tier I metals feed rate
    screening limits under Section 726.206(b) or (e) and the total chlorine
    and chloride feed rate screening limits under Section 726.207(b)(1) or
    (e)):
     
    i) Minimum electrical power in kVA to the precipitator plates;
    and
     
    ii) Maximum flue gas flow rate;
     
    M) For systems using fabric filters (baghouses), the minimum pressure
    drop (unless complying with the Tier I or adjusted Tier I metals feed
    rate screening limits under Section 726.206(b) or (e) and the total
    chlorine and chloride feed rate screening limits under Section
    726.207(b)(1) or (e)).
     
    2) Prior notice of compliance testing. At least 30 days prior to the compliance
    testing required by subsection (c)(3) of this Section, the owner or operator
    must notify the Agency and submit the following information:
     
    A) General facility information including:
     
    i) USEPA facility ID number;
     
    ii) Facility name, contact person, telephone number, and
    address;
     
    iii) Person responsible for conducting compliance test, including

     
    733
    company name, address, and telephone number, and a
    statement of qualifications;
     
    iv) Planned date of the compliance test;
     
    B) Specific information on each device to be tested, including the
    following:
     
    i) A Description of BIF;
     
    ii) A scaled plot plan showing the entire facility and location of
    the BIF;
     
    iii) A description of the APCS;
     
    iv) Identification of the continuous emission monitors that are
    installed, including the following: CO monitor; Oxygen
    monitor; HC monitor, specifying the minimum temperature of
    the system, and, if the temperature is less than 150° C, an
    explanation of why a heated system is not used (see
    subsection (c)(5) of this Section) and a brief description of the
    sample gas conditioning system;
     
    v) Indication of whether the stack is shared with another device
    that will be in operation during the compliance test; and
     
    vi) Other information useful to an understanding of the system
    design or operation; and
     
    C) Information on the testing planned, including a complete copy of the
    test protocol and QA/QC plan, and a summary description for each
    test providing the following information at a minimum:
     
    i) Purpose of the test (e.g., demonstrate compliance with
    emissions of PM); and
     
    ii) Planned operating conditions, including levels for each
    pertinent parameter specified in subsection (c)(1) of this
    Section.
     
    3) Compliance testing.
     
    A) General. Compliance testing must be conducted under conditions for
    which the owner or operator has submitted a certification of
    precompliance under subsection (b) of this Section and under
    conditions established in the notification of compliance testing

     
    734
    required by subsection (c)(2) of this Section. The owner or operator
    may seek approval on a case-by-case basis to use compliance test
    data from one unit in lieu of testing a similar on-site unit. To support
    the request, the owner or operator must provide a comparison of the
    hazardous waste burned and other feedstreams, and the design,
    operation, and maintenance of both the tested unit and the similar
    unit. The Agency must provide a written approval to use compliance
    test data in lieu of testing a similar unit if the Agency finds that the
    hazardous wastes, devices and the operating conditions are
    sufficiently similar, and the data from the other compliance test is
    adequate to meet the requirements of this subsection (c).
     
    B) Special requirements for industrial furnaces that recycle collected
    PM. Owners and operators of industrial furnaces that recycle back
    into the furnace PM from the APCS must comply with one of the
    following procedures for testing to determine compliance with the
    metals standards of Section 726.206(c) or (d):
     
    i) The special testing requirements prescribed in “Alternative
    Method for Implementing Metals Controls” in Appendix I to
    this Part;
     
    ii) Stack emissions testing for a minimum of six hours each day
    while hazardous waste is burned during interim status. The
    testing must be conducted when burning normal hazardous
    waste for that day at normal feed rates for that day and when
    the APCS is operated under normal conditions. During
    interim status, hazardous waste analysis for metals content
    must be sufficient for the owner or operator to determine if
    changes in metals content affect the ability of the unit to meet
    the metals emissions standards established under Section
    726.206(c) or (d). Under this option, operating limits (under
    subsection (c)(1) of this Section) must be established during
    compliance testing under this subsection (c)(3) only on the
    following parameters: feed rate of total hazardous waste;
    total feed rate of total chlorine and chloride in total feed
    streams; total feed rate of ash in total feed streams, except that
    the ash feed rate for cement kilns and light-weight aggregate
    kilns is not limited; CO concentration, and where required,
    HC concentration in stack gas; and maximum production rate
    of the device in appropriate units when producing normal
    product; or
     
    iii) Conduct compliance testing to determine compliance with the
    metals standards to establish limits on the operating
    parameters of subsection (c)(1) of this Section only after the

     
    735
    kiln system has been conditioned to enable it to reach
    equilibrium with respect to metals fed into the system and
    metals emissions. During conditioning, hazardous waste and
    raw materials having the same metals content as will be fed
    during the compliance test must be fed at the feed rates that
    will be fed during the compliance test.
     
    C) Conduct of compliance testing.
     
    i) If compliance with all applicable emissions standards of
    Sections 726.204 through 726.207 is not demonstrated
    simultaneously during a set of test runs, the operating
    conditions of additional test runs required to demonstrate
    compliance with remaining emissions standards must be as
    close as possible to the original operating conditions.
     
    ii) Prior to obtaining test data for purposes of demonstrating
    compliance with the applicable emissions standards of
    Sections 726.204 through 726.207 or establishing limits on
    operating parameters under this Section, the facility must
    operate under compliance test conditions for a sufficient
    period to reach steady-state operations. Industrial furnaces
    that recycle collected PM back into the furnace and that
    comply with subsection (c)(3)(B)(i) or (c)(3)(B)(ii) of this
    Section, however, need not reach steady state conditions with
    respect to the flow of metals in the system prior to beginning
    compliance testing for metals.
     
    iii) Compliance test data on the level of an operating parameter
    for which a limit must be established in the certification of
    compliance must be obtained during emissions sampling for
    the pollutants (i.e., metals, PM, HCl/chlorine gas, organic
    compounds) for which the parameter must be established as
    specified by subsection (c)(1) of this Section.
     
    4) Certification of compliance. Within 90 days of completing compliance
    testing, the owner or operator must certify to the Agency compliance with the
    emissions standards of Sections 726.204(b), (c) and (e); 726.205; 726.206;
    726.207; and subsection (a)(5)(A)(iv) of this Section. The certification of
    compliance must include the following information:
     
    A) General facility and testing information, including the following:
     
    i) USEPA facility ID number;
     
    ii) Facility name, contact person, telephone number, and

     
    736
    address;
     
    iii) Person responsible for conducting compliance testing,
    including company name, address, and telephone number,
    and a statement of qualifications;
     
    iv) Dates of each compliance test;
     
    v) Description of BIF tested;
     
    vi) Person responsible for QA/QC, title and telephone number,
    and statement that procedures prescribed in the QA/QC plan
    submitted under Section 726.203(c)(2)(C) have been
    followed, or a description of any changes and an explanation
    of why changes were necessary;
     
    vii) Description of any changes in the unit configuration prior to
    or during testing that would alter any of the information
    submitted in the prior notice of compliance testing under
    subsection (c)(2) of this Section and an explanation of why
    the changes were necessary;
     
    viii) Description of any changes in the planned test conditions
    prior to or during the testing that alter any of the information
    submitted in the prior notice of compliance testing under
    subsection (c)(2) of this Section and an explanation of why
    the changes were necessary; and
     
    ix) The complete report on results of emissions testing.
     
    B) Specific information on each test, including the following:
     
    i) Purposes of test (e.g., demonstrate conformance with the
    emissions limits for PM, metals, HCl, chlorine gas, and CO);
     
    ii) Summary of test results for each run and for each test
    including the following information: date of run; duration of
    run; time-weighted average and highest hourly rolling
    average CO level for each run and for the test; highest hourly
    rolling average HC level, if HC monitoring is required for
    each run and for the test; if dioxin and furan testing is
    required under Section 726.204(e), time-weighted average
    emissions for each run and for the test of chlorinated dioxin
    and furan emissions, and the predicted maximum annual
    average ground level concentration of the toxicity
    equivalency factor (defined in Section 726.200(i)); time-

     
    737
    weighted average PM emissions for each run and for the test;
    time-weighted average HCl and chlorine gas emissions for
    each run and for the test; time-weighted average emissions
    for the metals subject to regulation under Section 726.206 for
    each run and for the test; and QA/QC results.
     
    C) Comparison of the actual emissions during each test with the
    emissions limits prescribed by Sections 726.204(b), (c), and (e);
    726.205; 726.206; and 726.207 and established for the facility in the
    certification of precompliance under subsection (b) of this Section.
     
    D) Determination of operating limits based on all valid runs of the
    compliance test for each applicable parameter listed in subsection
    (c)(1) of this Section using one of the following procedures:
     
    i) Instantaneous limits. A parameter must be measured and
    recorded on an instantaneous basis (i.e., the value that occurs
    at any time) and the operating limit specified as the time-
    weighted average during all runs of the compliance test.
     
    ii) Hourly rolling average basis. The limit for a parameter must
    be established and continuously monitored on an hourly
    rolling average basis, as defined in Section 726.200(i). The
    operating limit for the parameter must be established based
    on compliance test data as the average over all test runs of the
    highest hourly rolling average value for each run.
     
    iii) Rolling average limits for carcinogenic metals (as defined in
    Section 726.200(i)) and lead. Feed rate limits for the
    carcinogenic metals and lead must be established either on an
    hourly rolling average basis as prescribed by subsection
    (c)(4)(D)(ii) of this Section or on (up to) a 24 hour rolling
    average basis. If the owner or operator elects to use an
    averaging period from two to 24 hours the following must
    occur: the feed rate of each metal must be limited at any time
    to ten times the feed rate that would be allowed on a hourly
    rolling average basis; the operating limit for the feed rate of
    each metal must be established based on compliance test data
    as the average over all test runs of the highest hourly rolling
    average feed rate for each run; and the continuous monitor
    and the rolling average for the selected averaging period
    are as defined in Section 726.200(i).
     
    iv) Feed rate limits for metals, total chlorine and chloride, and
    ash. Feed rate limits for metals, total chlorine and chloride,
    and ash are established and monitored by knowing the

     
    738
    concentration of the substance (i.e., metals, chloride/chlorine,
    and ash) in each feedstream and the flow rate of the
    feedstream. To monitor the feed rate of these substances, the
    flow rate of each feedstream must be monitored under the
    continuous monitoring requirements of subsections
    (c)(4)(D)(i) through (c)(4)(D)(iii) of this Section.
     
    E) Certification of compliance statement. The following statement must
    accompany the certification of compliance:
     
    “I certify under penalty of law that this information was
    prepared under my direction or supervision in accordance
    with a system designed to ensure that qualified personnel
    properly gathered and evaluated the information and
    supporting documentation. Copies of all emissions tests,
    dispersion modeling results, and other information used to
    determine conformance with the requirements of 35 Ill. Adm.
    Code 726.203(c) are available at the facility and can be
    obtained from the facility contact person listed above. Based
    on my inquiry of the person or persons who manage the
    facility, or those persons directly responsible for gathering the
    information, the information submitted is, to the best of my
    knowledge and belief, true, accurate, and complete. I am
    aware that there are significant penalties for submitting false
    information, including the possibility of fine and
    imprisonment for knowing violations.
     
    I also acknowledge that the operating limits established
    pursuant to 35 Ill. Adm. Code 726.203(c)(4)(D) are
    enforceable limits at which the facility can legally operate
    during interim status until a revised certification of
    compliance is submitted.”
     
    5) Special requirements for HC monitoring systems. When an owner or
    operator is required to comply with the HC controls provided by Section
    726.204(c) or subsection (a)(5)(A)(iv) of this Section, a conditioned gas
    monitoring system may be used in conformance with specifications provided
    in Appendix I to this Part provided that the owner or operator submits a
    certification of compliance without using extensions of time provided by
    subsection (c)(7) of this Section.
     
    6) Special operating requirements for industrial furnaces that recycle collected
    PM. Owners and operators of industrial furnaces that recycle back into the
    furnace PM from the APCS must do the following:
     
    A) When complying with the requirements of subsection (c)(3)(B)(i) of

     
    739
    this Section, comply with the operating requirements prescribed in
    “Alternative Method to Implement the Metals Controls” in Appendix
    I to this Part; and
     
    B) When complying with the requirements of subsection (c)(3)(B)(ii) of
    this Section, comply with the operating requirements prescribed by
    that subsection.
     
    7) Extensions of time.
     
    A) If the owner or operator does not submit a complete certification of
    compliance for all of the applicable emissions standards of Sections
    726.204, 726.205, 726.206, and 726.207 by August 21, 1992, the
    owner or operator must do the following:
     
    i) Stop burning hazardous waste and begin closure activities
    under subsection (l) of this Section for the hazardous waste
    portion of the facility;
     
    ii) Limit hazardous waste burning only for purposes of
    compliance testing (and pretesting to prepare for compliance
    testing) a total period of 720 hours for the period of time
    beginning August 21, 1992, submit a notification to the
    Agency by August 21, 1992 stating that the facility is
    operating under restricted interim status and intends to
    resume burning hazardous waste, and submit a complete
    certification of compliance by August 23, 1993; or
     
    iii) Obtain a case-by-case extension of time under subsection
    (c)(7)(B) of this Section.
     
    B) Case-by-case extensions of time. See Section 726.219.
     
    8) Revised certification of compliance. The owner or operator may submit at
    any time a revised certification of compliance (recertification of compliance)
    under the following procedures:
     
    A) Prior to submittal of a revised certification of compliance, hazardous
    waste must not be burned for more than a total of 720 hours under
    operating conditions that exceed those established under a current
    certification of compliance, and such burning must be conducted only
    for purposes of determining whether the facility can operate under
    revised conditions and continue to meet the applicable emissions
    standards of Sections 726.204, 726.205, 726.206, and 726.207;
     
    B) At least 30 days prior to first burning hazardous waste under

     
    740
    operating conditions that exceed those established under a current
    certification of compliance, the owner or operator must notify the
    Agency and submit the following information:
     
    i) USEPA facility ID number, and facility name, contact person,
    telephone number, and address;
     
    ii) Operating conditions that the owner or operator is seeking to
    revise and description of the changes in facility design or
    operation that prompted the need to seek to revise the
    operating conditions;
     
    iii) A determination that, when operating under the revised
    operating conditions, the applicable emissions standards of
    Sections 726.204, 726.205, 726.206, and 726.207 are not
    likely to be exceeded. To document this determination, the
    owner or operator must submit the applicable information
    required under subsection (b)(2) of this Section; and
     
    iv) Complete emissions testing protocol for any pretesting and
    for a new compliance test to determine compliance with the
    applicable emissions standards of Sections 726.204, 726.205,
    726.206, and 726.207 when operating under revised operating
    conditions. The protocol must include a schedule of pre-
    testing and compliance testing. If the owner or operator
    revises the scheduled date for the compliance test, the owner
    or operator must notify the Agency in writing at least 30 days
    prior to the revised date of the compliance test;
     
    C) Conduct a compliance test under the revised operating conditions and
    the protocol submitted to the Agency to determine compliance with
    the applicable emissions standards of Sections 726.204, 726.205,
    726.206, and 726.207; and
     
    D) Submit a revised certification of compliance under subsection (c)(4)
    of this Section.
     
    d) Periodic Recertifications. The owner or operator must conduct compliance testing
    and submit to the Agency a recertification of compliance under provisions of
    subsection (c) of this Section within three years from submitting the previous
    certification or recertification. If the owner or operator seeks to recertify compliance
    under new operating conditions, the owner or operator must comply with the
    requirements of subsection (c)(8) of this Section.
     
    e) Noncompliance with certification schedule. If the owner or operator does not
    comply with the interim status compliance schedule provided by subsections (b), (c),

     
    741
    and (d) of this Section, hazardous waste burning must terminate on the date that the
    deadline is missed, closure activities must begin under subsection (l) of this Section,
    and hazardous waste burning must not resume except under an operating permit
    issued under 35 Ill. Adm. Code 703.232. For purposes of compliance with the
    closure provisions of subsection (l) of this Section and 35 Ill. Adm. Code
    725.212(d)(2) and 725.213, the BIF has received “the known final volume of
    hazardous waste” on the date the deadline is missed.
     
    f) Start-up and shut-down. Hazardous waste (except waste fed solely as an ingredient
    under the Tier I (or adjusted Tier I) feed rate screening limits for metals and
    chloride/chlorine) must not be fed into the device during start-up and shut-down of
    the BIF, unless the device is operating within the conditions of operation specified in
    the certification of compliance.
     
    g) Automatic waste feed cutoff. During the compliance test required by subsection
    (c)(3) of this Section and upon certification of compliance under subsection (c) of
    this Section, a BIF must be operated with a functioning system that automatically
    cuts off the hazardous waste feed when the applicable operating conditions specified
    in subsections (c)(1)(A) and (c)(1)(E) through (c)(1)(M) of this Section deviate from
    those established in the certification of compliance. In addition, the following must
    occur:
     
    1) To minimize emissions of organic compounds, the minimum combustion
    chamber temperature (or the indicator of combustion chamber temperature)
    that occurred during the compliance test must be maintained while hazardous
    waste or hazardous waste residues remain in the combustion chamber, with
    the minimum temperature during the compliance test defined as either of the
    following:
     
    A) If compliance with the combustion chamber temperature limit is
    based on a hourly rolling average, the minimum temperature during
    the compliance test is considered to be the average over all runs of
    the lowest hourly rolling average for each run; or
     
    B) If compliance with the combustion chamber temperature limit is
    based on an instantaneous temperature measurement, the minimum
    temperature during the compliance test is considered to be the time-
    weighted average temperature during all runs of the test; and
     
    2) Operating parameters limited by the certification of compliance must
    continue to be monitored during the cutoff, and the hazardous waste feed
    must not be restarted until the levels of those parameters comply with the
    limits established in the certification of compliance.
     
    h) Fugitive emissions. Fugitive emissions must be controlled as follows:
     

     
    742
    1) By keeping the combustion zone totally sealed against fugitive emissions; or
     
    2) By maintaining the combustion zone pressure lower than atmospheric
    pressure; or
     
    3) By an alternative means of control that the owner or operator demonstrates
    provides fugitive emissions control equivalent to maintenance of combustion
    zone pressure lower than atmospheric pressure. Support for such
    demonstration must be included in the operating record.
     
    i) Changes. A BIF must cease burning hazardous waste when combustion properties,
    or feed rates of the hazardous waste, other fuels or industrial furnace feedstocks, or
    the BIF design or operating conditions deviate from the limits specified in the
    certification of compliance.
     
    j) Monitoring and Inspections.
     
    1) The owner or operator must monitor and record the following, at a minimum,
    while burning hazardous waste:
     
    A) Feed rates and composition of hazardous waste, other fuels, and
    industrial furnace feed stocks and feed rates of ash, metals, and total
    chlorine and chloride as necessary to ensure conformance with the
    certification of precompliance or certification of compliance;
     
    B) CO, oxygen, and, if applicable, HC on a continuous basis at a
    common point in the BIF downstream of the combustion zone and
    prior to release of stack gases to the atmosphere in accordance with
    the operating limits specified in the certification of compliance. CO,
    HC, and oxygen monitors must be installed, operated, and maintained
    in accordance with methods specified in Appendix I to this Part; and
     
    C) Upon the request of the Agency, sampling and analysis of the
    hazardous waste (and other fuels and industrial furnace feed stocks as
    appropriate) and the stack gas emissions must be conducted to verify
    that the operating conditions established in the certification of
    precompliance or certification of compliance achieve the applicable
    standards of Sections 726.204, 726.205, 726.206, and 726.207.
     
    2) The BIF and associated equipment (pumps, valves, pipes, fuel storage tanks,
    etc.) must be subjected to thorough visual inspection when they contain
    hazardous waste, at least daily for leaks, spills, fugitive emissions, and signs
    of tampering.
     
    3) The automatic hazardous waste feed cutoff system and associated alarms
    must be tested at least once every seven days when hazardous waste is

     
    743
    burned to verify operability, unless the owner or operator can demonstrate
    that weekly inspections will unduly restrict or upset operations and that less
    frequent inspections will be adequate. Support for such demonstration must
    be included in the operating record. At a minimum, operational testing must
    be conducted at least once every 30 days.
     
    4) These monitoring and inspection data must be recorded and the records must
    be placed in the operating log.
     
    k) Recordkeeping. The owner or operator must keep in the operating record of the
    facility all information and data required by this Section until closure of the BIF unit.
     
    l) Closure. At closure, the owner or operator must remove all hazardous waste and
    hazardous waste residues (including, but not limited to, ash, scrubber waters and
    scrubber sludges) from the BIF and must comply with 35 Ill. Adm. Code 725.211
    through 725.215.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.204 Standards to Control Organic Emissions
     
    a) DRE standard.
     
    1) General. Except as provided in subsection (a)(3) of this Section, a BIF
    burning hazardous waste must achieve a DRE of 99.99 percent for all
    organic hazardous constituents in the waste feed. To demonstrate
    conformance with this requirement, 99.99 percent DRE must be
    demonstrated during a trial burn for each principal organic hazardous
    constituent (POHC) designated (under subsection (a)(2) of this Section) in
    its permit for each waste feed. DRE is determined for each POHC from the
    following equation:
     
    DRE = 100
    (I - O)
    I
     
     
    Where:
     
    I = Mass feed rate of one POHC in the hazardous waste
    fired to the BIF; and
     
    O = Mass emission rate of the same POHC present in
    stack gas prior to release to the atmosphere.
     
    2) Designation of POHCs. POHCs are those compounds for which compliance
    with the DRE requirements of this Section must be demonstrated in a trial
    burn in conformance with procedures prescribed in 35 Ill. Adm. Code

     
    744
    703.232. One or more POHCs must be designated by the Agency for each
    waste feed to be burned. POHCs must be designated based on the degree of
    difficulty of destruction of the organic constituents in the waste and on their
    concentrations or mass in the waste feed considering the results of waste
    analyses submitted with Part B of the permit application. POHCs are most
    likely to be selected from among those compounds listed in Appendix H to
    35 Ill. Adm. Code 721 that are also present in the normal waste feed.
    However, if the applicant demonstrates to the Agency that a compound not
    listed in Appendix H to 35 Ill. Adm. Code 721 or not present in the normal
    waste feed is a suitable indicator of compliance with the DRE requirements
    of this Section, that compound must be designated as a POHC. Such
    POHCs need not be toxic or organic compounds.
     
    3) Dioxin-listed waste. A BIF burning hazardous waste containing (or derived
    from) USEPA Hazardous Wastes Nos. F020, F021, F022, F023, F026, or
    F027 must achieve a destruction and removal efficiency (DRE) of 99.9999
    percent for each POHC designated (under subsection (a)(2) of this Section)
    in its permit. This performance must be demonstrated on POHCs that are
    more difficult to burn than tetra-, penta-, and hexachlorodibenzo-p-dioxins
    and dibenzofurans. DRE is determined for each POHC from the equation in
    subsection (a)(1) of this Section. In addition, the owner or operator of the
    BIF must notify the Agency of intent to burn USEPA hazardous waste
    numbers F020, F021, F022, F023, F026, or F027.
     
    4) Automatic waiver of DRE trial burn. Owners and operators of boilers
    operated under the special operating requirements provided by Section
    726.210 are considered to be in compliance with the DRE standard of
    subsection (a)(1) of this Section and are exempt from the DRE trial burn.
     
    5) Low risk waste. Owners and operators of BIFs that burn hazardous waste in
    compliance with the requirements of Section 726.209(a) are considered to
    be in compliance with the DRE standard of subsection (a)(1) of this Section
    and are exempt from the DRE trial burn.
     
    b) CO standard.
     
    1) Except as provided in subsection (c) of this Section, the stack gas
    concentration of CO from a BIF burning hazardous waste cannot exceed
    100 ppmv on an hourly rolling average basis (i.e., over any 60 minute
    period), continuously corrected to seven percent oxygen, dry gas basis.
     
    2) CO and oxygen must be continuously monitored in conformance with
    “Performance Specifications for Continuous Emission Monitoring of
    Carbon Monoxide and Oxygen for Incinerators, Boilers, and Industrial
    Furnaces Burning Hazardous Waste” in Appendix I to this Part.
     

     
    745
    3) Compliance with the 100 ppmv CO limit must be demonstrated during the
    trial burn (for new facilities or an interim status facility applying for a
    permit) or the compliance test (for interim status facilities). To demonstrate
    compliance, the highest hourly rolling average CO level during any valid
    run of the trial burn or compliance test must not exceed 100 ppmv.
     
    c) Alternative CO standard.
     
    1) The stack gas concentration of CO from a BIF burning hazardous waste
    may exceed the 100 ppmv limit provided that stack gas concentrations of
    HCs do not exceed 20 ppmv, except as provided by subsection (f) of this
    Section for certain industrial furnaces.
     
    2) HC limits must be established under this Section on an hourly rolling
    average basis (i.e., over any 60 minute period), reported as propane, and
    continuously corrected to seven percent oxygen, dry gas basis.
     
    3) HC must be continuously monitored in conformance with “Performance
    Specifications for Continuous Emission Monitoring of Hydrocarbons for
    Incinerators, Boilers, and Industrial Furnaces Burning Hazardous Waste” in
    Appendix I to this Part. CO and oxygen must be continuously monitored in
    conformance with subsection (b)(2) of this Section.
     
    4) The alternative CO standard is established based on CO data during the trial
    burn (for a new facility) and the compliance test (for an interim status
    facility). The alternative CO standard is the average over all valid runs of
    the highest hourly average CO level for each run. The CO limit is
    implemented on an hourly rolling average basis, and continuously corrected
    to seven percent oxygen, dry gas basis.
     
    d) Special requirements for furnaces. Owners and operators of industrial furnaces
    (e.g., kilns, cupolas) that feed hazardous waste for a purpose other than solely as an
    ingredient (see Section 726.203(a)(5)(B)) at any location other than the end where
    products are normally discharged and where fuels are normally fired must comply
    with the HC limits provided by subsection (c) or (f) of this Section irrespective of
    whether stack gas CO concentrations meet the 100 ppmv limit of subsection (b) of
    this Section.
     
    e) Controls for dioxins and furans. Owners and operators of BIFs that are equipped
    with a dry PM control device that operates within the temperature range of 450º
    through 750° F, and industrial furnaces operating under an alternative HC limit
    established under subsection (f) of this Section must conduct a site-specific risk
    assessment as follows to demonstrate that emissions of chlorinated dibenzo-p-
    dioxins and dibenzofurans do not result in an increased lifetime cancer risk to the
    hypothetical maximum exposed individual (MEI) exceeding 1
    ×
    10
    -5
    (1 in 100,000):
     

     
    746
    1) During the trial burn (for new facilities or an interim status facility applying
    for a permit) or compliance test (for interim status facilities), determine
    emission rates of the tetra-octa congeners of chlorinated dibenzo-p-dioxins
    and dibenzofurans (CDDs/CDFs) using Method 0023A, “(Sampling
    Method for Polychlorinated Dibenzo-p-Dioxins and Polychlorinated
    Dibenzofurans Emissions from Stationary Sources,”) in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    Publication publication number EPA-530/SW-846, incorporated by
    reference in 35 Ill. Adm. Code 720.111 720.111(a);
     
    2) Estimate the 2,3,7,8-TCDD toxicity equivalence of the tetra-octa
    CDDs/CDFs congeners using “section 4.0 (Procedures for Estimating the
    Toxicity Equivalence of Chlorinated Dibenzo-p-Dioxin and Dibenzofuran
    Congeners”) in appendix IX to 40 CFR 266 (Methods Manual for
    Compliance with the BIF Regulations), incorporated by reference in 35 Ill.
    Adm. Code 720.111(b) (see Appendix I to this Part). Multiply the
    emission rates of CDD/CDF congeners with a toxicity equivalence greater
    than zero (see the procedure) by the calculated toxicity equivalence factor to
    estimate the equivalent emission rate of 2,3,7,8-TCDD;
     
    3) Conduct dispersion modeling using methods recommended in federal
    appendix W to 40 CFR 51, Appendix W, as incorporated by reference at
    35 Ill. Adm. Code 720.111 (“Guideline on Air Quality Models (Revised)”
    (1986) and its supplements), the “ in section 5.0 (Hazardous Waste
    Combustion Air Quality Screening Procedure,”) provided in Appendix I in
    appendix IX to 40 CFR 266 (Methods Manual for Compliance with the
    BIF Regulations), or in “Screening Procedures for Estimating Air Quality
    Impact of Stationary Sources, Revised,” (USEPA publication number EPA-
    454/R-92-019, each incorporated by reference in 35 Ill. Adm. Code
    720.111), to predict the maximum annual average off-site ground level
    concentration of 2,3,7,8-TCDD equivalents determined under subsection
    (e)(2) of this Section. The maximum annual average on-site concentration
    must be used when a person resides on-site; and
     
    4) The ratio of the predicted maximum annual average ground level
    concentration of 2,3,7,8-TCDD equivalents to the risk-specific dose (RSD)
    for 2,3,7,8-TCDD provided in Appendix E to this Part (2.2
    ×
    10
    -7
    ) must not
    exceed 1.0.
     
    f) Monitoring CO and HC in the by-pass duct of a cement kiln. Cement kilns may
    comply with the CO and HC limits provided by subsections (b), (c), and (d) of this
    Section by monitoring in the by-pass duct provided that the following conditions
    are fulfilled:
     
    1) Hazardous waste is fired only into the kiln and not at any location
    downstream from the kiln exit relative to the direction of gas flow; and

     
    747
     
    2) The by-pass duct diverts a minimum of 10 percent of kiln off-gas into the
    duct.
     
    g) Use of emissions test data to demonstrate compliance and establish operating
    limits. Compliance with the requirements of this Section must be demonstrated
    simultaneously by emissions testing or during separate runs under identical
    operating conditions. Further, data to demonstrate compliance with the CO and HC
    limits of this Section or to establish alternative CO or HC limits under this Section
    must be obtained during the time that DRE testing, and where applicable,
    CDD/CDF testing under subsection (e) of this Section and comprehensive organic
    emissions testing under subsection (f) of this Section is conducted.
     
    h) Enforcement. For the purposes of permit enforcement, compliance with the
    operating requirements specified in the permit (under Section 726.202) will be
    regarded as compliance with this Section. However, evidence that compliance with
    those permit conditions is insufficient to ensure compliance with the requirements
    of this Section is “information” justifying modification or revocation and re-
    issuance of a permit under 35 Ill. Adm. Code 703.270 et seq.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.205 Standards to Control PM
     
    a) A BIF burning hazardous waste must not emit PM in excess of 180 mg/dry standard
    m
    3
    (0.08 grains/dry standard cubic foot) after correction to a stack gas concentration
    of seven percent oxygen, using procedures prescribed in the following methods in
    appendix A to 40 CFR 60, Appendix A, methods 1 through 5 (Test Methods),
    each incorporated by reference in 35 Ill. Adm. Code 720.111, 720.111(b) and
    incorporated by reference in (see Appendix I of this Part): Method 1 (Sample and
    Velocity Traverses for Stationary Sources), Method 2 (Determination of Volatile
    Organic Compound Leaks), Method 2A (Direct Measurement of Gas Volume
    through Pipes and Small Ducts), Method 2B (Determination of Exhaust Gas
    Volume Flow Rate from Gasoline Vapor Incinerators), Method 2C (Determination
    of Gas Velocity and Volumetric Flow Rate in Small Stacks or Ducts (Standard
    Pitot Tube)), Method 2D (Measurement of Gas Volume Flow Rates in Small Pipes
    and Ducts), Method 2E (Determination of Landfill Gas Production Flow Rate),
    Method 2F (Determination of Stack Gas Velocity and Volumetric Flow Rate with
    Three-Dimensional Probes), Method 2G (Determination of Stack Gas Velocity
    and Volumetric Flow Rate with Two-Dimensional Probes), Method 2H
    (Determination of Stack Gas Velocity Taking into Account Velocity Decay Near
    the Stack Wall), Method 3 (Gas Analysis for the Determination of Dry Molecular
    Weight), Method 3A (Determination of Oxygen and Carbon Dioxide
    Concentrations in Emissions from Stationary Sources (Instrumental Analyzer
    Procedure)), Method 3B (Gas Analysis for the Determination of Emission Rate
    Correction Factor or Excess Air), Method 3C (Determination of Carbon Dioxide,

     
    748
    Methane, Nitrogen, and Oxygen from Stationary Sources), Method 4
    (Determination of Moisture Content in Stack Gases), Method 5 (Determination of
    Particulate Matter Emissions from Stationary Sources), Method 5A
    (Determination of Particulate Matter Emissions from the Asphalt Processing and
    Asphalt Roofing Industry), Method 5B (Determination of Nonsulfuric Acid
    Particulate Matter Emissions from Stationary Sources), Method 5D
    (Determination of Particulate Matter Emissions from Positive Pressure Fabric
    Filters), Method 5E (Determination of Particulate Matter Emissions from the
    Wool Fiberglass Insulation Manufacturing Industry), Method 5F (Determination
    of Nonsulfate Particulate Matter Emissions from Stationary Sources), Method 5G
    (Determination of Particulate Matter Emissions from Wood Heaters (Dilution
    Tunnel Sampling Location)), Method 5H (Determination of Particulate Emissions
    from Wood Heaters from a Stack Location), and Method 5I (Determination of
    Low Level Particulate Matter Emissions from Stationary Sources).
     
    b) An owner or operator meeting the requirements of Section 726.209(b) for the low
    risk waste exemption is exempt from the PM standard.
     
    c) Oxygen correction.
     
    1) Measured pollutant levels must be corrected for the amount of oxygen in
    the stack gas according to the following formula:
     
    ()
    Y
    -
    E
    14
    P
    P
    m
    c
    ×
    =
      
     
    Where:
     
    Pc is the corrected concentration of the pollutant in the stack
    gas,
     
    Pm is the measured concentration of the pollutant in the stack
    gas,
     
    E is the oxygen concentration on a dry basis in the
    combustion air fed to the device, and
     
    Y is the measured oxygen concentration on a dry basis in the
    stack.
     
    2) For devices that feed normal combustion air, E will equal 21 percent. For
    devices that feed oxygen-enriched air for combustion (that is, air with an
    oxygen concentration exceeding 21 percent), the value of E will be the
    concentration of oxygen in the enriched air.
     
    3) Compliance with all emission standards provided by this Subpart H must
    be based on correcting to seven percent oxygen using this procedure.

     
    749
     
    d) For the purposes of permit enforcement, compliance with the operating requirements
    specified in the permit (under Section 726.202) will be regarded as compliance with
    this Section. However, evidence that compliance with those permit conditions is
    insufficient to ensure compliance with the requirements of this Section is
    “information” justifying modification or revocation and re-issuance of a permit under
    35 Ill. Adm. Code 703.270 through 703.273.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.206 Standards to Control Metals Emissions
     
    a) General. The owner or operator must comply with the metals standards provided
    by subsections (b), (c), (d), (e), or (f) of this Section for each metal listed in
    subsection (b) of this Section that is present in the hazardous waste at detectable
    levels using appropriate analytical procedures specified in Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods, SW-846, incorporated by
    reference in 35 Ill. Adm. Code 720.111.
     
    b) Tier I feed rate screening limits. Feed rate screening limits for metals are
    specified in Appendix A to this Part as a function of terrain-adjusted effective
    stack height (TESH) and terrain and land use in the vicinity of the facility.
    Criteria for facilities that are not eligible to comply with the screening limits are
    provided in subsection (b)(7) of this Section.
     
    1) Noncarcinogenic metals. The feed rates of the noncarcinogenic metals in
    all feed streams, including hazardous waste, fuels, and industrial furnace
    feed stocks must not exceed the screening limits specified in Appendix A
    to this Part.
     
    A) The feed rate screening limits for antimony, barium, mercury,
    thallium, and silver are based on either of the following:
     
    i) An hourly rolling average, as defined in Sections
    726.200(g) and 726.202(e)(6)(A)(ii); or
     
    ii) An instantaneous limit not to be exceeded at any time.
     
    B) The feed rate screening limit for lead is based on one of the
    following:
     
    i) An hourly rolling average, as defined in Sections
    726.200(g) and 726.202(e)(6)(A)(ii);
     
    ii) An averaging period of 2 to 24 hours, as defined in Section
    726.202(e)(6)(B) with an instantaneous feed rate limit not

     
    750
    to exceed 10 times the feed rate that would be allowed on
    an hourly rolling average basis; or
     
    iii) An instantaneous limit not to be exceeded at any time.
     
    2) Carcinogenic metals.
     
    A) The feed rates of carcinogenic metals in all feed streams, including
    hazardous waste, fuels, and industrial furnace feed stocks must not
    exceed values derived from the screening limits specified in
    Appendix A to this Part. The feed rate of each of these metals is
    limited to a level such that the sum of the ratios of the actual feed
    rate to the feed rate screening limit specified in Appendix A to this
    Part must not exceed 1.0, as provided by the following equation:
     
    i=1
    n
    i
    i
    A
    F
    1.0
      
     
    Where:
     
    Σ
    Ai/Fi means the sum of the values of A/F for each
    metal “i,” from i = 1 to n.
     
    n = number of carcinogenic metals.
     
    Ai = the actual feed rate to the device for metal
    “i.”
     
    Fi = the feed rate screening limit provided by
    Appendix A to this Part for metal “i.”
     
    B) The feed rate screening limits for the carcinogenic metals are
    based on either:
     
    i) An hourly rolling average; or
     
    ii) An averaging period of two to 24 hours, as defined in
    Section 726.202(e)(6)(B), with an instantaneous feed rate
    limit not to exceed 10 times the feed rate that would be
    allowed on an hourly rolling average basis.
     
    3) TESH (terrain adjusted effective stack height).
     
    A) The TESH is determined according to the following equation:
     

     
    751
    TESH = H + P - T
     
    Where:
     
    H = Actual physical stack height (m).
     
    P = Plume rise (in m) as determined from
    Appendix F to this Part as a function of
    stack flow rate and stack gas exhaust
    temperature.
     
    T = Terrain rise (in m) within five kilometers of
    the stack.
     
    B) The stack height (H) must not exceed good engineering practice
    stack height, as defined in Section 726.200(i).
     
    C) If the TESH calculated pursuant to subsection (b)(3)(A) of this
    Section is not listed in Appendix A through Appendix C to this
    Part, the values for the nearest lower TESH listed in the table must
    be used. If the TESH is four meters or less, a value based on four
    meters must be used.
     
    4) Terrain type. The screening limits are a function of whether the facility is
    located in noncomplex or complex terrain. A device located where any
    part of the surrounding terrain within five kilometers of the stack equals or
    exceeds the elevation of the physical stack height (H) is considered to be
    in complex terrain and the screening limits for complex terrain apply.
    Terrain measurements are to be made from U.S. Geological Survey 7.5-
    minute topographic maps of the area surrounding the facility.
     
    5) Land use. The screening limits are a function of whether the facility is
    located in an area where the land use is urban or rural. To determine
    whether land use in the vicinity of the facility is urban or rural, procedures
    provided in Appendix I or Appendix J to this Part must be used.
     
    6) Multiple stacks. An owners or operator of a facility with more than one
    on-site stack from a BIF, incinerator, or other thermal treatment unit
    subject to controls of metals emissions under a RCRA permit or interim
    status controls must comply with the screening limits for all such units
    assuming all hazardous waste is fed into the device with the worst-case
    stack based on dispersion characteristics. The stack with the lowest value
    of K is the worst-case stack. K is determined from the following equation
    as applied to each stack:
     
    K = H
    ×
    V
    ×
    T

     
    752
     
    Where:
     
    K = a parameter accounting for relative influence of
    stack height and plume rise;
     
    H = physical stack height (meters);
     
    V = stack gas flow rate (m
    3
    /sec (cubic meters per
    second); and
     
    T = exhaust temperature (degrees K).
     
    7) Criteria for facilities not eligible for screening limits. If any criteria below
    are met, the Tier I (and Tier II) screening limits do not apply. Owners and
    operators of such facilities must comply with either the Tier III standards
    provided by subsection (d) of this Section or with the adjusted Tier I feed
    rate screening limits provided by subsection (e) of this Section.
     
    A) The device is located in a narrow valley less than one kilometer
    wide;
     
    B) The device has a stack taller than 20 meters and is located such
    that the terrain rises to the physical height within one kilometer of
    the facility;
     
    C) The device has a stack taller than 20 meters and is located within
    five kilometers of a shoreline of a large body of water such as an
    ocean or large lake; or
     
    D) The physical stack height of any stack is less than 2.5 times the
    height of any building within five building heights or five
    projected building widths of the stack and the distance from the
    stack to the closest boundary is within five building heights or five
    projected building widths of the associated building.
     
    8) Implementation. The feed rate of metals in each feedstream must be
    monitored to ensure that the feed rate screening limits are not exceeded.
     
    c) Tier II emission rate screening limits. Emission rate screening limits are specified
    in Appendix A to this Part as a function of TESH and terrain and land use in the
    vicinity of the facility. Criteria for facilities that are not eligible to comply with
    the screening limits are provided in subsection (b)(7) of this Section.
     
    1) Noncarcinogenic metals. The emission rates of noncarcinogenic metals
    must not exceed the screening limits specified in Appendix A to this Part.

     
    753
     
    2) Carcinogenic metals. The emission rates of carcinogenic metals must not
    exceed values derived from the screening limits specified in Appendix A
    to this Part. The emission rate of each of these metals is limited to a level
    such that the sum of the ratios of the actual emission rate to the emission
    rate screening limit specified in Appendix A to this Part must not exceed
    1.0, as provided by the following equation:
     
    1.0
    E
    A
    i
    i
    n
    1
    =
    i
      
     
    Where:
     
    Σ
    Ai/Ei means the sum of the values of A/E for each metal
    “i,” from i = 1 to n.
     
    n = number of carcinogenic metals.
     
    Ai = the actual emission rate to the device for metal “i.”
     
    Ei = the emission rate screening limit provided by
    Appendix A to this Part for metal “i.”
     
    3) Implementation. The emission rate limits must be implemented by
    limiting feed rates of the individual metals to levels during the trial burn
    (for new facilities or an interim status facility applying for a permit) or the
    compliance test (for interim status facilities). The feed rate averaging
    periods are the same as provided by subsections (b)(1)(A), (b)(1)(B), and
    (b)(2)(B) of this Section. The feed rate of metals in each feedstream must
    be monitored to ensure that the feed rate limits for the feedstreams
    specified under Sections 726.202 or 726.203 are not exceeded.
     
    4) Definitions and limitations. The definitions and limitations provided by
    subsection (b) of this Section and 726.200(g) for the following terms also
    apply to the Tier II emission rate screening limits provided by this
    subsection (c): TESH, good engineering practice stack height, terrain
    type, land use, and criteria for facilities not eligible to use the screening
    limits.
     
    5) Multiple stacks.
     
    A) An owner or operator of a facility with more than one on-site stack
    from a BIF, incinerator, or other thermal treatment unit subject to
    controls on metals emissions under a RCRA permit or interim
    status controls must comply with the emissions screening limits for

     
    754
    any such stacks assuming all hazardous waste is fed into the device
    with the worst-case stack based on dispersion characteristics.
     
    B) The worst-case stack is determined by procedures provided in
    subsection (b)(6) of this Section.
     
    C) For each metal, the total emissions of the metal from those stacks
    must not exceed the screening limit for the worst-case stack.
     
    d) Tier III site-specific risk assessment. The requirements of this subsection (d)
    apply to facilities complying with either the Tier III or Adjusted Tier I except
    where specified otherwise.
     
    1) General. Conformance with the Tier III metals controls must be
    demonstrated by emissions testing to determine the emission rate for each
    metal. In addition, conformance with either Tier III or Adjusted Tier I
    metals controls must be demonstrated by air dispersion modeling to
    predict the maximum annual average off-site ground level concentration
    for each metal and a demonstration that acceptable ambient levels are not
    exceeded.
     
    2) Acceptable ambient levels. Appendix D and Appendix E to this Part list
    the acceptable ambient levels for purposes of this Subpart H. Reference
    air concentrations (RACs) are listed for the noncarcinogenic metals and
    1
    ×
    10
    -5
    RSDs are listed for the carcinogenic metals. The RSD for a metal
    is the acceptable ambient level for that metal provided that only one of the
    four carcinogenic metals is emitted. If more than one carcinogenic metal
    is emitted, the acceptable ambient level for the carcinogenic metals is a
    fraction of the RSD, as described in subsection (d)(3) of this Section.
     
    3) Carcinogenic metals. For the carcinogenic metals the sum of the ratios of
    the predicted maximum annual average off-site ground level
    concentrations (except that on-site concentrations must be considered if a
    person resides on site) to the RSD for all carcinogenic metals emitted must
    not exceed 1.0 as determined by the following equation:
     
    i=1
    n
    i
    i
    P
    R
    1.0
      
     
    Where:
     
    Σ
    Pi/Ri means the sum of the values of P/R for each metal “i,”
    from i = 1 to n.
     
    n = number of carcinogenic metals.

     
    755
     
    Pi = the predicted ambient concentration for metal i.
     
    Ri = the RSD for metal i.
     
    4) Noncarcinogenic metals. For the noncarcinogenic metals, the predicted
    maximum annual average off-site ground level concentration for each
    metal must not exceed the RAC.
     
    5) Multiple stacks. Owners and operators of facilities with more than one
    on-site stack from a BIF, incinerator, or other thermal treatment unit
    subject to controls on metals emissions under a RCRA permit or interim
    status controls must conduct emissions testing (except that facilities
    complying with Adjusted Tier I controls need not conduct emissions
    testing) and dispersion modeling to demonstrate that the aggregate
    emissions from all such on-site stacks do not result in an exceedence of
    the acceptable ambient levels.
     
    6) Implementation. Under Tier III, the metals controls must be implemented
    by limiting feed rates of the individual metals to levels during the trial
    burn (for new facilities or an interim status facility applying for a permit)
    or the compliance test (for interim status facilities). The feed rate
    averaging periods are the same as provided by subsections (b)(1)(A),
    (b)(1)(B), and (b)(2)(B) of this Section. The feed rate of metals in each
    feedstream must be monitored to ensure that the feed rate limits for the
    feedstreams specified under Sections 726.202 or 726.203 are not
    exceeded.
     
    e) Adjusted Tier I feed rate screening limits. The owner or operator may adjust the
    feed rate screening limits provided by Appendix A to this Part to account for site-
    specific dispersion modeling. Under this approach, the adjusted feed rate
    screening limit for a metal is determined by back-calculating from the acceptable
    ambient levels provided by Appendix D and Appendix E to this Part using
    dispersion modeling to determine the maximum allowable emission rate. This
    emission rate becomes the adjusted Tier I feed rate screening limit. The feed rate
    screening limits for carcinogenic metals are implemented as prescribed in
    subsection (b)(2) of this Section.
     
    f) Alternative implementation approaches.
     
    1) Pursuant to subsection (f)(2) of this Section the Agency must approve on a
    case-by-case basis approaches to implement the Tier II or Tier III metals
    emission limits provided by subsection (c) or (d) of this Section alternative
    to monitoring the feed rate of metals in each feedstream.
     
    2) The emission limits provided by subsection (d) of this Section must be

     
    756
    determined as follows:
     
    A) For each noncarcinogenic metal, by back-calculating from the
    RAC provided in Appendix D to this Part to determine the
    allowable emission rate for each metal using the dilution factor for
    the maximum annual average ground level concentration predicted
    by dispersion modeling in conformance with subsection (h) of this
    Section; and
     
    B) For each carcinogenic metal by the following methods:
     
    i) By back-calculating from the RSD provided in Appendix E
    to this Part to determine the allowable emission rate for
    each metal if that metal were the only carcinogenic metal
    emitted using the dilution factor for the maximum annual
    average ground level concentration predicted by dispersion
    modeling in conformance with subsection (h) of this
    Section; and
     
    ii) If more than one carcinogenic metal is emitted, by selecting
    an emission limit for each carcinogenic metal not to exceed
    the emission rate determined by subsection (f)(2)(B)(i) of
    this Section, such that the sum for all carcinogenic metals
    of the ratios of the selected emission limit to the emission
    rate determined by that subsection does not exceed 1.0.
     
    g) Emission testing.
     
    1) General. Emission testing for metals must be conducted using Method
    0060, “(Determinations of Metals in Stack Emissions,”) in “Test Methods
    for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    Publication publication number EPA-530/SW-846, incorporated by
    reference in 35 Ill. Adm. Code 720.111 720.111(a).
     
    2) Hexavalent chromium. Emissions of chromium are assumed to be
    hexavalent chromium unless the owner or operator conducts emissions
    testing to determine hexavalent chromium emissions using procedures
    prescribed in Method 0061, “(Determination of Hexavalent Chromium
    Emissions from Stationary Sources,”) in “Test Methods for Evaluating
    Solid Waste, Physical/Chemical Methods,” USEPA Publication
    publication number EPA-530/SW-846, incorporated by reference in 35 Ill.
    Adm. Code 720.111 720.111(a).
     
    h) Dispersion modeling. Dispersion modeling required under this Section must be
    conducted according to methods recommended in federal appendix W to 40 CFR
    51, appendix W (“Guideline on Air Quality Models (Revised)” (1986) and its

     
    757
    supplements), the “ in section 5.0 (Hazardous Waste Combustion Air Quality
    Screening Procedure,”) described in Appendix I to this Part in appendix IX to 40
    CFR 266 (Methods Manual for Compliance with the BIF Regulations), or in
    “Screening Procedures for Estimating the Air Quality Impact of Stationary
    Sources, Revised,” (USEPA publication number EPA-454/R-92-019, each
    incorporated by reference in 35 Ill. Adm. Code 720.111), to predict the maximum
    annual average off-site ground level concentration. However, on-site
    concentrations must be considered when a person resides on-site.
     
    i) Enforcement. For the purposes of permit enforcement, compliance with the
    operating requirements specified in the permit (under Section 726.202) will be
    regarded as compliance with this Section. However, evidence that compliance
    with those permit conditions is insufficient to ensure compliance with the
    requirements of this Section is “information” justifying modification or
    revocation and re-issuance of a permit under 35 Ill. Adm. Code 703.270 through
    703.273.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.207 Standards to Control HCl and Chlorine Gas Emissions
     
    a) General. The owner or operator must comply with the HCl and chlorine gas controls
    provided by subsection (b), (c), or (e) of this Section.
     
    b) Screening limits.
     
    1) Tier I feed rate screening limits. Feed rate screening limits are specified for
    total chlorine in Appendix B to this Part as a function of TESH and terrain
    and land use in the vicinity of the facility. The feed rate of total chlorine and
    chloride, both organic and inorganic, in all feed streams, including hazardous
    waste, fuels, and industrial furnace feed stocks must not exceed the levels
    specified.
     
    2) Tier II emission rate screening limits. Emission rate screening limits for HCl
    and chlorine gas are specified in Appendix C to this Part as a function of
    TESH and terrain and land use in the vicinity of the facility. The stack
    emission rates of HCl and chlorine gas must not exceed the levels specified.
     
    3) Definitions and limitations. The definitions and limitations provided by
    Sections 726.200(i) and 726.206(b) for the following terms also apply to the
    screening limits provided by this subsection: TESH, good engineering
    practice stack height, terrain type, land use, and criteria for facilities not
    eligible to use the screening limits.
     
    4) Multiple stacks. Owners and operators of facilities with more than one on-
    site stack from a BIF, incinerator or other thermal treatment unit subject to

     
    758
    controls on HCl or chlorine gas emissions under a RCRA permit or interim
    status controls must comply with the Tier I and Tier II screening limits for
    those stacks assuming all hazardous waste is fed into the device with the
    worst-case stack based on dispersion characteristics.
     
    A) The worst-case stack is determined by procedures provided in
    Section 726.206(b)(6).
     
    B) Under Tier I, the total feed rate of chlorine and chloride to all subject
    devices must not exceed the screening limit for the worst-case stack.
     
    C) Under Tier II, the total emissions of HCl and chlorine gas from all
    subject stacks must not exceed the screening limit for the worst-case
    stack.
     
    c) Tier III site-specific risk assessments.
     
    1) General. Conformance with the Tier III controls must be demonstrated by
    emissions testing to determine the emission rate for HCl and chlorine gas, air
    dispersion modeling to predict the maximum annual average off-site ground
    level concentration for each compound, and a demonstration that acceptable
    ambient levels are not exceeded.
     
    2) Acceptable ambient levels. Appendix D to this Part lists the RACs for HCl
    (7 ug/m
    3
    ) and chlorine gas (0.4 ug/m
    3
    ).
     
    3) Multiple stacks. Owners and operators of facilities with more than one on-
    site stack from a BIF, incinerator, or other thermal treatment unit subject to
    controls on HCl or chlorine gas emissions under a RCRA permit or interim
    status controls must conduct emissions testing and dispersion modeling to
    demonstrate that the aggregate emissions from all such on-site stacks do not
    result in an exceedence of the acceptable ambient levels for HCl and chlorine
    gas.
     
    d) Averaging periods. The HCl and chlorine gas controls are implemented by limiting
    the feed rate of total chlorine and chloride in all feedstreams, including hazardous
    waste, fuels, and industrial furnace feed stocks. Under Tier I, the feed rate of total
    chlorine and chloride is limited to the Tier I Screening Limits. Under Tier II and
    Tier III, the feed rate of total chlorine and chloride is limited to the feed rates during
    the trial burn (for new facilities or an interim status facility applying for a permit) or
    the compliance test (for interim status facilities). The feed rate limits are based on
    either of the following:
     
    1) An hourly rolling average, as defined in Sections 726.200(i) and
    726.202(e)(6); or
     

     
    759
    2) An instantaneous basis not to be exceeded at any time.
     
    e) Adjusted Tier I feed rate screening limits. The owner or operator may adjust the feed
    rate screening limit provided by Appendix B to this Part to account for site-specific
    dispersion modeling. Under this approach, the adjusted feed rate screening limit is
    determined by back-calculating from the acceptable ambient level for chlorine gas
    provided by Appendix D to this Part using dispersion modeling to determine the
    maximum allowable emission rate. This emission rate becomes the adjusted Tier I
    feed rate screening limit.
     
    f) Emissions testing. Emissions testing for HCl and chlorine gas (Cl2) must be
    conducted using the procedures described in Method 0050 or 0051, in “Test
    Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    Publication publication number EPA-530/SW-846, incorporated by reference in
    35 Ill. Adm. Code 720.111 720.111(a).
     
    g) Dispersion modeling. Dispersion modeling must be conducted according to the
    provisions of Section 726.206(h).
     
    h) Enforcement. For the purposes of permit enforcement, compliance with the
    operating requirements specified in the permit (under Section 726.202) will be
    regarded as compliance with this Section. However, evidence that compliance with
    those permit conditions is insufficient to ensure compliance with the requirements of
    this Section is “information” justifying modification or revocation and re-issuance of
    a permit under 35 Ill. Adm. Code 703.270 through 703.273.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.211 Standards for Direct Transfer
     
    a) Applicability. The regulations in this Section apply to owners and operators of BIFs
    subject to Section 726.202 or 726.203 if hazardous waste is directly transferred from
    a transport vehicle to a BIF without the use of a storage unit.
     
    b) Definitions.
     
    1) When used in this Section, terms have the following meanings:
     
    “Direct transfer equipment” means any device (including but not
    limited to, such devices as piping, fittings, flanges, valves and pumps)
    that is used to distribute, meter or control the flow of hazardous waste
    between a container (i.e., transport vehicle) and a BIF.
     
    “Container” means any portable device in which hazardous waste is
    transported, stored, treated, or otherwise handled, and includes
    transport vehicles that are containers themselves (e.g., tank trucks,

     
    760
    tanker-trailers, and rail tank cars) and containers placed on or in a
    transport vehicle.
     
    2) This Section references several requirements provided in Subparts I and J of
    35 Ill. Adm. Code 724 and Subparts I and J of 35 Ill. Adm. Code 725. For
    purposes of this Section, the term “tank systems” in those referenced
    requirements means direct transfer equipment, as defined in subsection (b)(1)
    of this Section.
     
    c) General operating requirements.
     
    1) No direct transfer of a pumpable hazardous waste must be conducted from an
    open-top container to a BIF.
     
    2) Direct transfer equipment used for pumpable hazardous waste must always
    be closed, except when necessary to add or remove the waste, and must not
    be opened, handled, or stored in a manner that could cause any rupture or
    leak.
     
    3) The direct transfer of hazardous waste to a BIF must be conducted so that it
    does not do any of the following:
     
    A) Generate extreme heat or pressure, fire, explosion, or violent
    reaction;
     
    B) Produce uncontrolled toxic mists, fumes, dusts, or gases in sufficient
    quantities to threaten human health;
     
    C) Produce uncontrolled flammable fumes or gases in sufficient
    quantities to pose a risk of fire or explosions;
     
    D) Damage the structural integrity of the container or direct transfer
    equipment containing the waste;
     
    E) Adversely affect the capability of the BIF to meet the standards
    provided by Sections 726.204 through 726.207; or
     
    F) Threaten human health or the environment.
     
    4) Hazardous waste must not be placed in direct transfer equipment, if it could
    cause the equipment or its secondary containment system to rupture, leak,
    corrode, or otherwise fail.
     
    5) The owner or operator of the facility must use appropriate controls and
    practices to prevent spills and overflows from the direct transfer equipment
    or its secondary containment systems. These include the following at a

     
    761
    minimum:
     
    A) Spill prevention controls (e.g., check valves, dry discount couplings,
    etc.); and
     
    B) Automatic waste feed cutoff to use if a leak or spill occurs from the
    direct transfer equipment.
     
    d) Areas where direct transfer vehicles (containers) are located. Applying the definition
    of container under this Section, owners and operators must comply with the
    following requirements:
     
    1) The containment requirements of 35 Ill. Adm. Code 724.275;
     
    2) The use and management requirements of Subpart I of 35 Ill. Adm. Code
    725, except for Sections 725.270 and 725.274, and except that in lieu of the
    special requirements of 35 Ill. Adm. Code 725.276 for ignitable or reactive
    waste, the owner or operator may comply with the requirements for the
    maintenance of protective distances between the waste management area and
    any public ways, streets, alleys, or an adjacent property line that can be built
    upon, as required in Tables 2-1 through 2-6 of “Flammable and
    Combustible Liquids Code,” NFPA 30, (incorporated by reference in 35 Ill.
    Adm. Code 720.111) 720.111(a). The owner or operator must obtain and
    keep on file at the facility a written certification by the local Fire Marshal that
    the installation meets the subject NFPA Codes; and
     
    3) The closure requirements of 35 Ill. Adm. Code 724.278.
     
    e) Direct transfer equipment. Direct transfer equipment must meet the following
    requirements:
     
    1) Secondary containment. Owners and operators must comply with the
    secondary containment requirements of 35 Ill. Adm. Code 725.293, except
    for Sections 725.293(a), (d), (e), and (i), as follows:
     
    A) For all new direct transfer equipment, prior to their being put into
    service; and
     
    B) For existing direct transfer equipment, by August 21, 1993.
     
    2) Requirements prior to meeting secondary containment requirements.
     
    A) For existing direct transfer equipment that does not have secondary
    containment, the owner or operator must determine whether the
    equipment is leaking or is unfit for use. The owner or operator must
    obtain and keep on file at the facility a written assessment reviewed

     
    762
    and certified by a qualified, registered professional engineer in
    accordance with 35 Ill. Adm. Code 703.126(d) that attests to the
    equipment’s integrity by August 21, 1992.
     
    B) This assessment must determine whether the direct transfer
    equipment is adequately designed and has sufficient structural
    strength and compatibility with the wastes to be transferred to ensure
    that it will not collapse, rupture, or fail. At a minimum, this
    assessment must consider the following:
     
    i) Design standards, if available, according to which the direct
    transfer equipment was constructed;
     
    ii) Hazardous characteristics of the wastes that have been or will
    be handled;
     
    iii) Existing corrosion protection measures;
     
    iv) Documented age of the equipment, if available, (otherwise,
    an estimate of the age); and
     
    v) Results of a leak test or other integrity examination such that
    the effects of temperature variations, vapor pockets, cracks,
    leaks, corrosion and erosion are accounted for.
     
    C) If, as a result of the assessment specified above, the direct transfer
    equipment is found to be leaking or unfit for use, the owner or
    operator must comply with the requirements of 35 Ill. Adm. Code
    725.296(a) and (b).
     
    3) Inspections and recordkeeping.
     
    A) The owner or operator must inspect at least once each operating hour
    when hazardous waste is being transferred from the transport vehicle
    (container) to the BIF:
     
    i) Overfill/spill control equipment (e.g., waste-feed cutoff
    systems, bypass systems, and drainage systems) to ensure that
    it is in good working order;
     
    ii) The above ground portions of the direct transfer equipment to
    detect corrosion, erosion, or releases of waste (e.g., wet spots,
    dead vegetation, etc.); and
     
    iii) Data gathered from monitoring equipment and leak-detection
    equipment, (e.g., pressure and temperature gauges) to ensure

     
    763
    that the direct transfer equipment is being operated according
    to its design.
     
    B) The owner or operator must inspect cathodic protection systems, if
    used, to ensure that they are functioning properly according to the
    schedule provided by 35 Ill. Adm. Code 725.295(b).
     
    C) Records of inspections made under this subsection must be
    maintained in the operating record at the facility, and available for
    inspection for at least three years from the date of the inspection.
     
    4) Design and installation of new ancillary equipment. Owners and operators
    must comply with the requirements of 35 Ill. Adm. Code 725.292.
     
    5) Response to leaks or spills. Owners and operators must comply with the
    requirements of 35 Ill. Adm. Code 725.296.
     
    6) Closure. Owners and operators must comply with the requirements of 35 Ill.
    Adm. Code 725.297, except for 35 Ill. Adm. Code 725.297(c)(2) through
    (c)(4).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.212 Regulation of Residues
     
    A residue derived from the burning or processing of hazardous waste in a BIF is not excluded from
    the definition of a hazardous waste under 35 Ill. Adm. Code 721.104(b)(4), (b)(7), or (b)(8), unless
    the device and the owner or operator meet the following requirements:
     
    a) The device meets the following criteria:
     
    1) Boilers. Boilers must burn at least 50 percent coal on a total heat input or
    mass basis, whichever results in the greater mass feed rate of coal;
     
    2) Ore or mineral furnaces. Industrial furnaces subject to 35 Ill. Adm. Code
    721.104(b)(7) must process at least 50 percent by weight of normal,
    nonhazardous raw materials;
     
    3) Cement kilns. Cement kilns must process at least 50 percent by weight of
    normal cement-production raw materials;
     
    b) The owner or operator demonstrates that the hazardous waste does not significantly
    affect the residue by demonstrating conformance with either of the following criteria:
     
    1) Comparison of waste-derived residue with normal residue. The waste-
    derived residue must not contain constituents listed in Appendix H to 35 Ill.

     
    764
    Adm. Code 721 constituents (toxic constituents) that could reasonably be
    attributable to the hazardous waste at concentrations significantly higher than
    in residue generated without burning or processing of hazardous waste, using
    the following procedure. Toxic compounds that could reasonably be
    attributable to burning or processing the hazardous waste (constituents of
    concern) include toxic constituents in the hazardous waste, and the organic
    compounds listed in Appendix H to 35 Ill. Adm. Code 721 that may be PICs.
    Sampling and analyses must be in conformance with procedures prescribed
    in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”
    USEPA Publication SW-846, incorporated by reference in 35 Ill. Adm. Code
    720.111(a). For polychlorinated dibenzo-p-dioxins and polychlorinated
    dibenzo-furans, analyses must be performed to determine specific
    congeners and homologues, and the results converted to 2,3,7,8-TCDD
    equivalent values using the procedure specified in section 4.0 of the
    documents referenced in Appendix I of this Part.
     
    A) Normal residue. Concentrations of toxic constituents of concern in
    normal residue must be determined based on analyses of a minimum
    of 10 samples representing a minimum of 10 days of operation.
    Composite samples may be used to develop a sample for analysis
    provided that the compositing period does not exceed 24 hours. The
    upper tolerance limit (at 95 percent confidence with a 95 percent
    proportion of the sample distribution) of the concentration in the
    normal residue must be considered the statistically-derived
    concentration in the normal residue. If changes in raw materials or
    fuels reduce the statistically-derived concentrations of the toxic
    constituents of concern in the normal residue, the statistically-derived
    concentrations must be revised or statistically-derived concentrations
    of toxic constituents in normal residue must be established for a new
    mode of operation with the new raw material or fuel. To determine
    the upper tolerance limit in the normal residue, the owner or operator
    must use statistical procedures prescribed in “section 7.0 (Statistical
    Methodology for Bevill Residue Determinations,” ) in federal
    appendix IX to 40 CFR 266 (Methods Manual for Compliance
    with the BIF Regulations), USEPA publication number EPA-
    454/R-92-019, incorporated by reference in 35 Ill. Adm. Code
    720.111(b) (see Appendix I of this Part).
     
    B) Waste-derived residue. Waste derived residue must be sampled and
    analyzed as often as necessary to determine whether the residue
    generated during each 24-hour period has concentrations of toxic
    constituents that are higher than the concentrations established for the
    normal residue under subsection (b)(1)(A) of this Section. If so,
    hazardous waste burning has significantly affected the residue and
    the residue is not excluded from the definition of “hazardous waste.”
    Concentrations of toxic constituents in waste-derived residue must be

     
    765
    determined based on analysis of one or more samples obtained over a
    24-hour period. Multiple samples may be analyzed, and multiple
    samples may be taken to form a composite sample for analysis
    provided that the sampling period does not exceed 24 hours. If more
    than one sample is analyzed to characterize waste-derived residues
    generated over a 24-hour period, the concentration of each toxic
    constituent must be the arithmetic mean of the concentrations in the
    samples. No results can be disregarded; or
     
    2) Comparison of waste-derived residue concentrations with health-based
    limits.
     
    A) Nonmetal constituents. The concentration of each nonmetal toxic
    constituent of concern (specified in subsection (b)(1) of this Section)
    in the waste-derived residue must not exceed the health-based level
    specified in Appendix G of this Part, or the level of detection (using
    analytical procedures prescribed in “Test Methods for Evaluating
    Solid Waste, Physical/Chemical Methods,” USEPA Publication SW-
    846, incorporated by reference in 35 Ill. Adm. Code 720.111),
    whichever is higher. If a health-based limit for a constituent of
    concern is not listed in Appendix G of this Part, then a limit of 0.002
    mg/kg or the level of detection (using appropriate analytical
    procedures prescribed in “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods,” USEPA Publication SW-846,
    incorporated by reference in 35 Ill. Adm. Code 720.111), whichever
    is higher, must be used. The levels specified in Appendix G of this
    Part (and the default level of 0.002 mg/kg or the level of detection for
    constituents, as identified in Note 1 of Appendix G of this Part) are
    administratively stayed under the condition, for those constituents
    specified in subsection (b)(1) of this Section, that the owner or
    operator complies with alternative levels defined as the land disposal
    restriction limits specified in 35 Ill. Adm. Code 728.143 and Table B
    to 35 Ill. Adm. Code 728 for F039 nonwastewaters. In complying
    with those alternative levels, if an owner or operator is unable to
    detect a constituent despite documenting use of the best good-faith
    efforts, as defined by applicable USEPA guidance and standards, the
    owner or operator is deemed to be in compliance for that constituent.
    Until USEPA develops new guidance or standards, the owner or
    operator may demonstrate such good-faith efforts by achieving a
    detection limit for the constituent that does not exceed an order of
    magnitude above (ten times) the level provided by 35 Ill. Adm. Code
    728.143 and Table B to 35 Ill. Adm. Code 728 for F039
    nonwastewater levels for polychlorinated dibenzo-p-dioxins and
    polychlorinated dibenzo-furans (D/F), analyses must be performed
    for total hexachlorodibenzo-p-dioxins, total
    hexachlorodibenzofurans, total pentachlorodibenzo-p-dioxins, total

     
    766
    pentachlorodibenzofurans, total tetrachlorodibenzo-p-dioxins, and
    total tetrachlorodibenzofurans;
     
    BOARD NOTE: In a note to corresponding 40 CFR 266.112(b)(2)(i)
    (2002), USEPA stated as follows:
     
    The administrative stay, under the condition that the
    owner or operator complies with alternative levels
    defined as the land disposal restriction limits
    specified in 35 Ill. Adm. Code 728.143 for F039
    nonwastewaters, remains in effect until further
    administrative action is taken and notice is
    published in the Federal Register and the Code of
    Federal Regulations.
     
    Under Section 3006(b) and (g) of RCRA, 42 USC 6926(b) and (g),
    federal amendments do not go into effect in Illinois until the State of
    Illinois incorporates them into the State program. This applies unless
    the authority under which USEPA adopted the amendments is the
    Hazardous and Solid Waste Amendments of 1984 (HSWA), in which
    case the federal amendments become effective in Illinois on their
    federal effective date.
     
    B) Metal constituents. The concentration of metals in an extract
    obtained using the TCLP test must not exceed the levels specified in
    Appendix G of this Part;
     
    C) Sampling and analysis. Wastewater-derived residue must be sampled
    and analyzed as often as necessary to determine whether the residue
    generated during each 24-hour period has concentrations of toxic
    constituents that are higher than the health-based levels.
    Concentrations of concern in the wastewater-derived residue must be
    determined based on analysis of one or more samples obtained over a
    24-hour period. Multiple samples may be analyzed, and multiple
    samples may be taken to form a composite for analysis provided that
    the sampling period does not exceed 24 hours. If more than one
    sample is analyzed to characterize waste-derived residues generated
    over a 24-hour period, the concentration of each toxic constituent is
    the arithmetic mean of the concentrations of the samples. No results
    can be disregarded; and
     
    c) Records sufficient to document compliance with the provisions of this Section must
    be retained until closure of the BIF unit. At a minimum, the following must be
    recorded:
     
    1) Levels of constituents in Appendix H to 35 Ill. Adm. Code 721 that are

     
    767
    present in waste-derived residues;
     
    2) If the waste-derived residue is compared with normal residue under
    subsection (b)(1) of this Section:
     
    A) The levels of constituents in Appendix H to 35 Ill. Adm. Code 721
    that are present in normal residues; and
     
    B) Data and information, including analyses of samples as necessary,
    obtained to determine if changes in raw materials or fuels would
    reduce the concentration of toxic constituents of concern in the
    normal residue.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART M: MILITARY MUNITIONS
     
    Section 726.303 Standards Applicable to the Transportation of Solid Waste Military
    Munitions
     
    a) Criteria for hazardous waste regulation of waste non-chemical military munitions
    in transportation.
     
    1) Waste military munitions that are being transported and which exhibit a
    hazardous waste characteristic or which are listed as hazardous waste
    under 35 Ill. Adm. Code 721 are subject to regulation under 35 Ill. Adm.
    Code 702, 703, 705, 720 through 726, and 728, unless the munitions meet
    all the following conditions:
     
    A) The waste military munitions are not chemical agents or chemical
    munitions;
     
    B) The waste military munitions are transported in accordance with
    the Department of Defense shipping controls applicable to the
    transport of military munitions;
     
    C) The waste military munitions are transported from a military-
    owned or -operated installation to a military-owned or -operated
    treatment, storage, or disposal facility; and
     
    D) The transporter of the waste must provide oral notice to the
    Agency within 24 hours from the time when either the transporter
    becomes aware of any loss or theft of the waste military munitions
    or when any failure to meet a condition of subsection (a)(1) of this
    Section occurs that may endanger human health or the
    environment. In addition, a written submission describing the

     
    768
    circumstances must be provided within five days from the time
    when the transporter becomes aware of any loss or theft of the
    waste military munitions or when any failure to meet a condition
    of subsection (a)(1) of this Section occurs.
     
    2) If any waste military munitions shipped under subsection (a)(1) of this
    Section are not received by the receiving facility within 45 days after the
    day the waste was shipped, the owner or operator of the receiving facility
    must report this non-receipt to the Agency within five days.
     
    3) The conditional exemption from regulation as hazardous waste in
    subsection (a)(1) of this Section must apply only to the transportation of
    non-chemical waste military munitions. It does not affect the regulatory
    status of waste military munitions as hazardous wastes with regard to
    storage, treatment, or disposal.
     
    4) The conditional exemption in subsection (a)(1) of this Section applies only
    so long as all of the conditions in subsection (a)(1) of this Section are met.
     
    b) Reinstatement of conditional exemption.
     
    1) If any waste military munition loses its conditional exemption under
    subsection (a)(1) of this Section, the transporter may file with the Agency
    an application for reinstatement of the conditional exemption from
    hazardous waste transportation regulation with respect to such munition as
    soon as the munition is returned to compliance with the conditions of
    subsection (a)(1) of this Section.
     
    2) If the Agency finds that reinstatement of the conditional exemption is
    appropriate, it must reinstate the conditional exemption of subsection
    (a)(1) of this Section in writing. The Agency’s decision to reinstate or not
    to reinstate the conditional exemption must be based on the nature of the
    risks to human health and the environment posed by the waste and either
    the transporter's provision of a satisfactory explanation of the
    circumstances of the violation or any demonstration that the violations are
    not likely to recur. If the Agency denies an application, it must transmit to
    the applicant specific, detailed statements in writing as to the reasons it
    denied the application. In reinstating the conditional exemption under
    subsection (a)(1) of this Section, the Agency may specify additional
    conditions as are necessary to ensure and document proper transportation
    to protect human health and the environment. If the Agency does not take
    action on the reinstatement application within 60 days after receipt of the
    application, then reinstatement must be deemed granted, retroactive to the
    date of the application.
     
    3) The Agency may terminate a conditional exemption reinstated by default

     
    769
    under the preceding sentence in writing if it finds that reinstatement is
    inappropriate based on its consideration of the factors set forth in
    subsection (b)(2) of this Section. If the Agency terminates a reinstated
    exemption, it must transmit to the applicant specific, detailed statements in
    writing as to the reasons it terminated the reinstated exemption.
     
    4) The applicant under this subsection (b) may appeal the Agency’s
    determination to deny the reinstatement, to grant the reinstatement with
    conditions, or to terminate a reinstatement before the Board pursuant to
    Section 40 of the Act [415 ILCS 5/40].
     
    c) Amendments to DOD shipping controls. The Department of Defense shipping
    controls applicable to the transport of military munitions referenced in subsection
    (a)(1)(B) of this Section are Government Bill of Lading (GBL) (GSA Standard
    Form 1109), Requisition Tracking Form (DD Form 1348), the Signature and
    Talley Record (DD Form 1907), Special Instructions for Motor Vehicle Drivers
    (DD Form 836), and the Motor Vehicle Inspection Report (DD Form 626) in
    effect on November 8, 1995, incorporated by reference in 35 Ill. Adm. Code
    720.111 720.111(a).
     
    BOARD NOTE: Corresponding federal provision 40 CFR 266.203(c), as added
    at 62 Fed. Reg. 6655 (Feb. 12, 1997) 2005, further provides as follows: “Any
    amendments to the Department of Defense shipping controls must become
    effective for purposes of paragraph (a)(1) of this section on the date the
    Department of Defense publishes notice in the Federal Register that the shipping
    controls referenced in paragraph (a)(1)(ii) of this section have been amended.”
    (40 CFR 266.203(a)(1)(ii) corresponds with 35 Ill. Adm. Code 726.303(a)(1)(B).)
    Section 5-75 of the Illinois Administrative Procedure Act [5 ILCS 100/5-75]
    prohibits the incorporation of later amendments and editions by reference. For
    this reason, interested members of the regulated community will need to notify
    the Board of any amendments of these references before those amendments can
    become effective under Illinois law.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART N: CONDITIONAL EXEMPTION FOR LOW-LEVEL MIXED
    WASTE STORAGE, TREATMENT, TRANSPORTATION AND DISPOSAL
     
    Section 726.310 Definitions
     
    Terms are defined as follows for the purposes of this Subpart N:
     
    “CERCLA reportable quantity” means that quantity of a particular substance
    designated by USEPA in federal 40 CFR 302.4 pursuant to the Comprehensive
    Environmental Response, Compensation and Liability Act of 1980 (42 USC 9601
    et seq.) for which notification is required upon a release to the environment.

     
    770
     
    “Certified delivery” means certified mail with return receipt requested, equivalent
    courier service, or other means that provides the sender with a receipt confirming
    delivery.
     
    “Director” is as defined in 35 Ill. Adm. Code 702.110.
     
    “DNS” means the Department of Nuclear Safety, the State of Illinois agency
    charged with regulating source, by-product, and special nuclear material in
    Illinois in accordance with an agreement between the State and the federal
    Nuclear Regulatory Commission (NRC) under section 274(b) of the federal
    Atomic Energy Act of 1954, as amended (42 USC 2021(b)).
     
    BOARD NOTE: In addition to the materials regulated under this Part, the DNS
    regulates radioactive materials under the Radiation Protection Act of 1990 [420
    ILCS 40] that are not licensed by the federal NRC. For the purposes of notices to
    the DNS required under this Subpart N, the address is as follows:
     
    Illinois Department of Nuclear Safety
    1035 Outer Park Drive
    Springfield, Illinois 62704
     
    “Eligible naturally occurring or accelerator-produced radioactive material” means
    naturally occurring or accelerator-produced radioactive material (NARM) that is
    eligible for a transportation and disposal conditional exemption. It is a NARM
    waste that contains RCRA hazardous waste, meets the waste acceptance criteria
    of, and is allowed by State NARM regulations to be disposed of at a low-level
    radioactive waste disposal facility (LLRWDF) licensed in accordance with
    federal 10 CFR 61, DNS EMA regulations, or the equivalent regulations of a
    licensing agency in another state.
     
    BOARD NOTE: The Illinois DNS EMA regulations are codified at 32 Ill. Adm.
    Code: Chapter II, Subchapters b and d.
     
    “EMA” means the Emergency Management Agency, the State of Illinois agency
    charged with regulating source, by-product, and special nuclear material in
    Illinois in accordance with an agreement between the State and the federal
    Nuclear Regulatory Commission (NRC) under section 274(b) of the federal
    Atomic Energy Act of 1954, as amended (42 USC 2021(b)).
     
    BOARD NOTE: In addition to the materials regulated under this Part, the EMA
    regulates radioactive materials under the Radiation Protection Act of 1990 [420
    ILCS 40] that are not licensed by the federal NRC. For the purposes of notices to
    the EMA required under this Subpart N, the address is as follows:
     
    Illinois Emergency Management Agency

     
    771
    1035 Outer Park Drive
    Springfield, Illinois 62704
     
    “Exempted waste” means a waste that meets the eligibility criteria in Section
    726.325 and all of the conditions in Section 726.330 or a waste that meets the
    eligibility criteria in Section 726.410 and which complies with all the conditions
    in Section 726.415. Such waste is conditionally exempted from the regulatory
    definition of hazardous waste in 35 Ill. Adm. Code 721.103.
     
    “Hazardous waste” means hazardous waste as defined in 35 Ill. Adm. Code
    721.103.
     
    “Land disposal restriction treatment standards” or “LDR treatment standards”
    means treatment standards, under 35 Ill. Adm. Code 728, that a RCRA hazardous
    waste must meet before it can be disposed of in a RCRA hazardous waste land
    disposal unit.
     
    “License” means a license issued by the federal NRC or the Illinois DNS EMA to
    a user that manages radionuclides regulated by the federal NRC or the Illinois
    DNS EMA under authority of the Atomic Energy Act of 1954, as amended (42
    USC 2014 et seq.) or the Radiation Protection Act of 1990 [420 ILCS 40].
     
    “Low-level mixed waste” or “LLMW” is a waste that contains both low-level
    radioactive waste and RCRA hazardous waste.
     
    “Low-level radioactive waste” or “LLRW” is a radioactive waste that contains
    source, by-product, or special nuclear material and which is not classified as high-
    level radioactive waste, transuranic waste, spent nuclear fuel, or by-product
    material, as defined in section 11(e)(2) of the Atomic Energy Act of 1954 (42
    USC 2014(e)(2)), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
    (See also the NRC definition of waste at federal 10 CFR 61.2.)
     
    BOARD NOTE: This definition differs from the similar definitions of low-level
    radioactive waste in the Illinois Low-Level Radioactive Waste Management Act
    [420 ILCS 20/3(k)], the Central Midwest Interstate Low-Level Radioactive Waste
    Compact Act [45 ILCS 140/1, Article II(k)], and 32 Ill. Adm. Code 606.20(g) of
    the DNS EMA regulations. Those basically define low-level radioactive waste as
    radioactive waste that is not (1) high-level radioactive waste, (2) transuranic
    waste, (3) spent nuclear fuel, or (4) by-product material, as such are defined in
    section 11 of the federal Atomic Energy Act of 1954 (42 USC 2014),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    “Mixed waste” means a waste that contains both RCRA hazardous waste and
    source, by-product, or special nuclear material subject to the Atomic Energy Act
    of 1954, as amended (42 USC 2014 et seq.).
     

     
    772
    BOARD NOTE: This definition differs from the similar definitions of mixed
    waste in the Illinois Low-Level Radioactive Waste Management Act [420 ILCS
    20/3(l)] and 32 Ill. Adm. Code 606.20(h) of the DNS EMA regulations. Those
    basically define mixed waste as containing both RCRA hazardous waste and low-
    level radioactive waste, as such is defined under Section 3(k) of the Illinois Low-
    Level Radioactive Waste Management Act [420 ILCS 20/3(k)].
     
    “Naturally occurring or accelerator-produced radioactive material” or “NARM”
    means a radioactive material that fulfills one of the following conditions:
     
    It is naturally occurring and it is not a source, by-product, or special
    nuclear material, as defined by in section 11 of the federal Atomic Energy
    Act of 1954 (42 USC 2014 et seq.), incorporated by reference in 35 Ill.
    Adm. Code 720.111(c); or
     
    It is produced by an accelerator.
     
    BOARD NOTE: NARM is regulated by the State, under the Radiation Protection
    Act of 1990 [420 ILCS 40] and 32 Ill. Adm. Code: Chapter II, Subchapters b and
    d, or by the federal Department of Energy (DOE), as authorized by the federal
    Atomic Energy Act (42 USC 2014 et seq.), under DOE regulations and orders.
     
    “NRC” means the United States Nuclear Regulatory Commission.
     
    BOARD NOTE: For the purposes of notices to the NRC required under this
    Subpart N, the address is as follows:
     
    U.S. Nuclear Regulatory Commission, Region III
    801 Warrenville Road
    Lisle, Illinois 60532-4351
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.325 Wastes Eligible for a Storage and Treatment Conditional Exemption for
    Low-Level Mixed Waste
     
    Low-level mixed waste (LLMW), as defined in Section 726.310, is eligible for a storage and
    treatment conditional exemption if it is generated and managed by a person under a single
    federal NRC or Illinois DNS EMA license. (Mixed waste generated at a facility with a different
    license number and shipped to a different person’s facility for storage or treatment requires a
    permit, and such mixed waste is ineligible for this exemption. In addition, NARM waste is
    ineligible for this exemption.)
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    773
    Section 726.330 Conditions to Qualify for and Maintain a Storage and Treatment
    Conditional Exemption
     
    a) For LLMW to qualify for the exemption, the generator must notify the Agency
    and the Illinois DNS EMA in writing by certified delivery that it is claiming a
    storage and treatment conditional exemption for the LLMW stored on the
    generator’s facility. The dated notification must include the generator’s name,
    address, RCRA identification number, federal NRC or Illinois DNS EMA license
    number, the waste codes and storage units for which the generator is seeking an
    exemption, and a statement that the generator meets the conditions of this Subpart
    N. The generator’s notification must be signed by the generator’s authorized
    representative who certifies that the information in the notification is true,
    accurate, and complete. The generator must notify the Agency of its claim either
    before July 21, 2002, or within 90 days after a storage unit is first used to store
    conditionally exempt LLMW, whichever is later.
     
    b) To qualify for and maintain an exemption for LLMW, the generator must do each
    of the following:
     
    1) Store its LLMW waste in tanks or containers in compliance with the
    requirements of its license that apply to the proper storage of low-level
    radioactive waste (not including those license requirements that relate
    solely to recordkeeping);
     
    2) Store its LLMW in tanks or containers in compliance with chemical
    compatibility requirements of a tank or container in 35 Ill. Adm. Code
    724.277 or 724.299 or 35 Ill. Adm. Code 725.277 or 725.299;
     
    3) Certify that facility personnel who manage stored conditionally exempt
    LLMW are trained in a manner that ensures that the conditionally exempt
    waste is safely managed and that the training includes training in chemical
    waste management and hazardous materials incidents response that meets
    the personnel training standards found in 35 Ill. Adm. Code 725.116(a)(3);
     
    4) Conduct an inventory of its stored conditionally exempt LLMW at least
    annually and inspect the waste at least quarterly for compliance with this
    Subpart N; and
     
    5) Maintain an accurate emergency plan and provide it to all local authorities
    who may have to respond to a fire, explosion, or release of hazardous
    waste or hazardous constituents. The generator’s plan must describe
    emergency response arrangements with local authorities; describe
    evacuation plans; list the names, addresses, and telephone numbers of all
    facility personnel qualified to work with local authorities as emergency
    coordinators; and list emergency equipment.
     

     
    774
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.335 Treatment Allowed by a Storage and Treatment Conditional Exemption
     
    The generator may treat its low-level mixed waste at its facility within a tank or container in
    accordance with the terms of its federal NRC or Illinois DNS EMA license. Treatment that
    cannot be done in a tank or container without a RCRA permit (such as incineration) is not
    allowed under this exemption.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.350 Recordkeeping for a Storage and Treatment Conditional Exemption
     
    a) In addition to those records required by the generator’s federal NRC or Illinois
    DNS EMA license, the generator must keep records as follows:
     
    1) The generator’s initial notification records, return receipts, reports to the
    Agency of failures to meet the exemption conditions, and all records
    supporting any reclaim of an exemption;
     
    2) Records of the generator’s LLMW annual inventories and quarterly
    inspections;
     
    3) The generator’s certification that facility personnel who manage stored
    mixed waste are trained in safe management of LLMW including training
    in chemical waste management and hazardous materials incidents
    response; and
     
    4) The generator’s emergency plan, as specified in Section 726.330(b).
     
    b) The generator must maintain records concerning notification, personnel trained,
    and its emergency plan for as long as the generator claims this exemption and for
    three years thereafter, or in accordance with federal NRC regulations, under
    federal 10 CFR 20, or under Illinois DNS EMA regulations, under 32 Ill. Adm.
    Code: Chapter II, Subchapter b, whichever is longer. A generator must maintain
    records concerning its annual inventory and quarterly inspections for three years
    after the waste is sent for disposal, or in accordance with federal NRC
    regulations, under 10 CFR 20, or with Illinois DNS EMA regulations, under 32
    Ill. Adm. Code: Chapter II, Subchapter b, whichever is longer.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.355 Waste No Longer Eligible for a Storage and Treatment Conditional
    Exemption
     
    a) When a generator’s LLMW has met the requirements of its federal NRC or

     
    775
    Illinois DNS EMA license for decay-in-storage and can be disposed of as non-
    radioactive waste, then the conditional exemption for storage no longer applies.
    On that date the generator’s waste is subject to hazardous waste regulation under
    the relevant Sections of 35 Ill. Adm. Code 702, 703, 720 through 726, and 728,
    and the time period for accumulation of a hazardous waste, as specified in 35 Ill.
    Adm. Code 722.134 begins.
     
    b) When a generator’s conditionally exempt LLMW, which has been generated and
    stored under a single federal NRC or Illinois DNS EMA license number, is
    removed from storage, it is no longer eligible for the storage and treatment
    exemption. However, a generator’s waste may be eligible for the transportation
    and disposal conditional exemption at Section 726.405.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.415 Conditions to Qualify for and Maintain a Transportation and Disposal
    Conditional Exemption
     
    A generator must meet the following conditions for its eligible waste to qualify for and maintain
    the exemption:
     
    a) The eligible waste must meet or be treated to meet LDR treatment standards, as
    described in Section 726.420;
     
    b) If the generator is not already subject to federal NRC or Illinois DNS EMA
    manifest and transportation regulations for the shipment of its waste, the
    generator must manifest and transport its waste according to federal NRC or
    Illinois DNS EMA regulations, as described in Section 726.425;
     
    c) The exempted waste must be in containers when it is disposed of in the
    LLRWDF, as described in Section 726.440; and
     
    d) The exempted waste must be disposed of at a designated LLRWDF, as described
    in Section 726.435.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.425 Applicability of the Manifest and Transportation Condition
     
    If a generator is not already subject to federal NRC or Illinois DNS EMA manifest and
    transportation regulations for the shipment of its waste, the generator must meet the federal NRC
    manifest requirements under 10 CFR 20.2006 (Transfer for Disposal and Manifests),
    incorporated by reference in 35 Ill. Adm. Code 720.111, 720.111(b); and Illinois DNS EMA
    manifest requirements under 32 Ill. Adm. Code 340,; and the federal NRC transportation
    requirements under 10 CFR 71.5 (Transportation of Licensed Material), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b); and the Illinois DNS EMA transportation

     
    776
    requirements under 32 Ill. Adm. Code 341 to ship the exempted waste.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.430 Effectiveness of a Transportation and Disposal Exemption
     
    The exemption becomes effective once all of the following have occurred:
     
    a) The generator’s eligible waste meets the applicable LDR treatment standards;
     
    b) The generator has received return receipts that it has notified the Agency and the
    LLRWDF, as described in Section 726.445;
     
    c) The generator has completed the packaging and preparation for shipment
    requirements for its waste according to federal NRC packaging and transportation
    regulations found under 10 CFR 71 (Packaging and Transportation of Radioactive
    Material), incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(b),
    and under Illinois DNS EMA regulations under 32 Ill. Adm. Code 341; and a
    generator has prepared a manifest for a generator’s waste according to NRC
    manifest regulations found under 10 CFR 20 (Standards for Protection against
    Radiation), incorporated by reference in 35 Ill. Adm. Code 720.111(b), or under
    Illinois DNS EMA regulations under 32 Ill. Adm. Code 340; and
     
    d) The generator has placed its waste on a transportation vehicle destined for a
    LLRWDF licensed by the federal NRC, the Illinois DNS, or by a nuclear
    licensing agency in another state.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.435 Disposal of Exempted Waste
     
    A generator’s exempted waste must be disposed of in a LLRWDF that is regulated and licensed
    by the federal NRC under 10 CFR 61, by the Illinois DNS EMA under 32 Ill. Adm. Code:
    Chapter II, Subchapters b and d, or by a licensing agency in another state, including State
    NARM licensing regulations for eligible NARM.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.440 Containers Used for Disposal of Exempted Waste
     
    A generator’s exempted waste must be placed in containers before it is disposed of. The
    container must be one of the following:
     
    a) A carbon steel drum;
     
    b) An alternative container with equivalent containment performance in the disposal

     
    777
    environment as a carbon steel drum; or
     
    c) A high-integrity container, as defined by NRC in Appendix G to 40 10 CFR 20
    (Requirements for Transfers of Low-Level Radioactive Waste Intended for
    Disposal at Licensed Land Disposal Facilities and Manifests), incorporated by
    reference in 35 Ill. Adm. Code 720.111 720.111(b).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.445 Notification
     
    a) A generator must provide a one time notice to the Agency and the Illinois DNS
    EMA stating that it is claiming the transportation and disposal conditional
    exemption prior to the initial shipment of an exempted waste from the generator’s
    facility to a LLRWDF. The generator’s dated written notice must include its
    facility name, address, phone number, and RCRA ID number and be sent by
    certified delivery.
     
    b) A generator must notify the LLRWDF receiving its exempted waste by certified
    delivery before shipment of each exempted waste. The generator can only ship
    the exempted waste after it has received the return receipt of its notice to the
    LLRWDF. This notification must include the following information:
     
    1) A statement that the generator has claimed the exemption for the waste;
     
    2) A statement that the eligible waste meets applicable LDR treatment
    standards;
     
    3) The generator’s facility’s name, address, and RCRA ID number;
     
    4) The RCRA hazardous waste codes prior to the exemption of the waste
    streams;
     
    5) A statement that the exempted waste must be placed in a container
    according to Section 726.440 prior to disposal in order for the waste to
    remain exempt under the transportation and disposal conditional
    exemption of this Subpart N;
     
    6) The manifest number of the shipment that will contain the exempted
    waste; and
     
    7) A certification that all the information provided is true, complete, and
    accurate. The statement must be signed by the generator’s authorized
    representative.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)

     
    778
     
    Section 726.450 Recordkeeping for a Transportation and Disposal Conditional Exemption
     
    In addition to those records required by a generator’s NRC or Illinois DNS EMA license, the
    generator must keep records as follows:
     
    a) The generator must follow the applicable existing recordkeeping requirements
    under 35 Ill. Adm. Code 724.173, 725.173, and 728.107 to demonstrate that its
    waste has met LDR treatment standards prior to the generator claiming the
    exemption.
     
    b) The generator must keep a copy of all notifications and return receipts required
    under Sections 726.455, and 726.460 for three years after the exempted waste is
    sent for disposal.
     
    c) The generator must keep a copy of all notifications and return receipts required
    under Section 726.445(a) for three years after the last exempted waste is sent for
    disposal.
     
    d) The generator must keep a copy of the notification and return receipt required
    under Section 726.445(b) for three years after the exempted waste is sent for
    disposal.
     
    e) If the generator is not already subject to federal NRC and Illinois DNS EMA
    manifest and transportation regulations for the shipment of its waste, the
    generator must also keep all other documents related to tracking the exempted
    waste as required under federal 10 CFR 20.2006 (Transfer for Disposal and
    Manifests), incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(b),
    and Illinois DNS EMA requirements under 32 Ill. Adm. Code 340, including
    applicable NARM requirements, in addition to the records specified in
    subsections (a) through (d) of this Section.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.460 Reclaiming a Lost Transportation and Disposal Conditional Exemption
     
    a) A generator may reclaim a lost transportation and disposal conditional exemption
    for a waste after the generator has received a return receipt confirming that the
    Agency and the Illinois DNS EMA have received the generator’s notification of
    the loss of the exemption specified in Section 726.455(a) and if the following
    conditions are fulfilled:
     
    1) The generator again meets the conditions specified in Section 726.415 for
    the waste; and
     
    2) The generator sends a notice, by certified delivery, to the Agency that the

     
    779
    generator is reclaiming the exemption for the waste. A generator’s notice
    must be signed by the generator’s authorized representative certifying that
    the information provided is true, accurate, and complete. The notice must
    include all of the following:
     
    A) An explanation of the circumstances of each failure;
     
    B) A certification that each failure that caused the generator to lose
    the exemption for the waste has been corrected and that the
    generator again meets all conditions for the waste as of the date the
    generator specifies;
     
    C) A description of plans that the generator has implemented, listing
    the specific steps that the generator has taken, to ensure that
    conditions will be met in the future; and
     
    D) Any other information that the generator wants the Agency to
    consider when the Agency reviews the generator’s notice
    reclaiming the exemption.
     
    b) The Agency may terminate a reclaimed conditional exemption if it determines, in
    writing, pursuant to Section 39 of the Act [415 ILCS 5/39], that the generator’s
    claim is inappropriate based on factors including, but not limited to, the
    following: the generator has failed to correct the problem; the generator
    explained the circumstances of the failure unsatisfactorily; or the generator has
    failed to implement a plan with steps to prevent another failure to meet the
    conditions of Section 726.415. In reviewing a reclaimed conditional exemption
    under this Section, the Agency may add conditions to the exemption to ensure
    that transportation and disposal activities will protect human health and the
    environment. Any Agency determination made pursuant to this subsection (b) is
    subject to review by the Board pursuant to Section 40 of the Act [415 ILCS 5/40].
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 726.Appendix I Methods Manual for Compliance with BIF Regulations
     
    See The document entitled, “Methods Manual for Compliance with BIF Regulations.” This
    document : Burning Hazardous Waste in Boilers and Industrial Furnaces,” December 1990, is
    available from two sourcesas appendix IX to 40 CFR 266 (Methods Manual for Compliance with
    the BIF Regulations), incorporated by reference in 35 Ill. Adm. Code 720.111(b). It is also
    available through NTIS, incorporated by reference in 35 Ill. Adm. Code 720.111 as described in
    the incorporation by reference. It is also available as 40 CFR 266, Appendix IX, incorporated by
    reference in 35 Ill. Adm. Code 720.111.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    780
    Section 726.Appendix J Guideline on Air Quality Models (Repealed)
     
    See “Guideline on Air Quality Models (Revised).” This document is available from two sources.
    It is available through NTIS, incorporated by reference in 35 Ill. Adm. Code 720.111. It is also
    available as 40 CFR 266, Appendix X, incorporated by reference in 35 Ill. Adm. Code 720.111.
    This incorporation includes no future editions or amendments.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
     
    PART 728
    LAND DISPOSAL RESTRICTIONS
     
    SUBPART A: GENERAL
    Section
    728.101 Purpose, Scope, and Applicability
    728.102 Definitions
    728.103 Dilution Prohibited as a Substitute for Treatment
    728.104 Treatment Surface Impoundment Exemption
    728.105 Procedures for Case-by-Case Extensions to an Effective Date
    728.106 Petitions to Allow Land Disposal of a Waste Prohibited under Subpart C
    728.107 Testing, Tracking, and Recordkeeping Requirements for Generators, Treaters, and
    Disposal Facilities
    728.108 Landfill and Surface Impoundment Disposal Restrictions (Repealed)
    728.109 Special Rules for Characteristic Wastes
     
    SUBPART B: SCHEDULE FOR LAND DISPOSAL PROHIBITION AND
    ESTABLISHMENT OF TREATMENT STANDARDS
    Section
    728.110 First Third (Repealed)
    728.111 Second Third (Repealed)
    728.112 Third Third (Repealed)
    728.113 Newly Listed Wastes
    728.114 Surface Impoundment Exemptions
     
    SUBPART C: PROHIBITION ON LAND DISPOSAL
    Section
    728.120 Waste-Specific Prohibitions: Dyes and Pigments Production Wastes
    728.130 Waste-Specific Prohibitions: Wood Preserving Wastes
    728.131 Waste-Specific Prohibitions: Dioxin-Containing Wastes
    728.132 Waste-Specific Prohibitions: Soils Exhibiting the Toxicity Characteristic for
    Metals and Containing PCBs

     
    781
    728.133 Waste-Specific Prohibitions: Chlorinated Aliphatic Wastes
    728.134 Waste-Specific Prohibitions: Toxicity Characteristic Metal Wastes
    728.135 Waste-Specific Prohibitions: Petroleum Refining Wastes
    728.136 Waste-Specific Prohibitions: Inorganic Chemical Wastes
    728.137 Waste-Specific Prohibitions: Ignitable and Corrosive Characteristic Wastes
    Whose Treatment Standards Were Vacated
    728.138 Waste-Specific Prohibitions: Newly-Identified Organic Toxicity Characteristic
    Wastes and Newly-Listed Coke By-Product and Chlorotoluene Production
    Wastes
    728.139 Waste-Specific Prohibitions: Spent Aluminum Potliners and Carbamate Wastes
     
    SUBPART D: TREATMENT STANDARDS
    Section
    728.140 Applicability of Treatment Standards
    728.141 Treatment Standards Expressed as Concentrations in Waste Extract
    728.142 Treatment Standards Expressed as Specified Technologies
    728.143 Treatment Standards Expressed as Waste Concentrations
    728.144 Adjustment of Treatment Standard
    728.145 Treatment Standards for Hazardous Debris
    728.146 Alternative Treatment Standards Based on HTMR
    728.148 Universal Treatment Standards
    728.149 Alternative LDR Treatment Standards for Contaminated Soil
     
    SUBPART E: PROHIBITIONS ON STORAGE
    Section
    728.150 Prohibitions on Storage of Restricted Wastes
     
    728.Appendix A Toxicity Characteristic Leaching Procedure (TCLP) (Repealed)
    728.Appendix B Treatment Standards (As concentrations in the Treatment Residual
    Extract) (Repealed)
    728.Appendix C List of Halogenated Organic Compounds Regulated under Section
    728.132
    728.Appendix D Wastes Excluded from Lab Packs
    728.Appendix E Organic Lab Packs (Repealed)
    728.Appendix F Technologies to Achieve Deactivation of Characteristics
    728.Appendix G Federal Effective Dates
    728.Appendix H National Capacity LDR Variances for UIC Wastes
    728.Appendix I EP Toxicity Test Method and Structural Integrity Test
    728.Appendix J Recordkeeping, Notification, and Certification Requirements (Repealed)
    728.Appendix K Metal-Bearing Wastes Prohibited from Dilution in a Combustion Unit
    According to Section 728.103(c)
    728.Table A Constituent Concentrations in Waste Extract (CCWE)
    728.Table B Constituent Concentrations in Wastes (CCW)
    728.Table C Technology Codes and Description of Technology-Based Standards
    728.Table D Technology-Based Standards by RCRA Waste Code
    728.Table E Standards for Radioactive Mixed Waste

     
    782
    728.Table F Alternative Treatment Standards for Hazardous Debris
    728.Table G Alternative Treatment Standards Based on HTMR
    728.Table H Wastes Excluded from CCW Treatment Standards
    728.Table I Generator Paperwork Requirements
    728.Table T Treatment Standards for Hazardous Wastes
    728.Table U Universal Treatment Standards (UTS)
     
    AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the
    Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].
     
    SOURCE: Adopted in R87-5 at 11 Ill. Reg. 19354, effective November 12, 1987; amended in
    R87-39 at 12 Ill. Reg. 13046, effective July 29, 1988; amended in R89-1 at 13 Ill. Reg. 18403,
    effective November 13, 1989; amended in R89-9 at 14 Ill. Reg. 6232, effective April 16, 1990;
    amended in R90-2 at 14 Ill. Reg. 14470, effective August 22, 1990; amended in R90-10 at 14 Ill.
    Reg. 16508, effective September 25, 1990; amended in R90-11 at 15 Ill. Reg. 9462, effective
    June 17, 1991; amended in R90-11 at 15 Ill. Reg. 11937, effective August 12, 1991; amendment
    withdrawn at 15 Ill. Reg. 14716, October 11, 1991; amended in R91-13 at 16 Ill. Reg. 9619,
    effective June 9, 1992; amended in R92-10 at 17 Ill. Reg. 5727, effective March 26, 1993;
    amended in R93-4 at 17 Ill. Reg. 20692, effective November 22, 1993; amended in R93-16 at 18
    Ill. Reg. 6799, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12203, effective July
    29, 1994; amended in R94-17 at 18 Ill. Reg. 17563, effective November 23, 1994; amended in
    R95-6 at 19 Ill. Reg. 9660, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 11100,
    effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 783, effective
    December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7685, effective April 15, 1998; amended
    in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17706, effective September 28, 1998; amended in R98-
    21/R99-2/R99-7 at 23 Ill. Reg. 1964, effective January 19, 1999; amended in R99-15 at 23 Ill.
    Reg. 9204, effective July 26, 1999; amended in R00-13 at 24 Ill. Reg. 9623, effective June 20,
    2000; amended in R01-3 at 25 Ill. Reg. 1296, effective January 11, 2001; amended in R01-
    21/R01-23 at 25 Ill. Reg. 9181, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26
    Ill. Reg. 6687, effective April 22, 2002; amended in R03-18 at 27 Ill. Reg. 13045, effective July
    17, 2003; amended in R05-8 at 29 Ill. Reg. 6049, effective April 13, 2005; amended in R06-
    5/R06-6/R06-7 at 30 Ill. Reg. ________, effective ______________________.
     
    SUBPART A: GENERAL
     
    Section 728.102 Definitions
     
    When used in this Part, the following terms have the meanings given below. All other terms
    have the meanings given under 35 Ill. Adm. Code 702.110, 720.110, or 721.102 through
    721.104.
     
    “Agency” means the Illinois Environmental Protection Agency.
     
    “Board” means the Illinois Pollution Control Board.
     
    “CERCLA” means the Comprehensive Environmental Response, Compensation,

     
    783
    and Liability Act of 1980 (42 USC 9601 et seq.)
     
    “Debris” means solid material exceeding a 60 mm particle size that is intended for
    disposal and that is: a manufactured object; plant or animal matter; or natural
    geologic material. However, the following materials are not debris: any material
    for which a specific treatment standard is provided in Subpart D of this Part,
    namely lead acid batteries, cadmium batteries, and radioactive lead solids; process
    residuals, such as smelter slag and residues from the treatment of waste,
    wastewater, sludges, or air emission residues; and intact containers of hazardous
    waste that are not ruptured and that retain at least 75 percent of their original
    volume. A mixture of debris that has not been treated to the standards provided
    by Section 728.145 of this Part and other material is subject to regulation as
    debris if the mixture is comprised primarily of debris, by volume, based on visual
    inspection.
     
    “End-of-pipe” refers to the point where effluent is discharged to the environment.
     
    “Halogenated organic compounds” or “HOCs” means those compounds having a
    carbon-halogen bond that are listed under Appendix C of this Part.
     
    “Hazardous constituent or constituents” means those constituents listed in
    Appendix H to 35 Ill. Adm. Code 721.
     
    “Hazardous debris” means debris that contains a hazardous waste listed in
    Subpart D of 35 Ill. Adm. Code 721 or that exhibits a characteristic of hazardous
    waste identified in Subpart C of 35 Ill. Adm. Code 721. Any deliberate mixing of
    prohibited waste with debris that changes its treatment classification (i.e., from
    waste to hazardous debris) is not allowed under the dilution prohibition in Section
    728.103.
     
    “Inorganic metal-bearing waste” is one for which USEPA has established
    treatment standards for metal hazardous constituents that does not otherwise
    contain significant organic or cyanide content, as described in Section
    728.103(b)(1), and which is specifically listed in Appendix K of this Part.
     
    “Land disposal” means placement in or on the land, except in a corrective action
    management unit or staging pile, and “land disposal” includes, but is not limited
    to, placement in a landfill, surface impoundment, waste pile, injection well, land
    treatment facility, salt dome formation, salt bed formation, underground mine or
    cave, or placement in a concrete vault or bunker intended for disposal purposes.
     
    “Nonwastewaters” are wastes that do not meet the criteria for “wastewaters” in
    this Section.
     
    “Polychlorinated biphenyls” or “PCBs” are halogenated organic compounds
    defined in accordance with federal 40 CFR 761.3 (Definitions), incorporated by

     
    784
    reference in 35 Ill. Adm. Code 720.111 720.111(b).
     
    “ppm” means parts per million.
     
    “RCRA corrective action” means corrective action taken under 35 Ill. Adm. Code
    724.200 or 725.193, federal 40 CFR 264.100 or 265.93, or similar regulations in
    other states with RCRA programs authorized by USEPA pursuant to 40 CFR 271.
     
    “Soil” means unconsolidated earth material composing the superficial geologic
    strata (material overlying bedrock), consisting of clay, silt, sand, or gravel size
    particles, as classified by the United States Natural Resources Conservation
    Service, or a mixture of such materials with liquids, sludges, or solids that is
    inseparable by simple mechanical removal processes and which is made up
    primarily of soil by volume based on visual inspection. Any deliberate mixing of
    prohibited waste with debris that changes its treatment classification (i.e., from
    waste to hazardous debris) is not allowed under the dilution prohibition in Section
    728.103.
     
    “Stormwater impoundments” are surface impoundments that receive wet weather
    flow and which receive process waste only during wet weather events.
     
    “Underlying hazardous constituent” means any constituent listed in Table U of
    this Part, “Universal Treatment Standards (UTS),” except fluoride, selenium,
    sulfides, vanadium, and zinc, that can reasonably be expected to be present at the
    point of generation of the hazardous waste at a concentration above the
    constituent-specific UTS treatment standard.
     
    “USEPA” or “U.S. EPA” means the United States Environmental Protection
    Agency.
     
    “Wastewaters” are wastes that contain less than one percent by weight total
    organic carbon (TOC) and less than one percent by weight total suspended solids
    (TSS).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.103 Dilution Prohibited as a Substitute for Treatment
     
    a) Except as provided in subsection (b) of this Section, no generator, transporter,
    handler, or owner or operator of a treatment, storage, or disposal facility must in
    any way dilute a restricted waste or the residual from treatment of a restricted
    waste as a substitute for adequate treatment to achieve compliance with Subpart D
    of this Part, to circumvent the effective date of a prohibition in Subpart C of this
    Part, to otherwise avoid a prohibition in Subpart C of this Part, or to circumvent a
    land disposal restriction imposed by RCRA section 3004 (42 USC 6924).
     

     
    785
    b) Dilution of waste that is hazardous only because it exhibits a characteristic of
    hazardous waste in a treatment system that treats wastes subsequently discharged
    to a water of the State pursuant to an NPDES permit issued under 35 Ill. Adm.
    Code 309, that treats wastes in a CWA-equivalent treatment system, or that treats
    wastes for purposes of pretreatment requirements under 35 Ill. Adm. Code 310 is
    not impermissible dilution for purposes of this Section, unless a method other
    than DEACT has been specified in Section 728.140 as the treatment standard or
    unless the waste is a D003 reactive cyanide wastewater or nonwastewater.
     
    c) Combustion of waste designated by any of the USEPA hazardous waste codes
    listed in Appendix J to this Part is prohibited, unless the waste can be
    demonstrated to comply with one or more of the following criteria at the point of
    generation or after any bona fide treatment, such as cyanide destruction prior to
    combustion (unless otherwise specifically prohibited from combustion):
     
    1) The waste contains hazardous organic constituents or cyanide at levels
    exceeding the constituent-specific treatment standard found in Section
    728.148;
     
    2) The waste consists of organic, debris-like materials (e.g., wood, paper,
    plastic, or cloth) contaminated with an inorganic metal-bearing hazardous
    waste;
     
    3) The waste has reasonable heating value, such as greater than or equal to
    5000 5,000 Btu per pound, at the point of generation;
     
    4) The waste is co-generated with wastes for which combustion is a required
    method of treatment;
     
    5) The waste is subject to any federal or state requirements necessitating
    reduction of organics (including biological agents); or
     
    6) The waste contains greater than one percent Total Organic Carbon (TOC).
     
    d) It is a form of impermissible dilution, and therefore prohibited, to add iron filings
    or other metallic forms of iron to lead-containing hazardous wastes in order to
    achieve any land disposal restriction treatment standard for lead. Lead-containing
    wastes include D008 wastes (wastes exhibiting a characteristic due to the
    presence of lead), all characteristic wastes containing lead as an underlying
    hazardous constituent, listed wastes containing lead as a regulated constituent,
    and hazardous media containing any of the aforementioned lead-containing
    wastes.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    786
    Section 728.105 Procedures for Case-by-Case Extensions to an Effective Date
     
    a)
    The Board incorporates by reference 40 CFR 268.5 (2002). This Part
    incorporates no future editions or amendments.
     
    b)
    Persons may apply to USEPA for extensions of effective dates pursuant to 40 CFR
    268.5. Extensions that are granted by USEPA will be deemed extensions of dates
    specified in the derivative Board rule.
     
    Any person may apply to USEPA for an extension of an effective date pursuant to 40 CFR 268.5.
    Any extension that is granted by USEPA will be deemed an extension of the effective date of the
    derivative Board rule.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.106 Petitions to Allow Land Disposal of a Waste Prohibited under Subpart C
     
    a) Any person seeking an exemption from a prohibition under Subpart C for the
    disposal of a restricted hazardous waste in a particular unit or units must submit a
    petition to the Board demonstrating, to a reasonable degree of certainty, that there
    will be no migration of hazardous constituents from the disposal unit or injection
    zone for as long as the wastes remain hazardous. The demonstration must include
    the following components:
     
    1) An identification of the specific waste and the specific unit for which the
    demonstration will be made;
     
    2) A waste analysis to describe fully the chemical and physical characteristics of
    the subject waste;
     
    3) A comprehensive characterization of the disposal unit site including an
    analysis of background air, soil, and water quality;
     
    4) A monitoring plan that detects migration at the earliest practical time;
     
    5) Sufficient information to assure the Agency that the owner or operator of a
    land disposal unit receiving restricted wastes will comply with other
    applicable federal, state, and local laws;
     
    6) Whether the facility is in interim status, or, if a RCRA permit has been
    issued, the term of the permit.
     
    b) The demonstration referred to in subsection (a) of this Section must meet the
    following criteria:
     
    1) All waste and environmental sampling, test and analysis data must be

     
    787
    accurate and reproducible to the extent that state-of-the-art techniques allow;
     
    2) All sampling, testing and estimation techniques for chemical and physical
    properties of the waste and all environmental parameters must conform with
    “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”
    USEPA publication number EPA-530/SW-846, and with “Generic Quality
    Assurance Project Plan for Land Disposal Restrictions Program,” USEPA
    publication number EPA-530/SW-87-011, each incorporated by reference
    in 35 Ill. Adm. Code 720.111.
     
    3) Simulation models must be calibrated for the specific waste and site
    conditions, and verified for accuracy by comparison with actual
    measurements;
     
    4) A quality assurance and quality control plan that addresses all aspects of the
    demonstration and conforms with “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods,” USEPA publication number EPA530/SW-
    846, and with “Generic Quality Assurance Project Plan for Land Disposal
    Restrictions Program,” USEPA publication number EPA-530/SW-87-011,
    incorporated by reference in 35 Ill. Adm. Code 720.111; and
     
    5) An analysis must be performed to identify and quantify any aspects of the
    demonstration that contribute significantly to uncertainty. This analysis must
    include an evaluation of the consequences of predictable future events,
    including, but not limited to, earthquakes, floods, severe storm events,
    droughts, or other natural phenomena.
     
    c) Each petition referred to in subsection (a) of this Section must include the following:
     
    1) A monitoring plan that describes the monitoring program installed at or
    around the unit to verify continued compliance with the conditions of the
    adjusted standard. This monitoring plan must provide information on the
    monitoring of the unit or the environment around the unit. The following
    specific information must be included in the plan:
     
    A) The media monitored in the cases where monitoring of the
    environment around the unit is required;
     
    B) The type of monitoring conducted at the unit, in the cases where
    monitoring of the unit is required;
     
    C) The location of the monitoring stations;
     
    D) The monitoring interval (frequency of monitoring at each station);
     
    E) The specific hazardous constituents to be monitored;

     
    788
     
    F) The implementation schedule for the monitoring program;
     
    G) The equipment used at the monitoring stations;
     
    H) The sampling and analytical techniques employed; and
     
    I) The data recording and reporting procedures.
     
    2) Where applicable, the monitoring program described in subsection (c)(1) of
    this Section must be in place for a period of time specified by the Board, as
    part of its approval of the petition, prior to receipt of prohibited waste at the
    unit.
     
    3) The monitoring data collected according to the monitoring plan specified
    under subsection (c)(1) of this Section must be sent to the Agency according
    to a format and schedule specified and approved in the monitoring plan.
     
    4) A copy of the monitoring data collected under the monitoring plan specified
    under subsection (c)(1) of this Section must be kept on-site at the facility in
    the operating record.
     
    5) The monitoring program specified under subsection (c)(1) of this Section
    must meet the following criteria:
     
    A) All sampling, testing, and analytical data must be approved by the
    Board and must provide data that is accurate and reproducible;
     
    B) All estimation and monitoring techniques must be approved by the
    Board; and
     
    C) A quality assurance and quality control plan addressing all aspects of
    the monitoring program must be provided to and approved by the
    Board.
     
    d) Each petition must be submitted to the Board as provided in Subpart D of 35 Ill.
    Adm. Code 104.
     
    e) After a petition has been approved, the owner or operator must report any changes in
    conditions at the unit or the environment around the unit that significantly depart
    from the conditions described in the petition and affect the potential for migration of
    hazardous constituents from the units as follows:
     
    1) If the owner or operator plans to make changes to the unit design,
    construction, or operation, the owner or operator must do the following at
    least 90 days prior to making the change:

     
    789
     
    A) File a petition for modification of or a new petition to amend an
    adjusted standard with the Board reflecting the changes; or
     
    B) Demonstrate to the Agency that the change can be made consistent
    with the conditions of the existing adjusted standard.
     
    2) If the owner or operator discovers that a condition at the site that was
    modeled or predicted in the petition does not occur as predicted, this change
    must be reported, in writing, to the Agency within 10 days after discovering
    the change. The Agency must determine whether the reported change from
    the terms of the petition requires further action, which may include
    termination of waste acceptance, a petition for modification of or a new
    petition for an adjusted standard.
     
    f) If there is migration of hazardous constituents from the unit, as determined by the
    owner or operator, the owner or operator must:
     
    1) Immediately suspend receipt of prohibited waste at the unit, and
     
    2) Notify the Agency, in writing, within 10 days after the determination that a
    release has occurred.
     
    3) Following receipt of the notification, the Agency shall, within 60 days after
    receiving notification:
     
    A) Determine whether the owner or operator can continue to receive
    prohibited waste in the unit under the conditions of the adjusted
    standard.
     
    B) If modification or vacation of the adjusted standard is necessary, file
    a motion to modify or vacate the adjusted standard with the Board.
     
    C) Determine whether further examination of any migration is required
    under the applicable provisions of 35 Ill. Adm. Code 724 or 725.
     
    g) Each petition must include the following statement signed by the petitioner or an
    authorized representative:
     
    I certify under penalty of law that I have personally examined and am
    familiar with the information submitted in this petition and all attached
    documents, and that, based on my inquiry of those individuals immediately
    responsible for obtaining the information. I believe that submitted
    information is true, accurate, and complete. I am aware that there are
    significant penalties for submitting false information, including the
    possibility of fine and imprisonment.

     
    790
     
    h) After receiving a petition, the Board may request any additional information that may
    be required to evaluate the demonstration.
     
    i) If approved, the petition will apply to land disposal of the specific restricted waste at
    the individual disposal unit described in the demonstration and will not apply to any
    other restricted waste at that disposal unit, or to that specific restricted waste at any
    other disposal unit.
     
    j) The Board will give public notice and provide an opportunity for public comment, as
    provided in Subpart D of 35 Ill. Adm. Code 104. Notice of a final decision on a
    petition will be published in the Environmental Register.
     
    k) The term of a petition granted under this Section will be no longer than the term of
    the RCRA permit if the disposal unit is operating under a RCRA permit, or up to a
    maximum of 10 years from the date of approval provided under subsection (g) of
    this Section if the unit is operating under interim status. In either case, the term of
    the granted petition expires upon the termination or denial of a RCRA permit, or
    upon the termination of interim status or when the volume limit of waste to be land
    disposed during the term of petition is reached.
     
    l) Prior to the Board’s decision, the applicant must comply with all restrictions on land
    disposal under this Part once the effective date for the waste has been reached.
     
    m) The petition granted by the Board does not relieve the petitioner of responsibilities in
    the management of hazardous waste under 35 Ill. Adm. Code 702, 703, and 720
    through 726.
     
    n) Liquid hazardous wastes containing PCBs at concentrations greater than or equal to
    500 ppm are not eligible for an adjusted standard under this Section.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.107 Testing, Tracking, and Recordkeeping Requirements for Generators,
    Treaters, and Disposal Facilities
     
    a) Requirements for generators.
     
    1) A generator of a hazardous waste must determine if the waste has to be
    treated before it can be land disposed. This is done by determining if the
    hazardous waste meets the treatment standards in Section 728.140,
    728.145, or 728.149. This determination can be made in either of two
    ways: testing the waste or using knowledge of the waste. If the generator
    tests the waste, testing determines the total concentration of hazardous
    constituents or the concentration of hazardous constituents in an extract of
    the waste obtained using SW-846 Method 1311 (the Toxicity

     
    791
    Characteristic Leaching Procedure), in “Test Methods for Evaluating
    Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(a), depending on whether the treatment standard for the waste is
    expressed as a total concentration or concentration of hazardous
    constituent in the waste extract. In addition, some hazardous wastes must
    be treated by particular treatment methods before they can be land
    disposed and some soils are contaminated by such hazardous wastes.
    These treatment standards are also found in Section 728.140 and Table T
    of this Part, and are described in detail in Table C of this Part. These
    wastes and soils contaminated with such wastes do not need to be tested
    (however, if they are in a waste mixture, other wastes with concentration
    level treatment standards must be tested). If a generator determines that it
    is managing a waste or soil contaminated with a waste that displays a
    hazardous characteristic of ignitability, corrosivity, reactivity, or toxicity,
    the generator must comply with the special requirements of Section
    728.109 in addition to any applicable requirements in this Section.
     
    2) If the waste or contaminated soil does not meet the treatment standard, the
    generator must send a one-time written notice to each treatment or storage
    facility receiving the waste with the initial shipment of waste to each
    treatment or storage facility, and the generator must place a copy of the
    one-time notice in the file. The notice must include the information in
    column “728.107(a)(2)” of the Generator Paperwork Requirements Table
    in Table I of this Part. No further notification is necessary until such time
    that the waste or facility changes, in which case a new notification must be
    sent and a copy placed in the generator’s file.
     
    A) For contaminated soil, the following certification statement should
    be included, signed by an authorized representative:
     
    I certify under penalty of law that I personally have
    examined this contaminated soil and it (does/does not)
    contain listed hazardous waste and (does/does not) exhibit
    a characteristic of hazardous waste and requires treatment
    to meet the soil treatment standards as provided by 35 Ill.
    Adm. Code 728.149(c).
     
    B) This subsection (a)(2)(B) corresponds with 40 CFR 268.7(a)(2)(ii),
    which is marked “reserved” by USEPA. This statement maintains
    structural consistency with USEPA rules.
     
    3) If the waste or contaminated soil meets the treatment standard at the
    original point of generation, the waste generator must do the following:
     
    A) With the initial shipment of waste to each treatment, storage, or

     
    792
    disposal facility, the generator must send a one-time written notice
    to each treatment, storage, or disposal facility receiving the waste,
    and place a copy in its own file. The notice must include the
    information indicated in column “728.107(a)(3)” of the Generator
    Paperwork Requirements Table in Table I of this Part and the
    following certification statement, signed by an authorized
    representative:
     
    I certify under penalty of law that I personally have
    examined and am familiar with the waste through analysis
    and testing or through knowledge of the waste to support
    this certification that the waste complies with the treatment
    standards specified in Subpart D of 35 Ill. Adm. Code 728.
    I believe that the information I submitted is true, accurate,
    and complete. I am aware that there are significant
    penalties for submitting a false certification, including the
    possibility of a fine and imprisonment.
     
    B) For contaminated soil, with the initial shipment of wastes to each
    treatment, storage, or disposal facility, the generator must send a
    one-time written notice to each facility receiving the waste and
    place a copy in the file. The notice must include the information in
    the column headed “(a)(3)” in Table I of this Part.
     
    C) If the waste changes, the generator must send a new notice and
    certification to the receiving facility and place a copy in its files.
    A generator of hazardous debris excluded from the definition of
    hazardous waste under 35 Ill. Adm. Code 721.103(f) is not subject
    to these requirements.
     
    4) For reporting, tracking and recordkeeping when exceptions allow certain
    wastes or contaminated soil that do not meet the treatment standards to be
    land disposed, there are certain exemptions from the requirement that
    hazardous wastes or contaminated soil meet treatment standards before
    they can be land disposed. These include, but are not limited to, case-by-
    case extensions under Section 728.105, disposal in a no-migration unit
    under Section 728.106, or a national capacity variance or case-by-case
    capacity variance under Subpart C of this Part. If a generator’s waste is so
    exempt, then with the initial shipment of waste, the generator must send a
    one-time written notice to each land disposal facility receiving the waste.
    The notice must include the information indicated in column
    “728.107(a)(4)” of the Generator Paperwork Requirements Table in Table
    I of this Part. If the waste changes, the generator must send a new notice
    to the receiving facility, and place a copy in its file.
     
    5) If a generator is managing and treating prohibited waste or contaminated

     
    793
    soil in tanks, containers, or containment buildings regulated under 35 Ill.
    Adm. Code 722.134 to meet applicable LDR treatment standards found at
    Section 728.140, the generator must develop and follow a written waste
    analysis plan that describes the procedures it will carry out to comply with
    the treatment standards. (Generators treating hazardous debris under the
    alternative treatment standards of Table F of this Part, however, are not
    subject to these waste analysis requirements.) The plan must be kept on
    site in the generator’s records, and the following requirements must be
    met:
     
    A) The waste analysis plan must be based on a detailed chemical and
    physical analysis of a representative sample of the prohibited
    wastes being treated, and contain all information necessary to treat
    the wastes in accordance with the requirements of this Part,
    including the selected testing frequency;
     
    B) Such plan must be kept in the facility’s on-site files and made
    available to inspectors; and
     
    C) Wastes shipped off-site pursuant to this subsection (a)(5) of this
    Section must comply with the notification requirements of
    subsection (a)(3) of this Section.
     
    6) If a generator determines that the waste or contaminated soil is restricted
    based solely on its knowledge of the waste, all supporting data used to
    make this determination must be retained on-site in the generator’s files.
    If a generator determines that the waste is restricted based on testing this
    waste or an extract developed using SW-846 Method 1311 (the Toxicity
    Characteristic Leaching Procedure), incorporated by reference in 35 Ill.
    Adm. Code 720.111, in “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods,” USEPA publication number EPA530/SW-
    846, all waste analysis data must be retained on-site in the generator’s
    files.
     
    7) If a generator determines that it is managing a prohibited waste that is
    excluded from the definition of hazardous or solid waste or which is
    exempt from Subtitle C regulation under 35 Ill. Adm. Code 721.102
    through 721.106 subsequent to the point of generation (including
    deactivated characteristic hazardous wastes that are managed in
    wastewater treatment systems subject to the CWA, as specified at 35 Ill.
    Adm. Code 721.104(a)(2); that are CWA-equivalent; or that are managed
    in an underground injection well regulated under 35 Ill. Adm. Code 730),
    the generator must place a one-time notice stating such generation,
    subsequent exclusion from the definition of hazardous or solid waste or
    exemption from RCRA Subtitle C regulation, and the disposition of the
    waste in the generating facility’s on-site file.

     
    794
     
    8) A generator must retain a copy of all notices, certifications, waste analysis
    data, and other documentation produced pursuant to this Section on-site
    for at least three years from the date that the waste that is the subject of
    such documentation was last sent to on-site or off-site treatment, storage,
    or disposal. The three-year record retention period is automatically
    extended during the course of any unresolved enforcement action
    regarding the regulated activity or as requested by the Agency. The
    requirements of this subsection (a)(8) apply to solid wastes even when the
    hazardous characteristic is removed prior to disposal, or when the waste is
    excluded from the definition of hazardous or solid waste under 35 Ill.
    Adm. Code 721.102 through 721.106, or exempted from RCRA Subtitle C
    regulation, subsequent to the point of generation.
     
    9) If a generator is managing a lab pack containing hazardous wastes and
    wishes to use the alternative treatment standard for lab packs found at
    Section 728.142(c), the generator must fulfill the following conditions:
     
    A) With the initial shipment of waste to a treatment facility, the
    generator must submit a notice that provides the information in
    column “Section 728.107(a)(9)” in the Generator Paperwork
    Requirements Table of Table I of this Part and the following
    certification. The certification, which must be signed by an
    authorized representative and must be placed in the generator’s
    files, must say the following:
     
    I certify under penalty of law that I personally have
    examined and am familiar with the waste and that the lab
    pack contains only wastes that have not been excluded
    under Appendix D to 35 Ill. Adm. Code 728 and that this
    lab pack will be sent to a combustion facility in compliance
    with the alternative treatment standards for lab packs at 35
    Ill. Adm. Code 728.142(c). I am aware that there are
    significant penalties for submitting a false certification,
    including the possibility of fine or imprisonment.
     
    B) No further notification is necessary until such time as the wastes in
    the lab pack change, or the receiving facility changes, in which
    case a new notice and certification must be sent and a copy placed
    in the generator’s file.
     
    C) If the lab pack contains characteristic hazardous wastes (D001-
    D043), underlying hazardous constituents (as defined in Section
    728.102(i)) need not be determined.
     
    D) The generator must also comply with the requirements in

     
    795
    subsections (a)(6) and (a)(7) of this Section.
     
    10) Small quantity generators with tolling agreements pursuant to 35 Ill. Adm.
    Code 722.120(e) must comply with the applicable notification and
    certification requirements of subsection (a) of this Section for the initial
    shipment of the waste subject to the agreement. Such generators must
    retain on-site a copy of the notification and certification, together with the
    tolling agreement, for at least three years after termination or expiration of
    the agreement. The three-year record retention period is automatically
    extended during the course of any unresolved enforcement action
    regarding the regulated activity or as requested by the Agency.
     
    b) The owner or operator of a treatment facility must test its wastes according to the
    frequency specified in its waste analysis plan, as required by 35 Ill. Adm. Code
    724.113 (for permitted TSDs) or 725.113 (for interim status facilities). Such
    testing must be performed as provided in subsections (b)(1), (b)(2), and (b)(3) of
    this Section.
     
    1) For wastes or contaminated soil with treatment standards expressed in the
    waste extract (TCLP), the owner or operator of the treatment facility must
    test an extract of the treatment residues using SW-846 Method 1311 (the
    Toxicity Characteristic Leaching Procedure), incorporated by reference in
    35 Ill. Adm. Code 720.111, in “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods,” USEPA publication number EPA530/SW-
    846, to assure that the treatment residues extract meets the applicable
    treatment standards.
     
    2) For wastes or contaminated soil with treatment standards expressed as
    concentrations in the waste, the owner or operator of the treatment facility
    must test the treatment residues (not an extract of such residues) to assure
    that the treatment residues meet the applicable treatment standards.
     
    3) A one-time notice must be sent with the initial shipment of waste or
    contaminated soil to the land disposal facility. A copy of the notice must
    be placed in the treatment facility’s file.
     
    A) No further notification is necessary until such time that the waste
    or receiving facility changes, in which case a new notice must be
    sent and a copy placed in the treatment facility’s file.
     
    B) The one-time notice must include the following requirements:
     
    i) USEPA hazardous waste number and manifest number of
    first shipment;
     
    ii) The waste is subject to the LDRs. The constituents of

     
    796
    concern for F001 through F005 and F039 waste and
    underlying hazardous constituents in characteristic wastes,
    unless the waste will be treated and monitored for all
    constituents. If all constituents will be treated and
    monitored, there is no need to put them all on the LDR
    notice;
     
    iii) The notice must include the applicable wastewater/
    nonwastewater category (see Section 728.102(d) and (f))
    and subdivisions made within a waste code based on waste-
    specific criteria (such as D003 reactive cyanide);
     
    iv) Waste analysis data (when available);
     
    v) For contaminated soil subject to LDRs as provided in
    Section 728.149(a), the constituents subject to treatment as
    described in Section 728.149(d) and the following
    statement, “this contaminated soil (does/does not) contain
    listed hazardous waste and (does/does not) exhibit a
    characteristic of hazardous waste and (is subject
    to/complies with) the soil treatment standards as provided
    by Section 728.149(c)”; and
     
    vi) A certification is needed (see applicable Section for exact
    wording).
     
    4) The owner or operator of a treatment facility must submit a certification
    signed by an authorized representative with the initial shipment of waste
    or treatment residue of a restricted waste to the land disposal facility. The
    certification must state as follows:
     
    I certify under penalty of law that I have personally examined and
    am familiar with the treatment technology and operation of the
    treatment process used to support this certification. Based on my
    inquiry of those individuals immediately responsible for obtaining
    this information, I believe that the treatment process has been
    operated and maintained properly so as to comply with the
    treatment standards specified in 35 Ill. Adm. Code 728.140
    without impermissible dilution of the prohibited waste. I am aware
    there are significant penalties for submitting a false certification,
    including the possibility of fine and imprisonment.
     
    A certification is also necessary for contaminated soil and it must state as
    follows:
     
    I certify under penalty of law that I have personally examined and

     
    797
    am familiar with the treatment technology and operation of the
    treatment process used to support this certification and believe that
    it has been maintained and operated properly so as to comply with
    treatment standards specified in 35 Ill. Adm. Code 728.149
    without impermissible dilution of the prohibited wastes. I am
    aware there are significant penalties for submitting a false
    certification, including the possibility of fine and imprisonment.
     
    A) A copy of the certification must be placed in the treatment
    facility’s on-site files. If the waste or treatment residue changes,
    or the receiving facility changes, a new certification must be sent
    to the receiving facility, and a copy placed in the treatment
    facility’s file.
     
    B) Debris excluded from the definition of hazardous waste under 35
    Ill. Adm. Code 721.103(e) (i.e., debris treated by an extraction or
    destruction technology listed in Table F of this Part and debris that
    the Agency has determined does not contain hazardous waste) is
    subject to the notification and certification requirements of
    subsection (d) of this Section rather than the certification
    requirements of this subsection (b)(4).
     
    C) For wastes with organic constituents having treatment standards
    expressed as concentration levels, if compliance with the treatment
    standards is based in part or in whole on the analytical detection
    limit alternative specified in Section 728.140(d), the certification
    must be signed by an authorized representative and must state as
    follows:
     
    I certify under penalty of law that I have personally
    examined and am familiar with the treatment technology
    and operation of the treatment process used to support this
    certification. Based on my inquiry of those individuals
    immediately responsible for obtaining this information, I
    believe that the nonwastewater organic constituents have
    been treated by combustion units as specified in Table C to
    35 Ill. Adm. Code 728. I have been unable to detect the
    nonwastewater organic constituents, despite having used
    best good faith efforts to analyze for such constituents. I
    am aware that there are significant penalties for submitting
    a false certification, including the possibility of fine and
    imprisonment.
     
    D) For characteristic wastes that are subject to the treatment standards
    in Section 728.140 and Table T of this Part (other than those
    expressed as a required method of treatment) or Section 728.149

     
    798
    and which contain underlying hazardous constituents, as defined in
    Section 728.102(i); if these wastes are treated on-site to remove
    the hazardous characteristic; and that are then sent off-site for
    treatment of underlying hazardous constituents, the certification
    must state as follows:
     
    I certify under penalty of law that the waste has been
    treated in accordance with the requirements of 35 Ill. Adm.
    Code 728.140 and Table T of Section 728.149 of that Part
    to remove the hazardous characteristic. This
    decharacterized waste contains underlying hazardous
    constituents that require further treatment to meet treatment
    standards. I am aware that there are significant penalties
    for submitting a false certification, including the possibility
    of fine and imprisonment.
     
    E) For characteristic wastes that contain underlying hazardous
    constituents, as defined in Section 728.102(i), that are treated on-
    site to remove the hazardous characteristic and to treat underlying
    hazardous constituents to levels in Section 728.148 and Table U of
    this Part universal treatment standards, the certification must state
    as follows:
     
    I certify under penalty of law that the waste has been
    treated in accordance with the requirements of 35 Ill. Adm.
    Code 728.140 and Table T of that Part to remove the
    hazardous characteristic and that underlying hazardous
    constituents, as defined in 35 Ill. Adm. Code 728.102(i),
    have been treated on-site to meet the universal treatment
    standards of 35 Ill. Adm. Code 728.148 and Table U of that
    Part. I am aware that there are significant penalties for
    submitting a false certification, including the possibility of
    fine and imprisonment.
     
    5) If the waste or treatment residue will be further managed at a different
    treatment, storage, or disposal facility, the treatment, storage, or disposal
    facility that sends the waste or treatment residue off-site must comply with
    the notice and certification requirements applicable to generators under
    this Section.
     
    6) Where the wastes are recyclable materials used in a manner constituting
    disposal subject to the provisions of 35 Ill. Adm. Code 726.120(b),
    regarding treatment standards and prohibition levels, the owner or
    operator of a treatment facility (i.e., the recycler) is not required to notify
    the receiving facility pursuant to subsection (b)(3) of this Section. With
    each shipment of such wastes the owner or operator of the recycling

     
    799
    facility must submit a certification described in subsection (b)(4) of this
    Section and a notice that includes the information listed in subsection
    (b)(3) of this Section (except the manifest number) to the Agency. The
    recycling facility also must keep records of the name and location of each
    entity receiving the hazardous waste-derived product.
     
    c) Except where the owner or operator is disposing of any waste that is a recyclable
    material used in a manner constituting disposal pursuant to 35 Ill. Adm. Code
    726.120(b), the owner or operator of any land disposal facility disposing any
    waste subject to restrictions under this Part shall do the following:
     
    1) Maintain in its files copies of the notice and certifications specified in
    subsection (a) or (b) of this Section.
     
    2) Test the waste or an extract of the waste or treatment residue developed
    using SW-846 Method 1311 (the Toxicity Characteristic Leaching
    Procedure), incorporated by reference in 35 Ill. Adm. Code 720.111, in
    “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”
    USEPA publication number EPA530/SW-846, to assure that the waste or
    treatment residue is in compliance with the applicable treatment standards
    set forth in Subpart D of this Part. Such testing must be performed
    according to the frequency specified in the facility’s waste analysis plan as
    required by 35 Ill. Adm. Code 724.113 or 35 Ill. Adm. Code 725.113.
     
    3) Where the owner or operator is disposing of any waste that is subject to
    the prohibitions under Section 728.133(f) but not subject to the
    prohibitions set forth in Section 728.132, the owner or operator must
    ensure that such waste is the subject of a certification according to the
    requirements of Section 728.108 prior to disposal in a landfill or surface
    impoundment unit, and that such disposal is in accordance with the
    requirements of Section 728.105(h)(2). The same requirement applies to
    any waste that is subject to the prohibitions under Section 728.133(f) and
    also is subject to the statutory prohibitions in the codified prohibitions in
    Section 728.139 or Section 728.132.
     
    4) Where the owner or operator is disposing of any waste that is a recyclable
    material used in a manner constituting disposal subject to the provisions of
    35 Ill. Adm. Code 726.120(b), the owner or operator is not subject to
    subsections (c)(1) through (c)(3) of this Section with respect to such
    waste.
     
    d) A generator or treater that first claims that hazardous debris is excluded from the
    definition of hazardous waste under 35 Ill. Adm. Code 721.103(e) (i.e., debris
    treated by an extraction or destruction technology provided by Table F of this
    Part, and debris that has been delisted) is subject to the following notification and
    certification requirements:

     
    800
     
    1) A one-time notification must be submitted to the Agency including the
    following information:
     
    A) The name and address of the RCRA Subtitle D (municipal solid
    waste landfill) facility receiving the treated debris;
     
    B) A description of the hazardous debris as initially generated,
    including the applicable USEPA hazardous waste numbers; and
     
    C) For debris excluded under 35 Ill. Adm. Code 721.103(e)(1), the
    technology from Table F of this Part used to treat the debris.
     
    2) The notification must be updated if the debris is shipped to a different
    facility and, for debris excluded under 35 Ill. Adm. Code 721.102(e)(1), if
    a different type of debris is treated or if a different technology is used to
    treat the debris.
     
    3) For debris excluded under 35 Ill. Adm. Code 721.103(e)(1), the owner or
    operator of the treatment facility must document and certify compliance
    with the treatment standards of Table F of this Part, as follows:
     
    A) Records must be kept of all inspections, evaluations, and analyses
    of treated debris that are made to determine compliance with the
    treatment standards;
     
    B) Records must be kept of any data or information the treater obtains
    during treatment of the debris that identifies key operating
    parameters of the treatment unit; and
     
    C) For each shipment of treated debris, a certification of compliance
    with the treatment standards must be signed by an authorized
    representative and placed in the facility’s files. The certification
    must state as follows:
     
    I certify under penalty of law that the debris has been
    treated in accordance with the requirements of 35 Ill. Adm.
    Code 728.145. I am aware that there are significant
    penalties for making a false certification, including the
    possibility of fine and imprisonment.
     
    e) A generator or treater that first receives a determination from USEPA or the
    Agency that a given contaminated soil subject to LDRs, as provided in Section
    728.149(a), no longer contains a listed hazardous waste and a generator or treater
    that first determines that a contaminated soil subject to LDRs, as provided in
    Section 728.149(a), no longer exhibits a characteristic of hazardous waste must

     
    801
    do the following:
     
    1) Prepare a one-time only documentation of these determinations including
    all supporting information; and
     
    2) Maintain that information in the facility files and other records for a
    minimum of three years.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART B: SCHEDULE FOR LAND DISPOSAL PROHIBITION AND
    ESTABLISHMENT OF TREATMENT STANDARDS
     
    Section 728.114 Surface Impoundment Exemptions
     
    a) This Section defines additional circumstances under which an otherwise prohibited
    waste may continue to be placed in a surface impoundment.
     
    b) Wastes that are newly identified or listed by USEPA persuant to Section 3001 of
    RCRA (42 USC § 6921) after November 8, 1984 and which are stored in a surface
    impoundment that is newly subject to subtitle C of RCRA (42 USC § 6921 et seq.)
    as a result of the additional identification or listing may continue to be stored in the
    surface impoundment for 48 months after the promulgation of the additional listing
    or characteristic, notwithstanding the fact that the waste is otherwise prohibited from
    land disposal, provided that the surface impoundment is in compliance with the
    requirements of Subpart F of 35 Ill. Adm. Code 725 within 12 months after
    promulgation of the new listing or characteristic.
     
    c) Wastes that are newly identified or listed by USEPA under Section 3001 of RCRA
    (42 U.S.C. § 6921) after November 8, 1984 and which are treated in a surface
    impoundment that is newly subject to Subtitle C of RCRA (42 U.S.C. § 6921 et seq.)
    as a result of the additional identification or listing may continue to be treated in that
    surface impoundment, notwithstanding the fact that the waste is otherwise prohibited
    from land disposal, provided that the surface impoundment is in compliance with the
    requirements of Subpart F of 35 Ill. Adm. Code 725 within 12 months after the
    promulgation of the new listing or characteristic. In addition, if the surface
    impoundment continues to treat hazardous waste after 48 months from promulgation
    of the additional listing or characteristic, it must then be in compliance with Section
    728.104.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    802
    SUBPART C: PROHIBITION ON LAND DISPOSAL
     
    Section 728.120 Waste-Specific Prohibitions: Dyes and Pigments Production
    Wastes
     
    a) The waste specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste
    number K181, soil and debris contaminated with this waste, radioactive wastes
    mixed with this waste, and soil and debris contaminated with radioactive wastes
    mixed with this waste are prohibited from land disposal.
     
    b) The requirements of subsection (a) of this Section do not apply if any of the
    following conditions are fulfilled:
     
    1) The wastes meet the applicable treatment standards specified in Subpart D
    of this Part;
     
    2) A no-migration exemption has been granted from a prohibition pursuant to
    a petition under Section 728.106, in which case the requirements of
    subsection (a) of this Section do not apply with respect to those wastes
    and units covered by the petition;
     
    3) The wastes meet the applicable treatment standards established pursuant
    to a petition granted under Section 728.144;
     
    4) Hazardous debris has met the treatment standards in Section 728.140 or
    the alternative treatment standards in Section 728.145; or
     
    5) USEPA has granted an extension to the effective date of a prohibition
    pursuant to 40 CFR 268.5, in which case the requirements of subsection
    (a) of this Section do not apply with respect to these wastes covered by the
    extension.
     
    c) To determine whether a hazardous waste identified in this Section exceeds the
    applicable treatment standards specified in Section 728.140, the initial generator
    must test a sample of the waste extract or the entire waste, depending on whether
    the treatment standards are expressed as concentrations in the waste extract of the
    waste, or the generator may use knowledge of the waste. If the waste contains
    regulated constituents in excess of the applicable levels set forth in Subpart D of
    this Part, the waste is prohibited from land disposal, and all requirements of this
    Part apply, except as otherwise specified.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.130 Waste-Specific Prohibitions: Wood Preserving Wastes
     
    a) The following wastes are prohibited from land disposal: the wastes specified in

     
    803
    35 Ill. Adm. Code 721 as USEPA hazardous waste numbers F032, F034, and
    F035.
     
    b) The following wastes are prohibited from land disposal: soil and debris
    contaminated with the wastes specified in 35 Ill. Adm. Code 721 as F032, F034,
    F035; and radioactive wastes mixed with USEPA hazardous waste numbers F032,
    F034, and F035.
     
    c) This subsection (c) corresponds with 40 CFR 268.30(c), which expired by its own
    terms on May 12, 1999. This statement maintains structural consistency with the
    corresponding federal regulations.
     
    d) The requirements of subsections (a) and (b) of this Section do not apply if any of
    the following conditions is fulfilled:
     
    1) The wastes meet the applicable treatment standards specified in Subpart D
    of this Part;
     
    2) A person has been granted an exemption from a prohibition pursuant to a
    petition under Section 728.106, with respect to those wastes and units
    covered by the petition;
     
    3) The wastes meet the applicable alternate treatment standards established
    pursuant to a petition granted under Section 728.144; or
     
    4) A person has been granted an extension to the effective date of a
    prohibition by USEPA pursuant to federal 40 CFR 268.5 (see Section
    728.105), with respect to those wastes covered by the extension.
     
    e) To determine whether a hazardous waste identified in this Section exceeds the
    applicable treatment standards specified in Section 728.140 and Table T to this
    Part, the initial generator must test a sample of the waste extract or the entire
    waste, depending on whether the treatment standards are expressed as
    concentrations in the waste extract or the waste, or the generator may use
    knowledge of the waste. If the waste contains constituents in excess of the
    applicable universal treatment standard levels of Section 728.148 and Table U to
    this Part, the waste is prohibited from land disposal and all requirements of Part
    728 are applicable, except as otherwise specified.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.134 Waste-Specific Prohibitions: Toxicity Characteristic Metal Wastes
     
    a) The following wastes are prohibited from land disposal: the wastes specified in
    35 Ill. Adm. Code 721 as USEPA hazardous waste numbers D004 through D011
    that are newly identified (i.e., wastes, soil, or debris identified as hazardous by the

     
    804
    Toxic Characteristic Leaching Procedure but not the Extraction Procedure), and
    waste, soil, or debris from mineral processing operations that is identified as
    hazardous by the specifications at 35 Ill. Adm. Code 721.
     
    b) The following waste is prohibited from land disposal: slag from secondary lead
    smelting that exhibits the characteristic of toxicity due to the presence of one or
    more metals.
     
    c) The following wastes are prohibited from land disposal: newly identified
    characteristic wastes from elemental phosphorus processing; radioactive wastes
    mixed with USEPA hazardous waste numbers D004 through D011 wastes that are
    newly identified (i.e., wastes, soil, or debris identified as hazardous by the Toxic
    Characteristic Leaching Procedure but not the Extraction Procedure); or mixed
    with newly identified characteristic mineral processing wastes, soil, or debris.
     
    d) This subsection (d) corresponds with 40 CFR 269.34(d), which expired by its own
    terms on May 26, 2000. This statement maintains structural consistency with the
    corresponding federal regulations.
     
    e) The requirements of subsections (a) and (b) of this Section do not apply if any of
    the following applies to the waste:
     
    1) The wastes meet the applicable treatment standards specified in Subpart D
    of this Part;
     
    2) The Board has granted an exemption from a prohibition pursuant to a
    petition under Section 728.106, with respect to those wastes and units
    covered by the petition;
     
    3) The wastes meet the applicable alternate treatment standards established
    pursuant to a petition granted under Section 728.144; or
     
    4) USEPA has granted an extension to the effective date of a prohibition
    pursuant to federal 40 CFR 268.5, with respect to those wastes covered by
    the extension.
     
    f) To determine whether a hazardous waste identified in this Section exceeds the
    applicable treatment standards specified in Section 728.140 and Table T of this
    Part, the initial generator must test a sample of the waste extract or the entire
    waste, depending on whether the treatment standards are expressed as
    concentrations in the waste extract or the waste, or the generator may use
    knowledge of the waste. If the waste contains constituents (including underlying
    hazardous constituents in characteristic wastes) in excess of the applicable
    universal treatment standard levels of Section 728.148 and Table U of this Part,
    the waste is prohibited from land disposal, and all requirements of this Part are
    applicable, except as otherwise specified.

     
    805
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.135 Waste-Specific Prohibitions: Petroleum Refining Wastes
     
    a) The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous wastes
    numbers K169, K170, K171, and K172; soils and debris contaminated with these
    wastes; radioactive wastes mixed with these hazardous wastes; and soils and
    debris contaminated with these radioactive mixed wastes are prohibited from land
    disposal.
     
    b) The requirements of subsection (a) of this Section do not apply if any of the
    following applies to the waste:
     
    1) The wastes meet the applicable treatment standards specified in Subpart D
    of this Part;
     
    2) The Board has granted an adjusted standard that exempts waste from a
    prohibition pursuant to Section 728.106, with respect to those wastes and
    units covered by the adjusted standard;
     
    3) The wastes meet an adjusted standard from an applicable treatment
    standard granted under Section 728.144;
     
    4) The waste is hazardous debris that has met the treatment standards set
    forth in Section 728.140 and Table T of this Part or the alternative
    treatment standards in Section 728.145; or
     
    5) USEPA has granted an extension to the effective date of a prohibition
    pursuant to federal 40 CFR 268.5, with respect to these wastes covered by
    the extension.
     
    c) To determine whether a hazardous waste identified in this Section exceeds the
    applicable treatment standards specified in Section 728.140, the initial generator
    must test a sample of the waste extract or the entire waste, depending on whether
    the treatment standards are expressed as concentrations in the waste extract or the
    waste, or the generator may use knowledge of the waste. If the waste contains
    constituents in excess of the applicable universal treatment standard levels of
    Section 728.148 and Table U of this Part, the waste is prohibited from land
    disposal, and all requirements of this Part are applicable, except as otherwise
    specified.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    806
    SUBPART D: TREATMENT STANDARDS
     
    Section 728.140 Applicability of Treatment Standards
     
    a) A prohibited waste identified in Table T of this Part, “Treatment Standards for
    Hazardous Wastes,” may be land disposed only if it meets the requirements found
    in that Table. For each waste, Table T of this Part identifies one of three types of
    treatment standard requirements:
     
    1) All hazardous constituents in the waste or in the treatment residue must be
    at or below the values found in Table T of this Part for that waste (total
    waste standards);
     
    2) The hazardous constituents in the extract of the waste or in the extract of
    the treatment residue must be at or below the values found in Table T of
    this Part (waste extract standards); or
     
    3) The waste must be treated using the technology specified in Table T of
    this Part (technology standard), which is described in detail in Table C of
    this Part, “Technology Codes and Description of Technology-Based
    Standards.”
     
    b) For wastewaters, compliance with concentration level standards is based on
    maximums for any one day, except for D004 through D011 wastes for which the
    previously promulgated treatment standards based on grab samples remain in
    effect. For all nonwastewaters, compliance with concentration level standards is
    based on grab sampling. For wastes covered by the waste extract standards, the
    test Method 1311, the (Toxicity Characteristic Leaching Procedure), found in
    “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    Publication publication number EPA-530/SW-846, incorporated by reference in
    35 Ill. Adm. Code 720.111 720.111(a), must be used to measure compliance. An
    exception is made for D004 and D008, for which either of two test methods may
    be used: Method 1311 or Method 1310B, the (Extraction Procedure Toxicity
    Test), found in “Test Methods for Evaluating Solid Waste, Physical/Chemical
    Methods,” USEPA Publication publication number EPA-530/SW-846,
    incorporated by reference in 35 Ill. Adm. Code 720.111. For wastes covered by a
    technology standard, the wastes may be land disposed after being treated using
    that specified technology or an equivalent treatment technology approved by the
    Agency pursuant to Section 728.142(b).
     
    c) When wastes with differing treatment standards for a constituent of concern are
    combined for purposes of treatment, the treatment residue must meet the lowest
    treatment standard for the constituent of concern.
     
    d) Notwithstanding the prohibitions specified in subsection (a) of this Section,
    treatment and disposal facilities may demonstrate (and certify pursuant to Section

     
    807
    728.107(b)(5)) compliance with the treatment standards for organic constituents
    specified by a footnote in Table T of this Part, provided the following conditions
    are satisfied:
     
    1) The treatment standards for the organic constituents were established
    based on incineration in units operated in accordance with the technical
    requirements of Subpart O of 35 Ill. Adm. Code 724, or based on
    combustion in fuel substitution units operating in accordance with
    applicable technical requirements;
     
    2) The treatment or disposal facility has used the methods referenced in
    subsection (d)(1) of this Section to treat the organic constituents; and
     
    3) The treatment or disposal facility may demonstrate compliance with
    organic constituents if good-faith analytical efforts achieve detection
    limits for the regulated organic constituents that do not exceed the
    treatment standards specified in this Section and Table T of this Part by an
    order of magnitude.
     
    e) For a characteristic waste (USEPA hazardous waste number D001 through D043)
    that is subject to treatment standards set forth in Table T of this Part, “Treatment
    Standards for Hazardous Wastes,” and the waste is not managed in a wastewater
    treatment system that is either regulated under the Clean Water Act (CWA) or one
    that is CWA-equivalent or the waste is injected into a Class I non-hazardous deep
    injection well, all underlying hazardous constituents (as defined in Section
    728.102) must meet the universal treatment standards, set forth in Table U of this
    Part prior to land disposal, as defined in Section 728.102.
     
    f) The treatment standards for USEPA hazardous waste numbers F001 through F005
    nonwastewater constituents carbon disulfide, cyclohexanone, or methanol apply
    to wastes that contain only one, two, or three of these constituents. Compliance is
    measured for these constituents in the waste extract from test Method 1311, the
    (Toxicity Characteristic Leaching Procedure), found in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA Publication
    publication number EPA530/SW-846, incorporated by reference in 35 Ill. Adm.
    Code 720.111 720.111(a). If the waste contains any of these three constituents
    along with any of the other 25 constituents found in USEPA hazardous waste
    numbers F001 through F005, then compliance with treatment standards for carbon
    disulfide, cyclohexanone, or methanol are not required.
     
    g) This subsection (g) corresponds with 40 CFR 268.40(g), which expired by its own
    terms on March 4, 1999. This statement maintains structural consistency with the
    corresponding federal rules.
     
    h) Prohibited USEPA hazardous waste numbers D004 through D011, mixed
    radioactive wastes, and mixed radioactive listed wastes containing metal

     
    808
    constituents that were previously treated by stabilization to the treatment
    standards in effect at that time and then put into storage do not have to be re-
    treated to meet treatment standards in this Section prior to land disposal.
     
    i) This subsection (i) corresponds with 40 CFR 268.40(i), which USEPA has removed
    and marked “reserved.” This statement maintains structural consistency with the
    corresponding federal regulations.
     
    j) The treatment standards for the wastes specified in 35 Ill. Adm. Code 721.133 as
    USEPA hazardous waste numbers P185, P191, P192, P197, U364, U394, and U395
    may be satisfied by either meeting the constituent concentrations presented in Table
    T of this Part, “Treatment Standards for Hazardous Wastes,” or by treating the
    waste by the following technologies: combustion, as defined by the technology
    code CMBST at Table C, for nonwastewaters; biodegradation, as defined by the
    technology code BIODG; carbon adsorption, as defined by the technology code
    CARBN; chemical oxidation, as defined by the technology code CHOXD; or
    combustion, as defined as technology code CMBST at Table C, for wastewaters.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.142 Treatment Standards Expressed as Specified Technologies
     
    a) The following wastes listed in Table T of this Part, “Treatment Standards for
    Hazardous Wastes,” for which standards are expressed as a treatment method rather
    than as a concentration level, must be treated using the technology or technologies
    specified in Table C of this Part.
     
    1) Liquid hazardous wastes containing PCBs at concentrations greater than or
    equal to 50 ppm but less than 500 ppm must be incinerated in accordance
    with the technical requirements of 40 CFR 761.70 (Incineration),
    incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(b), or
    burned in high efficiency boilers in accordance with the technical
    requirements of 40 CFR 761.60 (Disposal Requirements), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b). Liquid hazardous wastes
    containing PCBs at concentrations greater than or equal to 500 ppm must be
    incinerated in accordance with the technical requirements of 40 CFR 761.70.
    Thermal treatment in accordance with this Section must be in compliance
    with applicable regulations in 35 Ill. Adm. Code 724, 725, and 726.
     
    2) Nonliquid hazardous wastes containing halogenated organic compounds
    (HOCs) in total concentrations greater than or equal to 1000 1,000 mg/kg and
    liquid HOC-containing wastes that are prohibited under Section
    728.132(e)(1) must be incinerated in accordance with the requirements of
    Subpart O of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725.
    These treatment standards do not apply where the waste is subject to a
    treatment standard codified in Subpart C of this Part for a specific HOC

     
    809
    (such as a hazardous waste chlorinated solvent for which a treatment
    standard is established under Section 728.141(a)).
     
    3) A mixture consisting of wastewater, the discharge of which is subject to
    regulation under 35 Ill. Adm. Code 309 or 310, and de minimis losses of
    materials from manufacturing operations in which these materials are used as
    raw materials or are produced as products in the manufacturing process that
    meet the criteria of the D001 ignitable liquids containing greater than 10
    percent total organic constituents (TOC) subcategory are subject to the
    DEACT treatment standard described in Table C of this Part. For purposes
    of this subsection (a)(3), “de minimis losses” include the following:
     
    A) Those from normal material handling operations (e.g., spills from the
    unloading or transfer of materials from bins or other containers, or
    leaks from pipes, valves, or other devices used to transfer materials);
     
    B) Minor leaks from process equipment, storage tanks, or containers;
     
    C) Leaks from well-maintained pump packings and seals;
     
    D) Sample purgings; and
     
    E) Relief device discharges.
     
    b) Any person may submit an application to the Agency demonstrating that an
    alternative treatment method can achieve a level of performance equivalent to that
    achievable by methods specified in subsections (a), (c), and (d) of this Section for
    wastes or specified in Table F of this Part for hazardous debris. The applicant must
    submit information demonstrating that the applicant’s treatment method is in
    compliance with federal and state requirements, including this Part; 35 Ill. Adm.
    Code 709, 724, 725, 726, and 729; and Sections 22.6 and 39(h) of the Environmental
    Protection Act [415 ILCS 5/22.6 and 39(h)] and that the treatment method is
    protective of human health and the environment. On the basis of such information
    and any other available information, the Agency must approve the use of the
    alternative treatment method if the Agency finds that the alternative treatment
    method provides a measure of performance equivalent to that achieved by methods
    specified in subsections (a), (c), and (d) of this Section and in Table F of this Part,
    for hazardous debris. Any approval must be stated in writing and may contain such
    provisions and conditions as the Agency determines to be appropriate. The person to
    whom such approval is issued must comply with all limitations contained in such
    determination.
     
    c) As an alternative to the otherwise applicable treatment standards of Subpart D of this
    Part, lab packs are eligible for land disposal provided the following requirements are
    met:
     

     
    810
    1) The lab packs comply with the applicable provisions of 35 Ill. Adm. Code
    724.416 and 725.416;
     
    BOARD NOTE: 35 Ill. Adm. Code 729.301 and 729.312 include additional
    restrictions on the use of lab packs.
     
    2) The lab pack does not contain any of the wastes listed in Appendix D of this
    Part;
     
    3) The lab packs are incinerated in accordance with the requirements of Subpart
    O of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725; and
     
    4) Any incinerator residues from lab packs containing D004, D005, D006,
    D007, D008, D010, and D011 are treated in compliance with the applicable
    treatment standards specified for such wastes in Subpart D of this Part.
     
    d) Radioactive hazardous mixed wastes are subject to the treatment standards in Section
    728.140 and Table T of this Part. Where treatment standards are specified for
    radioactive mixed wastes in Table T of this Part, “Table of Treatment Standards,”
    those treatment standards will govern. Where there is no specific treatment standard
    for radioactive mixed waste, the treatment standard for the hazardous waste (as
    designated by USEPA hazardous waste code) applies. Hazardous debris containing
    radioactive waste is subject to the treatment standards specified in Section 728.145.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.144 Adjustment of Treatment Standard
     
    a) Based on a petition filed by a generator or treater of hazardous waste, the Board
    will grant an adjusted standard from an applicable treatment standard if the
    petitioner can demonstrate that either of the following applies to treatment of the
    waste:
     
    1) It is not physically possible to treat the waste to the level specified in the
    treatment standard, or by the method specified as the treatment standard.
    To show that this is the case, the petitioner must demonstrate that because
    the physical or chemical properties of the waste differ significantly from
    waste analyzed in developing the treatment standard, the waste cannot be
    treated to the specified level or by the specified method; or
     
    2) It is inappropriate to require the waste to be treated to the level specified
    in the treatment standard or by the method specified as the treatment
    standard, even though such treatment is technically possible. To show
    that this is the case, the petitioner must demonstrate that either of the
    following applies to treatment of the waste:
     

     
    811
    A) Treatment to the specified level or by the specified method is
    technically inappropriate (for example, resulting in combustion of
    large amounts of mildly contaminated environmental media); or
     
    B) For remediation waste only, treatment to the specified level or by
    the specified method is environmentally inappropriate because it
    would likely discourage aggressive remediation.
     
    BOARD NOTE: Corresponding federal 40 CFR 268.44 refers to these as
    “treatability variances.” The Board has not used this term in its rules to
    avoid confusion with the Board variances under Title IX of the
    Environmental Protection Act. The equivalent Board procedures are an
    “adjusted standard from a treatment standard” pursuant to subsections (a)
    through (m) of this Section, or a “treatability exception” adopted pursuant
    to subsection (p) of this Section. While the latter is adopted by “identical
    in substance” rulemaking following a USEPA action, the former is an
    original Board action that will be the only mechanism following
    authorization to the State of this component of the RCRA program.
     
    b) Each petition must be submitted in accordance with the procedures in Subpart D
    of 35 Ill. Adm. Code 104.
     
    c) Each petition must include the following statement signed by the petitioner or an
    authorized representative:
     
    I certify under penalty of law that I have personally examined and am
    familiar with the information submitted in this petition and all attached
    documents, and that, based on my inquiry of those individuals
    immediately responsible for obtaining the information, I believe that the
    submitted information is true, accurate and complete. I am aware that
    there are significant penalties for submitting false information, including
    the possibility of fine and imprisonment.
     
    d) After receiving a petition for an adjusted treatment standard, the Board may
    request any additional information or samples that are necessary to evaluate the
    petition.
     
    e) The Board will give public notice and provide an opportunity for public comment,
    as provided in Subpart D of 35 Ill. Adm. Code 104. In conjunction with any
    updating of the RCRA regulations, the Board will maintain, in this Part, a listing
    of all adjusted treatment standards granted by the Board pursuant to this Section.
    A LISTING OF ALL ADJUSTED STANDARDS GRANTED PURSUANT TO
    THIS SECTION WILL BE PUBLISHED IN THE ILLINOIS REGISTER AND
    ENVIRONMENTAL REGISTER AT THE END OF EACH FISCAL YEAR.
    (Section 28.1(d)(3) of the Environmental Protection Act [415 ILCS 5/28.1(d)(3)])
     

     
    812
    f) A generator, treatment facility or disposal facility that is managing a waste
    covered by an adjusted treatment standard must comply with the waste analysis
    requirements for restricted wastes found under Section 728.107.
     
    g) During the petition review process, the applicant is required to comply with all
    restrictions on land disposal under this Part once the effective date for the waste
    has been reached.
     
    h) Based on a petition filed by a generator or treater of hazardous waste, the Board
    will grant an adjusted standard from an applicable treatment standard if the
    petitioner can demonstrate that either of the following applies to treatment of the
    waste:
     
    1) It is not physically possible to treat the waste to the level specified in the
    treatment standard, or by the method specified as the treatment standard.
    To show that this is the case, the petitioner must demonstrate that because
    the physical or chemical properties of the waste differ significantly from
    waste analyzed in developing the treatment standard, the waste cannot be
    treated to the specified level or by the specified method; or
     
    2) It is inappropriate to require the waste to be treated to the level specified
    in the treatment standard or by the method specified as the treatment
    standard, even though such treatment is technically possible. To show
    that this is the case, the petitioner must demonstrate that either of the
    following applies to treatment of the waste:
     
    A) Treatment to the specified level or by the specified method is
    technically inappropriate (for example, resulting in combustion of
    large amounts of mildly contaminated environmental media where
    the treatment standard is not based on combustion of such media);
    or
     
    B) For remediation waste only, treatment to the specified level or by
    the specified method is environmentally inappropriate because it
    would likely discourage aggressive remediation.
     
    3) For contaminated soil only, treatment to the level or by the method
    specified in the soil treatment standards would result in concentrations of
    hazardous constituents that are below (i.e., lower than) the concentrations
    necessary to minimize short- and long-term threats to human health and
    the environment. An adjusted standard from a treatment standard granted
    under this subsection (h)(3) will include the following features:
     
    A) At a minimum, the adjusted standard from the treatment standard
    will impose an alternative land disposal restriction treatment
    standard that will achieve the following, using a reasonable

     
    813
    maximum exposure scenario:
     
    i) For carcinogens, it will achieve constituent concentrations
    that result in the total excess risk to an individual exposed
    over a lifetime, generally falling within a range from 10
    -4
    to
    10
    -6
    ; and
     
    ii) For constituents with non-carcinogenic effects, it will
    achieve constituent concentrations that an individual could
    be exposed to on a daily basis without appreciable risk of
    deleterious effect during a lifetime.
     
    B) The treatment adjusted standard will not consider post-land-
    disposal controls.
     
    4) For contaminated soil only, treatment to the level or by the method
    specified in the soil treatment standards would result in concentrations of
    hazardous constituents that are below (i.e., lower than) natural background
    concentrations at the site where the contaminated soil will be land
    disposed.
     
    5) The Board will follow the procedures of Section 28.1 of the Act and
    Subpart D of 35 Ill. Adm. Code 104 pertaining to public notice and a
    reasonable opportunity for public comment before granting or denying a
    petition.
     
    i) Each petition for a site-specific adjusted treatment standard must include the
    information in 35 Ill. Adm. Code 720.120(b)(1) through (b)(4).
     
    j) After receiving a petition for a site-specific adjusted treatment standard, the Board
    may request any additional information or samples that the Board determines are
    necessary to evaluate the petition.
     
    k) A generator, treatment facility or disposal facility that is managing a waste
    covered by a site-specific adjusted treatment standard must comply with the waste
    analysis requirements for restricted wastes in Section 728.107.
     
    l) During the petition review process, the petitioner for a site-specific adjusted
    treatment standard must comply with all restrictions on land disposal under this
    Part once the effective date for the waste has been reached.
     
    m) For any adjusted standard from a treatment standard, the petitioner must also
    demonstrate that compliance with the requested adjusted standard is sufficient to
    minimize threats to human health and the environment posed by land disposal of
    the waste. In evaluating this demonstration, the Board will take into account
    whether the adjusted standard should be granted if the subject waste is to be used

     
    814
    in a manner constituting disposal pursuant to Sections 728.120 through 728.123.
     
    n) This subsection (n) corresponds with 40 CFR 264.1030(n) 268.44(n), marked
    “reserved” by USEPA. This statement maintains structural consistency with
    corresponding federal regulations.
     
    o) The facilities listed in Table H of this Part are excluded from the treatment
    standards under Section 728.143(a) and Table B of this Part, and are subject to the
    constituent concentrations listed in Table H of this Part.
     
    p) If USEPA grants a treatability exception by regulatory action pursuant to 40 CFR
    268.44 and a person demonstrates that the treatability exception needs to be
    adopted as part of the Illinois RCRA program because the waste is generated or
    managed in Illinois, the Board will adopt the treatability exception by identical in
    substance rulemaking pursuant to Section 22.4(a) of the Environmental Protection
    Act [415 ILCS 5/22.4(a)].
     
    BOARD NOTE: The Board will adopt the treatability exception during a RCRA
    update Docket if a timely demonstration is made. Otherwise, the Board will
    assign the matter to a separate Docket.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.145 Treatment Standards for Hazardous Debris
     
    a) Treatment standards. Hazardous debris must be treated prior to land disposal as
    follows, unless the Agency has determined, under 35 Ill. Adm. Code 721.103(f)(2),
    that the debris is no longer contaminated with hazardous waste or the debris is
    treated to the waste-specific treatment standard provided in this Subpart D for the
    waste contaminating the debris:
     
    1) General. Hazardous debris must be treated for each “contaminant subject to
    treatment,” defined by subsection (b) of this Section, using the technology or
    technologies identified in Table F of this Part.
     
    2) Characteristic debris. Hazardous debris that exhibits the characteristic of
    ignitability, corrosivity, or reactivity identified under 35 Ill. Adm. Code
    721.121, 721.122, or 721.123, respectively, must be deactivated by treatment
    using one of the technologies identified in Table F of this Part.
     
    3) Mixtures of debris types. The treatment standards of Table F of this Part
    must be achieved for each type of debris contained in a mixture of debris
    types. If an immobilization technology is used in a treatment train, it must be
    the last treatment technology used.
     
    4) Mixtures of contaminant types. Debris that is contaminated with two or

     
    815
    more contaminants subject to treatment identified under subsection (b) of
    this Section must be treated for each contaminant using one or more
    treatment technologies identified in Table F of this Part. If an
    immobilization technology is used in a treatment train, it must be the last
    treatment technology used.
     
    5) Waste PCBs. Hazardous debris that is also a waste PCB under 40 CFR 761
    (Polychlorinated Biphenyls (PCBs) Manufacturing, Processing,
    Distribution in Commerce, and Use Prohibitions), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b), is subject to the requirements of
    either 40 CFR 761 or the requirements of this Section, whichever are more
    stringent.
     
    b) Contaminants subject to treatment. Hazardous debris must be treated for each
    “contaminant subject to treatment.” The contaminants subject to treatment must be
    determined as follows:
     
    1) Toxicity characteristic debris. The contaminants subject to treatment for
    debris that exhibits the Toxicity Characteristic (TC) by 35 Ill. Adm. Code
    721.124 are those EP constituents for which the debris exhibits the TC
    toxicity characteristic.
     
    2) Debris contaminated with listed waste. The contaminants subject to
    treatment for debris that is contaminated with a prohibited listed hazardous
    waste are those constituents or wastes for which treatment standards are
    established for the waste under Section 728.140 and Table T of this Part.
     
    3) Cyanide reactive debris. Hazardous debris that is reactive because of cyanide
    must be treated for cyanide.
     
    c) Conditioned exclusion of treated debris. Hazardous debris that has been treated
    using one of the specified extraction or destruction technologies in Table F of this
    Part and that does not exhibit a characteristic of hazardous waste identified under
    Subpart C of 35 Ill. Adm. Code 721 after treatment is not a hazardous waste and
    need not be managed in a subtitle C facility. Hazardous debris contaminated with a
    listed waste that is treated by an immobilization technology specified in Table F of
    this Part is a hazardous waste and must be managed in a RCRA Subtitle C treatment,
    storage, or disposal facility.
     
    d) Treatment residuals.
     
    1) General requirements. Except as provided by subsections (d)(2) and (d)(4)
    of this Section:
     
    A) Residue from the treatment of hazardous debris must be separated
    from the treated debris using simple physical or mechanical means;

     
    816
    and
     
    B) Residue from the treatment of hazardous debris is subject to the
    waste-specific treatment standards provided by Subpart D of this Part
    for the waste contaminating the debris.
     
    2) Nontoxic debris. Residue from the deactivation of ignitable, corrosive, or
    reactive characteristic hazardous debris (other than cyanide-reactive) that is
    not contaminated with a contaminant subject to treatment defined by
    subsection (b) of this Section, must be deactivated prior to land disposal and
    is not subject to the waste-specific treatment standards of Subpart D of this
    Part.
     
    3) Cyanide-reactive debris. Residue from the treatment of debris that is reactive
    because of cyanide must meet the standards for USEPA hazardous waste
    number D003 under Section 728.140 and Table T of this Part.
     
    4) Ignitable nonwastewater residue. Ignitable nonwastewater residue
    containing equal to or greater than 10 percent total organic carbon is subject
    to the technology specified in the treatment standard for USEPA hazardous
    waste number D001: Ignitable Liquids.
     
    5) Residue from spalling. Layers of debris removed by spalling are hazardous
    debris that remains subject to the treatment standards of this Section.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART E: PROHIBITIONS ON STORAGE
     
    Section 728.150 Prohibitions on Storage of Restricted Wastes
     
    a) Except as provided in this Section, the storage of hazardous wastes restricted from
    land disposal under Subpart C of this Part is prohibited, unless the following
    conditions are met:
     
    1) A generator stores such wastes in tanks, containers, or containment buildings
    on-site solely for the purpose of the accumulation of such quantities of
    hazardous waste as necessary to facilitate proper recovery, treatment, or
    disposal and the generator complies with the requirements in 35 Ill. Adm.
    Code 722.134 and 35 Ill. Adm. Code 724 and 725. (A generator that is in
    existence on the effective date of a regulation under this Part and which must
    store hazardous wastes for longer than 90 days due to the regulations under
    this Part becomes an owner or operator of a storage facility and must obtain a
    RCRA permit, as required by 35 Ill. Adm. Code 703. Such a facility may
    qualify for interim status upon compliance with the regulations governing
    interim status under 35 Ill. Adm. Code 703.153.)

     
    817
     
    2) An owner or operator of a hazardous waste treatment, storage, or disposal
    facility stores such wastes in tanks, containers, or containment buildings
    solely for the purpose of the accumulation of such quantities of hazardous
    waste as necessary to facilitate proper recovery, treatment, or disposal and
    each of the following conditions are fulfilled:
     
    A) Each container is clearly marked to identify its contents and the date
    each period of accumulation begins; and
     
    B) Each tank is clearly marked with a description of its contents, the
    quantity of each hazardous waste received and the date each period of
    accumulation begins, or such information is recorded and maintained
    in the operating record at the facility. Regardless of whether the tank
    itself is marked, the owner and operator must comply with the
    operating record requirements of 35 Ill. Adm. Code 724.173 or
    725.173.
     
    3) A transporter stores manifested shipments of such wastes at a transfer facility
    for 10 days or less.
     
    b) An owner or operator of a treatment, storage, or disposal facility may store such
    wastes for up to one year unless the Agency can demonstrate that such storage was
    not solely for the purpose of accumulation of such quantities of hazardous waste as
    are necessary to facilitate proper recovery, treatment, or disposal.
     
    c) An owner or operator of a treatment, storage, or disposal facility may store wastes
    beyond one year; however, the owner or operator bears the burden of proving that
    such storage was solely for the purpose of accumulation of such quantities of
    hazardous waste as are necessary to facilitate proper recovery, treatment, or disposal.
     
    d) If a generator’s waste is exempt from a prohibition on the type of land disposal
    utilized for the waste (for example, because of an approved case-by-case extension
    under granted by USEPA pursuant to 40 CFR 268.5, incorporated by reference in
    Section 728.105, an approved Section 728.106 petition or a national capacity
    variance under granted by USEPA pursuant to subpart C of 40 CFR 268, Subpart
    C), the prohibition in subsection (a) does not apply during the period of such
    exemption.
     
    e) The prohibition in subsection (a) of this Section does not apply to hazardous wastes
    that meet the treatment standards specified under Sections 728.141, 728.142, and
    728.143 or the adjusted treatment standards specified under Section 728.144, or,
    where treatment standards have not been specified, the waste is in compliance with
    the applicable prohibitions specified in Section 728.132 or 728.139.
     
    f) Liquid hazardous wastes containing PCBs at concentrations greater than or equal to

     
    818
    50 ppm must be stored at a facility that meets the requirements of federal 40 CFR
    761.65(b) (Storage for Disposal), incorporated by reference in 35 Ill. Adm. Code
    720.111 720.111(b), and must be removed from storage and treated or disposed as
    required by the Part within one year of the date when such wastes are first placed
    into storage. The provisions of subsection (c) of this Section do not apply to such
    PCB wastes prohibited under Section 728.132.
     
    g) The prohibition and requirements in this Section do not apply to hazardous
    remediation wastes stored in a staging pile approved pursuant to 35 Ill. Adm.
    Code 724.654.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.Appendix C List of Halogenated Organic Compounds Regulated under Section
    728.132
     
    In determining the concentration of halogenated organic compounds (HOCs) in a hazardous
    waste for purposes of the Section 728.132 land disposal prohibition, USEPA has defined the
    HOCs that must be included in a calculation as any compounds having a carbon-halogen bond
    that are listed in this Appendix (see Section 728.102). This Appendix C to Part 728 consists of
    the following compounds:
     
    I. Volatiles
     
    1. Bromodichloromethane
    2. Bromomethane
    3. Carbon Tetrachloride
    4. Chlorobenzene
    5. 2-Chloro-1,3-butadiene
    6. Chlorodibromomethane
    7. Chloroethane
    8. 2-Chloroethyl vinyl ether
    9. Chloroform
    10. Chloromethane
    11. 3-Chloropropene
    12. 1,2-Dibromo-3-chloropropane
    13. 1,2-Dibromomethane
    14. Dibromomethane
    15. Trans-1,4-Dichloro-2--butene
    16. Dichlorodifluoromethane
    17. 1,1-Dichloroethane
    18. 1,2-Dichloroethane
    19. 1,1-Dichloroethylene
    20. Trans-1,2-Dichloroethene
    21. 1,2-Dichloropropane
    22. Trans-1,3-Dichloropropene

     
    819
    23. cis-1,3-Dichloropropene
    24. Iodomethane
    25. Methylene chloride
    26. 1,1,1,2-Tetrachloroethane
    27. 1,1,2,2-Tetrachloroethane
    28. Tetrachloroethene
    29. Tribromomethane
    30. 1,1,1-Trichloroethane
    31. 1,1,2-Trichloroethane
    32. Trichloroethene
    33. Trichloromonofluoromethane
    34. 1,2,3-Thrichloropropane
    35. Vinyl Chloride
     
    II. Semivolatiles
     
    1. Bis(2-chloroethoxy)ethane
    2. Bis(2-chloroethyl)ether
    3. Bis(2-chloroisopropyl)ether
    4. p-Chloroaniline
    5. Chlorobenzilate
    6. p-Chloro-m-cresol
    7. 2-Chloronaphthalene
    8. 2-Chlorophenol
    9. 3-Chloropropionitrile
    10. m-Dichlorobenzene
    11. o-Dichlorobenzene
    12. p-Dichlorobenzene
    13. 3.3'-Dichlorobenzidine
    14. 2,4-Dichlorophenol
    15. 2,6-Dichlorophenol
    16. Hexachlorobenzene
    17. Hexachlorobutadiene
    18. Hexachlorocyclopentadiene
    19. Hexachloroethane
    20. Hexachlorophene
    21. Hexachloropropene
    22. 4,4'-Methylenebis(2-chloroanaline)
    23. Pentachlorobenzene
    24. Pentachloroethane
    25. Pentachloronitrobenzene
    26. Pentachlorophenol
    27. Pronamide
    28. 1,2,4,5-Tetrachlorobenzene
    29. 2,3,4,6-Tetrachlorophenol
    30. 1,2,4-Trichlorobenzene

     
    820
    31. 2,4,5-Trichlorophenol
    32. 2,4,6-Trichlorophenol
    33. Tris(2,3-dibromopropyl)phosphate
     
    III. Organochlorine Pesticides
     
    1. Aldrin
    2. alpha-BHC
    3. beta-BHC
    4. delta-BHC
    5. gamma-BHC
    6. Chlorodane
    7. DDD
    8. DDE
    9. DDT
    10. Dieldrin
    11. Endosulfan I
    12. Endosulfan II
    13. Endrin
    14. Endrin aldehyde
    15. Heptachlor
    16. Heptachlor epoxide
    17. Isodrin
    18. Kepone
    19. Methoxyclor
    20. Toxaphene
     
    IV. Phenoxyacetic Acid Herbicides
     
    1. 2,4-Dichlorophenoxyacetic acid
    2. Silvex
    3. 2,4,5-T
     
    V. PCBs
     
    1. Aroclor 1016
    2. Aroclor 1221
    3. Aroclor 1232
    4. Aroclor 1242
    5. Aroclor 1248
    6. Aroclor 1254
    7. Aroclor 1260
    8. PCBs not otherwise specified
     

     
    821
    VI. Dioxins and Furans
     
    1. Hexachlorodibenzo-p-dioxins
    2. Hexachlorodibenzofuran
    3. Pentachlorodibenzo-p-dioxins
    4. Pentachlorodibenzofuran
    5. Tetrachlorodibenzo-p-dioxins
    6. Tetrachlorodibenzofuran
    7. 2,3,7,8-Tetrachlorodibenzo-p-dioxin
     
    BOARD NOTE: Derived from appendix III to 40 CFR 268, Appendix III (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.Appendix G Federal Effective Dates
     
    The following are the effective dates for the USEPA rules in 40 CFR 268. These generally became
    effective as Illinois rules at a later date.
     
    TABLE 1
    EFFECTIVE DATES OF SURFACE DISPOSED WASTES (NON-SOIL AND
    DEBRIS) REGULATED IN THE LDRS
    a
    —COMPREHENSIVE LIST
     
    Waste code Waste category Effective date
    D001
    c
    All (except High TOC Ignitable Liquids) August 9, 1993
    D001 High TOC Ignitable Liquids August 8, 1990
    D002
    c
    All August 9, 1993
    D003
    e
    Newly identified surface-disposed
    elemental phosphorus processing wastes
    May 26, 2000
    D004 Newly identified D004 and mineral
    processing wastes
    August 24, 1998
    D004 Mixed radioactive/newly identified D004
    or mineral processing wastes
    May 26, 2000
    D005 Newly identified D005 and mineral
    processing wastes
    August 24, 1998
    D005 Mixed radioactive/newly identified D005
    or mineral processing wastes
    May 26, 2000
    D006 Newly identified D006 and mineral
    processing wastes
    August 24, 1998
    D006 Mixed radioactive/newly identified D006
    or mineral processing wastes
    May 26, 2000
    D007 Newly identified D007 and mineral
    processing wastes
    August 24, 1998
    D007 Mixed radioactive/newly identified
    D007or mineral processing wastes
    May 26, 2000

     
    822
    D008 Newly identified D008 and mineral
    processing waste
    August 24, 1998
    D008 Mixed radioactive/newly identified D008
    or mineral processing wastes
    May 26, 2000
    D009 Newly identified D009 and mineral
    processing waste
    August 24, 1998
    D009 Mixed radioactive/newly identified
    D009or mineral processing wastes
    May 26, 2000
    D010 Newly identified D010 and mineral
    processing wastes
    August 24, 1998
    D010 Mixed radioactive/newly identified D010
    or mineral processing wastes
    May 26, 2000
    D011 Newly identified D011 and mineral
    processing wastes
    August 24, 1998
    D011 Mixed radioactive/newly identified
    D011or mineral processing wastes
    May 26, 2000
    D012 (that exhibit the toxici-
    ty characteristic based on the
    TCLP)
    d
     
    All December 14, 1994
    D013 (that exhibit the toxici-
    ty characteristic based on the
    TCLP)
    d
     
    All December 14, 1994
    D014 (that exhibit the toxici-
    ty characteristic based on the
    TCLP)
    d
     
    All December 14, 1994
    D015 (that exhibit the toxici-
    ty characteristic based on the
    TCLP)
    d
     
    All December 14, 1994
    D016 (that exhibit the toxici-
    ty characteristic based on the
    TCLP)
    d
     
    All December 14, 1994
    D017 (that exhibit the toxici-
    ty characteristic based on the
    TCLP)
    d
     
    All December 14, 1994
    D018 Mixed with radioactive wastes September 19, 1996
    D018 All others December 19, 1994
    D019 Mixed with radioactive wastes September 19, 1996
    D019 All others December 19, 1994
    D020 Mixed with radioactive wastes September 19, 1996
    D020 All others December 19, 1994
    D021 Mixed with radioactive wastes September 19, 1996
    D021 All others December 19, 1994
    D022 Mixed with radioactive wastes September 19, 1996
    D022 All others December 19, 1994
    D023 Mixed with radioactive wastes September 19, 1996
    D023 All others December 19, 1994

     
    823
    D024 Mixed with radioactive wastes September 19, 1996
    D024 All others December 19, 1994
    D025 Mixed with radioactive wastes September 19, 1996
    D025 All others December 19, 1994
    D026 Mixed with radioactive wastes September 19, 1996
    D026 All others December 19, 1994
    D027 Mixed with radioactive wastes September 19, 1996
    D027 All others December 19, 1994
    D028 Mixed with radioactive wastes September 19, 1996
    D028 All others December 19, 1994
    D029 Mixed with radioactive wastes September 19, 1996
    D029 All others December 19, 1994
    D030 Mixed with radioactive wastes September 19, 1996
    D030 All others December 19, 1994
    D031 Mixed with radioactive wastes September 19, 1996
    D031 All others December 19, 1994
    D032 Mixed with radioactive wastes September 19, 1996
    D032 All others December 19, 1994
    D033 Mixed with radioactive wastes September 19, 1996
    D033 All others December 19, 1994
    D034 Mixed with radioactive wastes September 19, 1996
    D034 All others December 19, 1994
    D035 Mixed with radioactive wastes September 19, 1996
    D035 All others December 19, 1994
    D036 Mixed with radioactive wastes September 19, 1996
    D036 All others December 19, 1994
    D037 Mixed with radioactive wastes September 19, 1996
    D037 All others December 19, 1994
    D038 Mixed with radioactive wastes September 19, 1996
    D038 All others December 19, 1994
    D039 Mixed with radioactive wastes September 19, 1996
    D039 All others December 19, 1994
    D040 Mixed with radioactive wastes September 19, 1996
    D040 All others December 19, 1994
    D041 Mixed with radioactive wastes September 19, 1996
    D041 All others December 19, 1994
    D042 Mixed with radioactive wastes September 19, 1996
    D042 All others December 19, 1994
    D043 Mixed with radioactive wastes September 19, 1996
    D043 All others December 19, 1994
    F001 Small quantity generators, CERCLA
    response/RCRA corrective action, initial
    generator’s solvent-water mixtures, solvent-
    containing sludges and solids
    November 8, 1988
    F001 All others November 8, 1986
    F002 (1,1,2-trichloroethane) Wastewater and Nonwastewater August 8, 1990

     
    824
    F002 Small quantity generators, CERCLA
    response/RCRA corrective action, initial
    generator’s solvent-water mixtures, solvent-
    containing sludges and solids
    November 8, 1988
    F002 All others November 8, 1986
    F003 Small quantity generators, CERCLA
    response/RCRA corrective action, initial
    generator’s solvent-water mixtures, solvent-
    containing sludges and solids
    November 8, 1988
    F003 All others November 8, 1986
    F004 Small quantity generators, CERCLA
    response/RCRA corrective action, initial
    generator’s solvent-water mixtures, solvent-
    containing sludges and solids
    November 8, 1988
    F004 All others November 8, 1986
    F005 (benzene, 2-ethoxy
    ethanol, 2-nitropropane)
    Wastewater and Nonwastewater August 8, 1990
    F005 Small quantity generators, CERCLA
    response/RCRA corrective action, initial
    generator’s solvent-water mixtures, solvent-
    containing sludges and solids
    November 8, 1988
    F005 All others November 8, 1986
    F006 Wastewater August 8, 1990
    F006 Nonwastewater August 8, 1988
    F006 (cyanides) Nonwastewater July 8, 1989
    F007 All July 8, 1989
    F008 All July 8, 1989
    F009 All July 8, 1989
    F010 All June 8, 1989
    F011 (cyanides) Nonwastewater December 8, 1989
    F011 All others July 8, 1989
    F012 (cyanides) Nonwastewater December 8, 1989
    F012 All others July 8, 1989
    F019 All August 8, 1990
    F020 All November 8, 1988
    F021 All November 8, 1988
    F025 All August 8, 1990
    F026 All November 8, 1988
    F027 All November 8, 1988
    F028 All November 8, 1988
    F032 Mixed with radioactive wastes May 12, 1999
    F032 All others August 12, 1997
    F034 Mixed with radioactive wastes May 12, 1999
    F034 All others August 12, 1997
    F035 Mixed with radioactive wastes May 12, 1999
    F035 All others August 12, 1997

     
    825
    F037 Not generated from surface impoundment
    cleanouts or closures
    June 30, 1993
    F037 Generated from surface impoundment
    cleanouts or closures
    June 30, 1994
    F037 Mixed with radioactive wastes June 30, 1994
    F038 Not generated from surface impoundment
    cleanouts or closures
    June 30, 1993
    F038 Generated from surface impoundment
    cleanouts or closures
    June 30, 1994
    F038 Mixed with radioactive wastes June 30, 1994
    F039 Wastewater August 8, 1990
    F039 Nonwastewater May 8, 1992
    K001 (organics)
    b
    All August 8, 1988
    K001 All others August 8, 1988
    K002 All August 8, 1990
    K003 All August 8, 1990
    K004 Wastewater August 8, 1990
    K004 Nonwastewater August 8, 1988
    K005 Wastewater August 8, 1990
    K005 Nonwastewater June 8, 1989
    K006 All August 8, 1990
    K007 Wastewater August 8, 1990
    K007 Nonwastewater June 8, 1989
    K008 Wastewater August 8, 1990
    K008 Nonwastewater August 8, 1988
    K009 All June 8, 1989
    K010 All June 8, 1989
    K011 Wastewater August 8, 1990
    K011 Nonwastewater June 8, 1989
    K013 Wastewater August 8, 1990
    K013 Nonwastewater June 8, 1989
    K014 Wastewater August 8, 1990
    K014 Nonwastewater June 8, 1989
    K015 Wastewater August 8, 1988
    K015 Nonwastewater August 8, 1990
    K016 All August 8, 1988
    K017 All August 8, 1990
    K018 All August 8, 1988
    K019 All August 8, 1988
    K020 All August 8, 1988
    K021 Wastewater August 8, 1990
    K021 Nonwastewater August 8, 1988
    K022 Wastewater August 8, 1990
    K022 Nonwastewater August 8, 1988
    K023 All June 8, 1989
    K024 All August 8, 1988

     
    826
    K025 Wastewater August 8, 1990
    K025 Nonwastewater August 8, 1988
    K026 All August 8, 1990
    K027 All June 8, 1989
    K028 (metals) Nonwastewater August 8, 1990
    K028 All others June 8, 1989
    K029 Wastewater August 8, 1990
    K029 Nonwastewater June 8, 1989
    K030 All August 8, 1988
    K031 Wastewater August 8, 1990
    K031 Nonwastewater May 8, 1992
    K032 All August 8, 1990
    K033 All August 8, 1990
    K034 All August 8, 1990
    K035 All August 8, 1990
    K036 Wastewater June 8, 1989
    K036 Nonwastewater August 8, 1988
    K037
    b
    Wastewater August 8, 1988
    K037 Nonwastewater August 8, 1988
    K038 All June 8, 1989
    K039 All June 8, 1989
    K040 All June 8, 1989
    K041 All August 8, 1990
    K042 All August 8, 1990
    K043 All June 8, 1989
    K044 All August 8, 1988
    K045 All August 8, 1988
    K046 (Nonreactive) Nonwastewater August 8, 1988
    K046 All others August 8, 1990
    K047 All August 8, 1988
    K048 Wastewater August 8, 1990
    K048 Nonwastewater November 8, 1990
    K049 Wastewater August 8, 1990
    K049 Nonwastewater November 8, 1990
    K050 Wastewater August 8, 1990
    K050 Nonwastewater November 8, 1990
    K051 Wastewater August 8, 1990
    K051 Nonwastewater November 8, 1990
    K052 Wastewater August 8, 1990
    K052 Nonwastewater November 8, 1990
    K060 Wastewater August 8, 1990
    K060 Nonwastewater August 8, 1988
    K061 Wastewater August 8, 1990
    K061 Nonwastewater June 30, 1992
    K062 All August 8, 1988
    K069 (non-calcium sulfate) Nonwastewater August 8, 1988

     
    827
    K069 All others August 8, 1990
    K071 All August 8, 1990
    K073 All August 8, 1990
    K083 All August 8, 1990
    K084 Wastewater August 8, 1990
    K084 Nonwastewater May 8, 1992
    K085 All August 8, 1990
    K086 (organics)
    b
    All August 8, 1988
    K086 All others August 8, 1988
    K087 All August 8, 1988
    K088 Mixed with radioactive wastes April 8, 1998
    K088 All others October 8, 1997
    K093 All June 8, 1989
    K094 All June 8, 1989
    K095 Wastewater August 8, 1990
    K095 Nonwastewater June 8, 1989
    K096 Wastewater August 8, 1990
    K096 Nonwastewater June 8, 1989
    K097 All August 8, 1990
    K098 All August 8, 1990
    K099 All August 8, 1988
    K100 Wastewater August 8, 1990
    K100 Nonwastewater August 8, 1988
    K101 (organics) Wastewater August 8, 1988
    K101 (metals) Wastewater August 8, 1990
    K101 (organics) Nonwastewater August 8, 1988
    K101 (metals) Nonwastewater May 8, 1992
    K102 (organics) Wastewater August 8, 1988
    K102 (metals) Wastewater August 8, 1990
    K102 (organics) Nonwastewater August 8, 1988
    K102 (metals) Nonwastewater May 8, 1992
    K103 All August 8, 1988
    K104 All August 8, 1988
    K105 All August 8, 1990
    K106 Wastewater August 8, 1990
    K106 Nonwastewater May 8, 1992
    K107 Mixed with radioactive wastes June 30, 1994
    K107 All others November 9, 1992
    K108 Mixed with radioactive wastes June 30, 1994
    K108 All others November 9, 1992
    K109 Mixed with radioactive wastes June 30, 1994
    K109 All others November 9, 1992
    K110 Mixed with radioactive wastes June 30, 1994
    K110 All others November 9, 1992
    K111 Mixed with radioactive wastes June 30, 1994
    K111 All others November 9, 1992

     
    828
    K112 Mixed with radioactive wastes June 30, 1994
    K112 All others November 9, 1992
    K113 All June 8, 1989
    K114 All June 8, 1989
    K115 All June 8, 1989
    K116 All June 8, 1989
    K117 Mixed with radioactive wastes June 30, 1994
    K117 All others November 9, 1992
    K118 Mixed with radioactive wastes June 30, 1994
    K118 All others November 9, 1992
    K123 Mixed with radioactive wastes June 30, 1994
    K123 All others November 9, 1992
    K124 Mixed with radioactive wastes June 30, 1994
    K124 All others November 9, 1992
    K125 Mixed with radioactive wastes June 30, 1994
    K125 All others November 9, 1992
    K126 Mixed with radioactive wastes June 30, 1994
    K126 All others November 9, 1992
    K131 Mixed with radioactive wastes June 30, 1994
    K131 All others November 9, 1992
    K132 Mixed with radioactive wastes June 30, 1994
    K132 All others November 9, 1992
    K136 Mixed with radioactive wastes June 30, 1994
    K136 All others November 9, 1992
    K141 Mixed with radioactive wastes September 19, 1996
    K141 All others December 19, 1994
    K142 Mixed with radioactive wastes September 19, 1996
    K142 All others December 19, 1994
    K143 Mixed with radioactive wastes September 19, 1996
    K143 All others December 19, 1994
    K144 Mixed with radioactive wastes September 19, 1996
    K144 All others December 19, 1994
    K145 Mixed with radioactive wastes September 19, 1996
    K145 All others December 19, 1994
    K147 Mixed with radioactive wastes September 19, 1996
    K147 All others December 19, 1994
    K148 Mixed with radioactive wastes September 19, 1996
    K148 All others December 19, 1994
    K149 Mixed with radioactive wastes September 19, 1996
    K149 All others December 19, 1994
    K150 Mixed with radioactive wastes September 19, 1996
    K150 All others December 19, 1994
    K151 Mixed with radioactive wastes September 19, 1996
    K151 All others December 19, 1994
    K156 Mixed with radioactive wastes April 8, 1998
    K156 All others July 8, 1996

     
    829
    K157 Mixed with radioactive wastes April 8, 1998
    K157 All others July 8, 1996
    K158 Mixed with radioactive wastes April 8, 1998
    K158 All others July 8, 1996
    K159 Mixed with radioactive wastes April 8, 1998
    K159 All others July 8, 1996
    K160 Mixed with radioactive wastes April 8, 1998
    K160 All others July 8, 1996
    K161 Mixed with radioactive wastes April 8, 1998
    K161 All others July 8, 1996
    K169 All February 8, 1999
    K170 All February 8, 1999
    K171 All February 8, 1999
    K172 All February 8, 1999
    K174 All May 7, 2001
    K175 All May 7, 2001
    K176 All May 20, 2002
    K177 All May 20, 2002
    K178 All May 20, 2002
    K181 All August 23, 2005
    P001 All August 8, 1990
    P002 All August 8, 1990
    P003 All August 8, 1990
    P004 All August 8, 1990
    P005 All August 8, 1990
    P006 All August 8, 1990
    P007 All August 8, 1990
    P008 All August 8, 1990
    P009 All August 8, 1990
    P010 Wastewater August 8, 1990
    P010 Nonwastewater May 8, 1992
    P011 Wastewater August 8, 1990
    P011 Nonwastewater May 8, 1992
    P012 Wastewater August 8, 1990
    P012 Nonwastewater May 8, 1992
    P013 (barium) Nonwastewater August 8, 1990
    P013 All others June 8, 1989
    P014 All August 8, 1990
    P015 All August 8, 1990
    P016 All August 8, 1990
    P017 All August 8, 1990
    P018 All August 8, 1990
    P020 All August 8, 1990
    P021 All June 8, 1989
    P022 All August 8, 1990
    P023 All August 8, 1990

     
    830
    P024 All August 8, 1990
    P026 All August 8, 1990
    P027 All August 8, 1990
    P028 All August 8, 1990
    P029 All June 8, 1989
    P030 All June 8, 1989
    P031 All August 8, 1990
    P033 All August 8, 1990
    P034 All August 8, 1990
    P036 Wastewater August 8, 1990
    P036 Nonwastewater May 8, 1992
    P037 All August 8, 1990
    P038 Wastewater August 8, 1990
    P038 Nonwastewater May 8, 1992
    P039 All June 8, 1989
    P040 All June 8, 1989
    P041 All June 8, 1989
    P042 All August 8, 1990
    P043 All June 8, 1989
    P044 All June 8, 1989
    P045 All August 8, 1990
    P046 All August 8, 1990
    P047 All August 8, 1990
    P048 All August 8, 1990
    P049 All August 8, 1990
    P050 All August 8, 1990
    P051 All August 8, 1990
    P054 All August 8, 1990
    P056 All August 8, 1990
    P057 All August 8, 1990
    P058 All August 8, 1990
    P059 All August 8, 1990
    P060 All August 8, 1990
    P062 All June 8, 1989
    P063 All June 8, 1989
    P064 All August 8, 1990
    P065 Wastewater August 8, 1990
    P065 Nonwastewater May 8, 1992
    P066 All August 8, 1990
    P067 All August 8, 1990
    P068 All August 8, 1990
    P069 All August 8, 1990
    P070 All August 8, 1990
    P071 All June 8, 1989
    P072 All August 8, 1990
    P073 All August 8, 1990

     
    831
    P074 All June 8, 1989
    P075 All August 8, 1990
    P076 All August 8, 1990
    P077 All August 8, 1990
    P078 All August 8, 1990
    P081 All August 8, 1990
    P082 All August 8, 1990
    P084 All August 8, 1990
    P085 All June 8, 1989
    P087 All May 8, 1992
    P088 All August 8, 1990
    P089 All June 8, 1989
    P092 Wastewater August 8, 1990
    P092 Nonwastewater May 8, 1992
    P093 All August 8, 1990
    P094 All June 8, 1989
    P095 All August 8, 1990
    P096 All August 8, 1990
    P097 All June 8, 1989
    P098 All June 8, 1989
    P099 (silver) Wastewater August 8, 1990
    P099 All others June 8, 1989
    P101 All August 8, 1990
    P102 All August 8, 1990
    P103 All August 8, 1990
    P104 (silver) Wastewater August 8, 1990
    P104 All others June 8, 1989
    P105 All August 8, 1990
    P106 All June 8, 1989
    P108 All August 8, 1990
    P109 All June 8, 1989
    P110 All August 8, 1990
    P111 All June 8, 1989
    P112 All August 8, 1990
    P113 All August 8, 1990
    P114 All August 8, 1990
    P115 All August 8, 1990
    P116 All August 8, 1990
    P118 All August 8, 1990
    P119 All August 8, 1990
    P120 All August 8, 1990
    P121 All June 8, 1989
    P122 All August 8, 1990
    P123 All August 8, 1990
    P127 Mixed with radioactive wastes April 8, 1998
    P127 All others July 8, 1996

     
    832
    P128 Mixed with radioactive wastes April 8, 1998
    P128 All others July 8, 1996
    P185 Mixed with radioactive wastes April 8, 1998
    P185 All others July 8, 1996
    P188 Mixed with radioactive wastes April 8, 1998
    P188 All others July 8, 1996
    P189 Mixed with radioactive wastes April 8, 1998
    P189 All others July 8, 1996
    P190 Mixed with radioactive wastes April 8, 1998
    P190 All others July 8, 1996
    P191 Mixed with radioactive wastes April 8, 1998
    P191 All others July 8, 1996
    P192 Mixed with radioactive wastes April 8, 1998
    P192 All others July 8, 1996
    P194 Mixed with radioactive wastes April 8, 1998
    P194 All others July 8, 1996
    P196 Mixed with radioactive wastes April 8, 1998
    P196 All others July 8, 1996
    P197 Mixed with radioactive wastes April 8, 1998
    P197 All others July 8, 1996
    P198 Mixed with radioactive wastes April 8, 1998
    P198 All others July 8, 1996
    P199 Mixed with radioactive wastes April 8, 1998
    P199 All others July 8, 1996
    P201 Mixed with radioactive wastes April 8, 1998
    P201 All others July 8, 1996
    P202 Mixed with radioactive wastes April 8, 1998
    P202 All others July 8, 1996
    P203 Mixed with radioactive wastes April 8, 1998
    P203 All others July 8, 1996
    P204 Mixed with radioactive wastes April 8, 1998
    P204 All others July 8, 1996
    P205 Mixed with radioactive wastes April 8, 1998
    P205 All others July 8, 1996
    U001 All August 8, 1990
    U002 All August 8, 1990
    U003 All August 8, 1990
    U004 All August 8, 1990
    U005 All August 8, 1990
    U006 All August 8, 1990
    U007 All August 8, 1990
    U008 All August 8, 1990
    U009 All August 8, 1990
    U010 All August 8, 1990
    U011 All August 8, 1990
    U012 All August 8, 1990

     
    833
    U014 All August 8, 1990
    U015 All August 8, 1990
    U016 All August 8, 1990
    U017 All August 8, 1990
    U018 All August 8, 1990
    U019 All August 8, 1990
    U020 All August 8, 1990
    U021 All August 8, 1990
    U022 All August 8, 1990
    U023 All August 8, 1990
    U024 All August 8, 1990
    U025 All August 8, 1990
    U026 All August 8, 1990
    U027 All August 8, 1990
    U028 All June 8, 1989
    U029 All August 8, 1990
    U030 All August 8, 1990
    U031 All August 8, 1990
    U032 All August 8, 1990
    U033 All August 8, 1990
    U034 All August 8, 1990
    U035 All August 8, 1990
    U036 All August 8, 1990
    U037 All August 8, 1990
    U038 All August 8, 1990
    U039 All August 8, 1990
    U041 All August 8, 1990
    U042 All August 8, 1990
    U043 All August 8, 1990
    U044 All August 8, 1990
    U045 All August 8, 1990
    U046 All August 8, 1990
    U047 All August 8, 1990
    U048 All August 8, 1990
    U049 All August 8, 1990
    U050 All August 8, 1990
    U051 All August 8, 1990
    U052 All August 8, 1990
    U053 All August 8, 1990
    U055 All August 8, 1990
    U056 All August 8, 1990
    U057 All August 8, 1990
    U058 All June 8, 1989
    U059 All August 8, 1990
    U060 All August 8, 1990
    U061 All August 8, 1990

     
    834
    U062 All August 8, 1990
    U063 All August 8, 1990
    U064 All August 8, 1990
    U066 All August 8, 1990
    U067 All August 8, 1990
    U068 All August 8, 1990
    U069 All June 30, 1992
    U070 All August 8, 1990
    U071 All August 8, 1990
    U072 All August 8, 1990
    U073 All August 8, 1990
    U074 All August 8, 1990
    U075 All August 8, 1990
    U076 All August 8, 1990
    U077 All August 8, 1990
    U078 All August 8, 1990
    U079 All August 8, 1990
    U080 All August 8, 1990
    U081 All August 8, 1990
    U082 All August 8, 1990
    U083 All August 8, 1990
    U084 All August 8, 1990
    U085 All August 8, 1990
    U086 All August 8, 1990
    U087 All June 8, 1989
    U088 All June 8, 1989
    U089 All August 8, 1990
    U090 All August 8, 1990
    U091 All August 8, 1990
    U092 All August 8, 1990
    U093 All August 8, 1990
    U094 All August 8, 1990
    U095 All August 8, 1990
    U096 All August 8, 1990
    U097 All August 8, 1990
    U098 All August 8, 1990
    U099 All August 8, 1990
    U101 All August 8, 1990
    U102 All June 8, 1989
    U103 All August 8, 1990
    U105 All August 8, 1990
    U106 All August 8, 1990
    U107 All June 8, 1989
    U108 All August 8, 1990
    U109 All August 8, 1990
    U110 All August 8, 1990

     
    835
    U111 All August 8, 1990
    U112 All August 8, 1990
    U113 All August 8, 1990
    U114 All August 8, 1990
    U115 All August 8, 1990
    U116 All August 8, 1990
    U117 All August 8, 1990
    U118 All August 8, 1990
    U119 All August 8, 1990
    U120 All August 8, 1990
    U121 All August 8, 1990
    U122 All August 8, 1990
    U123 All August 8, 1990
    U124 All August 8, 1990
    U125 All August 8, 1990
    U126 All August 8, 1990
    U127 All August 8, 1990
    U128 All August 8, 1990
    U129 All August 8, 1990
    U130 All August 8, 1990
    U131 All August 8, 1990
    U132 All August 8, 1990
    U133 All August 8, 1990
    U134 All August 8, 1990
    U135 All August 8, 1990
    U136 Wastewater August 8, 1990
    U136 Nonwastewater May 8, 1992
    U137 All August 8, 1990
    U138 All August 8, 1990
    U140 All August 8, 1990
    U141 All August 8, 1990
    U142 All August 8, 1990
    U143 All August 8, 1990
    U144 All August 8, 1990
    U145 All August 8, 1990
    U146 All August 8, 1990
    U147 All August 8, 1990
    U148 All August 8, 1990
    U149 All August 8, 1990
    U150 All August 8, 1990
    U151 Wastewater August 8, 1990
    U151 Nonwastewater May 8, 1992
    U152 All August 8, 1990
    U153 All August 8, 1990
    U154 All August 8, 1990
    U155 All August 8, 1990

     
    836
    U156 All August 8, 1990
    U157 All August 8, 1990
    U158 All August 8, 1990
    U159 All August 8, 1990
    U160 All August 8, 1990
    U161 All August 8, 1990
    U162 All August 8, 1990
    U163 All August 8, 1990
    U164 All August 8, 1990
    U165 All August 8, 1990
    U166 All August 8, 1990
    U167 All August 8, 1990
    U168 All August 8, 1990
    U169 All August 8, 1990
    U170 All August 8, 1990
    U171 All August 8, 1990
    U172 All August 8, 1990
    U173 All August 8, 1990
    U174 All August 8, 1990
    U176 All August 8, 1990
    U177 All August 8, 1990
    U178 All August 8, 1990
    U179 All August 8, 1990
    U180 All August 8, 1990
    U181 All August 8, 1990
    U182 All August 8, 1990
    U183 All August 8, 1990
    U184 All August 8, 1990
    U185 All August 8, 1990
    U186 All August 8, 1990
    U187 All August 8, 1990
    U188 All August 8, 1990
    U189 All August 8, 1990
    U190 All June 8, 1989
    U191 All August 8, 1990
    U192 All August 8, 1990
    U193 All August 8, 1990
    U194 All June 8, 1989
    U196 All August 8, 1990
    U197 All August 8, 1990
    U200 All August 8, 1990
    U201 All August 8, 1990
    U202 All August 8, 1990
    U203 All August 8, 1990
    U204 All August 8, 1990
    U205 All August 8, 1990

     
    837
    U206 All August 8, 1990
    U207 All August 8, 1990
    U208 All August 8, 1990
    U209 All August 8, 1990
    U210 All August 8, 1990
    U211 All August 8, 1990
    U213 All August 8, 1990
    U214 All August 8, 1990
    U215 All August 8, 1990
    U216 All August 8, 1990
    U217 All August 8, 1990
    U218 All August 8, 1990
    U219 All August 8, 1990
    U220 All August 8, 1990
    U221 All June 8, 1989
    U222 All August 8, 1990
    U223 All June 8, 1989
    U225 All August 8, 1990
    U226 All August 8, 1990
    U227 All August 8, 1990
    U228 All August 8, 1990
    U234 All August 8, 1990
    U235 All June 8, 1989
    U236 All August 8, 1990
    U237 All August 8, 1990
    U238 All August 8, 1990
    U239 All August 8, 1990
    U240 All August 8, 1990
    U243 All August 8, 1990
    U244 All August 8, 1990
    U246 All August 8, 1990
    U247 All August 8, 1990
    U248 All August 8, 1990
    U249 All August 8, 1990
    U271 Mixed with radioactive wastes April 8, 1998
    U271 All others July 8, 1996
    U277 Mixed with radioactive wastes April 8, 1998
    U277 All others July 8, 1996
    U278 Mixed with radioactive wastes April 8, 1998
    U278 All others July 8, 1996
    U279 Mixed with radioactive wastes April 8, 1998
    U279 All others July 8, 1996
    U280 Mixed with radioactive wastes April 8, 1998
    U280 All others July 8, 1996
    U328 Mixed with radioactive wastes June 30, 1994
    U328 All others November 9, 1992

     
    838
    U353 Mixed with radioactive wastes June 30, 1994
    U353 All others November 9, 1992
    U359 Mixed with radioactive wastes June 30, 1994
    U359 All others November 9, 1992
    U364 Mixed with radioactive wastes April 8, 1998
    U364 All others July 8, 1996
    U365 Mixed with radioactive wastes April 8, 1998
    U365 All others July 8, 1996
    U366 Mixed with radioactive wastes April 8, 1998
    U366 All others July 8, 1996
    U367 Mixed with radioactive wastes April 8, 1998
    U367 All others July 8, 1996
    U372 Mixed with radioactive wastes April 8, 1998
    U372 All others July 8, 1996
    U373 Mixed with radioactive wastes April 8, 1998
    U373 All others July 8, 1996
    U375 Mixed with radioactive wastes April 8, 1998
    U375 All others July 8, 1996
    U376 Mixed with radioactive wastes April 8, 1998
    U376 All others July 8, 1996
    U377 Mixed with radioactive wastes April 8, 1998
    U377 All others July 8, 1996
    U378 Mixed with radioactive wastes April 8, 1998
    U378 All others July 8, 1996
    U379 Mixed with radioactive wastes April 8, 1998
    U379 All others July 8, 1996
    U381 Mixed with radioactive wastes April 8, 1998
    U381 All others July 8, 1996
    U382 Mixed with radioactive wastes April 8, 1998
    U382 All others July 8, 1996
    U383 Mixed with radioactive wastes April 8, 1998
    U383 All others July 8, 1996
    U384 Mixed with radioactive wastes April 8, 1998
    U384 All others July 8, 1996
    U385 Mixed with radioactive wastes April 8, 1998
    U385 All others July 8, 1996
    U386 Mixed with radioactive wastes April 8, 1998
    U386 All others July 8, 1996
    U387 Mixed with radioactive wastes April 8, 1998
    U387 All others July 8, 1996
    U389 Mixed with radioactive wastes April 8, 1998
    U389 All others July 8, 1996
    U390 Mixed with radioactive wastes April 8, 1998
    U390 All others July 8, 1996
    U391 Mixed with radioactive wastes April 8, 1998
    U391 All others July 8, 1996

     
    839
    U392 Mixed with radioactive wastes April 8, 1998
    U392 All others July 8, 1996
    U393 Mixed with radioactive wastes April 8, 1998
    U393 All others July 8, 1996
    U394 Mixed with radioactive wastes April 8, 1998
    U394 All others July 8, 1996
    U395 Mixed with radioactive wastes April 8, 1998
    U395 All others July 8, 1996
    U396 Mixed with radioactive wastes April 8, 1998
    U396 All others July 8, 1996
    U400 Mixed with radioactive wastes April 8, 1998
    U400 All others July 8, 1996
    U401 Mixed with radioactive wastes April 8, 1998
    U401 All others July 8, 1996
    U402 Mixed with radioactive wastes April 8, 1998
    U402 All others July 8, 1996
    U403 Mixed with radioactive wastes April 8, 1998
    U403 All others July 8, 1996
    U404 Mixed with radioactive wastes April 8, 1998
    U404 All others July 8, 1996
    U407 Mixed with radioactive wastes April 8, 1998
    U407 All others July 8, 1996
    U409 Mixed with radioactive wastes April 8, 1998
    U409 All others July 8, 1996
    U410 Mixed with radioactive wastes April 8, 1998
    U410 All others July 8, 1996
    U411 Mixed with radioactive wastes April 8, 1998
    U411 All others July 8, 1996
     
    a
    This table does not include mixed radioactive wastes (from the First, Second, and Third
    Third rules) that are receiving a national capacity variance until May 8, 1992. This table
    also does not include contaminated soil and debris wastes.
     
    b
    The standard was revised in the Third Third Final Rule (adopted by USEPA at 55 Fed.
    Reg. 22520 (June 1, 1990) and by, which the Board adopted in docket R90-11 by orders
    dated April 11, May 23, and August 8 and 22, 1991) at 15 Ill. Reg. 9462, effective June
    17, 1991.
     
    c
    USEPA amended the standard in the Third Third Emergency Rule (at 58 Fed. Reg. 29860
    (May 24, 1993), which the Board adopted in docket R93-16 on March 17, 1994 at 18 Ill.
    Reg. 6799, effective April 26, 1994); the original effective date was August 8, 1990.
     
    d
    The standard was revised in the Phase II Final Rule (that USEPA adopted at 59 Fed. Reg.
    47982 (September 19, 1994) and, which the Board adopted in docket R95-6 by orders
    dated June 1 and 15, 1995 at 19 Ill. Reg. 9660, effective June 27, 1995); the original
    effective date was August 8, 1990.

     
    840
     
    e
    The standards for selected reactive wastes was revised in the Phase III Final Rule (that
    USEPA adopted at 61 Fed. Reg. 15566 (April 8, 1996) and, which the Board adopted in
    docket R96-10/R97-3/R97-5 (consolidated) by an order dated November 6, 1997 at 22
    Ill. Reg. 783, effective December 16, 1997); the original effective date was August 8,
    1990.
     
    TABLE 2
    SUMMARY OF EFFECTIVE DATES OF LAND DISPOSAL RESTRICTIONS
    FOR CONTAMINATED SOIL AND DEBRIS (CSD)
     
    Restricted hazardous waste in CSD Effective date
    1. Solvent- (F001-F005) and dioxin- (F020-F023 and F026-F028) containing soil
    and debris from CERCLA response or RCRA corrective actions.
    November 8, 1990
    2. Soil and debris not from CERCLA response or RCRA corrective actions
    contaminated with less than one percent total solvents (F001-F005) or dioxins
    (F020-F023 and F026-F028).
    November 8, 1988
    3. All soil and debris contaminated with First Third wastes for which treatment
    standards are based on incineration.
    August 8, 1990
    4. All soil and debris contaminated with Second Third wastes for which treatment
    standards are based on incineration.
    June 8, 1991
    5. All soil and debris contaminated with Third Third wastes or, First or Second
    Third “soft hammer” wastes that had treatment standards promulgated in the
    Third Third rule, for which treatment standards are based on incineration,
    vitrification, or mercury retorting, acid leaching followed by chemical
    precipitation, or thermal recovery of metals, as well as all inorganic solids debris
    contaminated with D004-D011 wastes, and all soil and debris contaminated with
    mixed RCRA/radioactive wastes.
    May 8, 1992
    6. Soil and debris contaminated with D012-D043, K141-K145, and K147-151
    wastes.
    December 19,
    1994
    7. Debris (only) contaminated with F037, F038, K107-K112, K117, K118,
    K123-K126, K131, K132, K136, U328, U353, U359.
    December 19,
    1994
    8. Soil and debris contaminated with K156- K161, P127, P128, P188-P192,
    P194, P196- P199, P201-P205, U271, U277-U280, U364-U367, U372, U373,
    U375-U379, U381-U387, U389-U396, U400-U404, U407, and U409-U411
    wastes.
    July 8, 1996
    9. Soil and debris contaminated with K088 wastes. October 8, 1997
    10. Soil and debris contaminated with radioactive wastes mixed with K088,
    K156-K161, P127, P128, P188-P192, P194, P196-P199, P201-P205, U271,
    U277-U280, U364-U367, U372, U373, U375-U379, U381-U387, U389-
    U396, U400-U404, U407, and U409-U411 wastes.
    April 8, 1998
    11. Soil and debris contaminated with F032, F034, and F035. May 12, 1997
    12. Soil and debris contaminated with newly identified D004-D011 toxicity
    characteristic wastes and mineral processing wastes.
    August 24, 1998
    13. Soil and debris contaminated with mixed radioactive newly identified D011
    characteristic wastes and mineral processing wastes.
    May 26, 2000

     
    841
     
    BOARD NOTE: This table is These tables are provided for the convenience of the reader.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.Appendix I EP Toxicity Test Method and Structural Integrity Test
     
    Note: The EP (Method 1310 1310B (the Extraction Procedure Toxicity Test) is published in “Test
    Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA Publication
    publication number EPA-530/SW-846, as incorporated by reference in 35 Ill. Adm. Code 720.111
    720.111(a).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.Table C Technology Codes and Description of Technology-Based
    Standards
     
    Technology
    Code Description of Technology-Based Standard
     
    ADGAS Venting of compressed gases into an absorbing or reacting media (i.e., solid or
    liquid)--venting can be accomplished through physical release utilizing valves or
    piping; physical penetration of the container; or penetration through detonation.
     
    AMLGM Amalgamation of liquid, elemental mercury contaminated with radioactive
    materials utilizing inorganic reagents such as copper, zinc, nickel, gold, and sulfur
    that result in a nonliquid, semi-solid amalgam and thereby reducing potential
    emissions of elemental mercury vapors to the air.
     
    BIODG Biodegradation of organics or non-metallic inorganics (i.e., degradable inorganics
    that contain the elements of phosphorus, nitrogen, and sulfur) in units operated
    under either aerobic or anaerobic conditions such that a surrogate compound or
    indicator parameter has been substantially reduced in concentration in the
    residuals (e.g., total organic carbon (TOC) can often be used as an indicator
    parameter for the biodegradation of many organic constituents that cannot be
    directly analyzed in wastewater residues).
     
    CARBN Carbon adsorption (granulated or powdered) of non-metallic inorganics, organo-
    metallics, or organic constituents, operated so that a surrogate compound or
    indicator parameter has not undergone breakthrough (e.g., total organic carbon
    (TOC) can often be used as an indicator parameter for the adsorption of many
    organic constituents that cannot be directly analyzed in wastewater residues).
    Breakthrough occurs when the carbon has become saturated with the constituent
    (or indicator parameter) and substantial change in adsorption rate associated with
    that constituent occurs.
     

     
    842
    CHOXD Chemical or electrolytic oxidation utilizing the following oxidation reagents (or
    waste reagents) or combinations or reagents:
     
    1) hypochlorite (e.g., bleach);
     
    2) chlorine;
     
    3) chlorine dioxide;
     
    4) ozone or UV (ultraviolet light) assisted ozone;
     
    5) peroxides;
     
    6) persulfates;
     
    7) perchlorates;
     
    8) permanganates; or
     
    9) other oxidizing reagents of equivalent efficiency, performed in units
    operated so that a surrogate compound or indicator parameter has been
    substantially reduced in concentration in the residuals (e.g., total organic
    carbon (TOC) can often be used as an indicator parameter for the
    oxidation of many organic constituents that cannot be directly analyzed in
    wastewater residues). Chemical oxidation specifically includes what is
    commonly referred to as alkaline chlorination.
     
    CHRED Chemical reduction utilizing the following reducing reagents (or waste reagents)
    or combinations of reagents:
     
    1) sulfur dioxide;
     
    2) sodium, potassium, or alkali salts of sulfites, bisulfites, metabisulfites, and
    polyethylene glycols (e.g., NaPEG and KPEG);
     
    3) sodium hydrosulfide;
     
    4) ferrous salts; or
     
    5) other reducing reagents of equivalent efficiency, performed in units
    operated such that a surrogate compound or indicator parameter has been
    substantially reduced in concentration in the residuals (e.g., total organic
    halogens (TOX) can often be used as an indicator parameter for the
    reduction of many halogenated organic constituents that cannot be directly
    analyzed in wastewater residues). Chemical reduction is commonly used
    for the reduction of hexavalent chromium to the trivalent state.

     
    843
     
    CMBST High temperature organic destruction technologies, such as combustion in
    incinerators, boilers, or industrial furnaces operated in accordance with the
    applicable requirements of Subpart O of 35 Ill. Adm. Code 724, Subpart O of 35
    Ill. Adm. Code 725, or Subpart H of 35 Ill. Adm. Code 726, and in other units
    operated in accordance with applicable technical operating requirements; and
    certain non-combustive technologies, such as the Catalytic Extraction Process.
     
    DEACT Deactivation to remove the hazardous characteristics of a waste due to its
    ignitability, corrosivity, or reactivity.
     
    FSUBS Fuel substitution in units operated in accordance with applicable technical
    operating requirements.
     
    HLVIT Vitrification of high-level mixed radioactive wastes in units in compliance with
    all applicable radioactive protection requirements under control of the federal
    Nuclear Regulatory Commission.
     
    IMERC Incineration of wastes containing organics and mercury in units operated in
    accordance with the technical operating requirements of Subpart O of 35 Ill.
    Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725. All wastewater and
    nonwastewater residues derived from this process must then comply with the
    corresponding treatment standards per waste code with consideration of any
    applicable subcategories (e.g., high or low mercury subcategories).
     
    INCIN Incineration in units operated in accordance with the technical operating
    requirements of Subpart O of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm.
    Code 725.
     
    LLEXT Liquid-liquid extraction (often referred to as solvent extraction) of organics from
    liquid wastes into an immiscible solvent for which the hazardous constituents
    have a greater solvent affinity, resulting in an extract high in organics that must
    undergo either incineration, reuse as a fuel, or other recovery or reuse and a
    raffinate (extracted liquid waste) proportionately low in organics that must
    undergo further treatment as specified in the standard.
     
    MACRO Macroencapsulation with surface coating materials such as polymeric organics
    (e.g., resins and plastics) or with a jacket of inert inorganic materials to
    substantially reduce surface exposure to potential leaching media.
    Macroencapsulation specifically does not include any material that would be
    classified as a tank or container according to 35 Ill. Adm. Code 720.110.
     
    NEUTR Neutralization with the following reagents (or waste reagents) or combinations of
    reagents:
     
    1) acids;

     
    844
     
    2) bases; or
     
    3) water (including wastewaters) resulting in a pH greater than two but less
    than 12.5 as measured in the aqueous residuals.
     
    NLDBR No land disposal based on recycling.
     
    POLYM Formation of complex high-molecular weight solids through polymerization of
    monomers in high-TOC D001 nonwastewaters that are chemical components in
    the manufacture of plastics.
     
    PRECP Chemical precipitation of metals and other inorganics as insoluble precipitates of
    oxides, hydroxides, carbonates, sulfides, sulfates, chlorides, fluorides, or
    phosphates. The following reagents (or waste reagents) are typically used alone
    or in combination:
     
    1) lime (i.e., containing oxides or hydroxides of calcium or magnesium);
     
    2) caustic (i.e., sodium or potassium hydroxides);
     
    3) soda ash (i.e., sodium carbonate);
     
    4) sodium sulfide;
     
    5) ferric sulfate or ferric chloride;
     
    6) alum; or
     
    7) sodium sulfate. Additional flocculating, coagulation, or similar reagents
    or processes that enhance sludge dewatering characteristics are not
    precluded from use.
     
    RBERY Thermal recovery of beryllium.
     
    RCGAS Recovery or reuse of compressed gases including techniques such as reprocessing
    of the gases for reuse or resale; filtering or adsorption of impurities; remixing for
    direct reuse or resale; and use of the gas as a fuel source.
     
    RCORR Recovery of acids or bases utilizing one or more of the following recovery
    technologies:
     
    1) distillation (i.e., thermal concentration);
     
    2) ion exchange;
     

     
    845
    3) resin or solid adsorption;
     
    4) reverse osmosis; or
     
    5) incineration for the recovery of acid
     
    Note: this does not preclude the use of other physical phase separation or
    concentration techniques such as decantation, filtration (including ultrafiltration),
    and centrifugation, when used in conjunction with the above listed recovery
    technologies.
     
    RLEAD Thermal recovery of lead in secondary lead smelters.
     
    RMERC Retorting or roasting in a thermal processing unit capable of volatilizing mercury
    and subsequently condensing the volatilized mercury for recovery. The retorting
    or roasting unit (or facility) must be subject to one or more of the following:
     
    a) A federal
    national emissions standard for hazardous air pollutants
    (NESHAP) for mercury (subpart E of 40 CFR 61, Subpart E);
     
    b) A best available control technology (BACT) or a lowest achievable
    emission rate (LAER) standard for mercury imposed pursuant to a
    prevention of significant deterioration (PSD) permit (including 35 Ill.
    Adm. Code 201 through 203); or
     
    c) A state permit that establishes emission limitations (within meaning of
    Section 302 of the Clean Air Act) for mercury, including a permit issued
    pursuant to 35 Ill. Adm. Code 201. All wastewater and nonwastewater
    residues derived from this process must then comply with the
    corresponding treatment standards per waste code with consideration of
    any applicable subcategories (e.g., high or low mercury subcategories).
     
    RMETL Recovery of metals or inorganics utilizing one or more of the following direct
    physical or removal technologies:
     
    1) ion exchange;
     
    2) resin or solid (i.e., zeolites) adsorption;
     
    3) reverse osmosis;
     
    4) chelation or solvent extraction;
     
    5) freeze crystallization;
     
    6) ultrafiltration; or

     
    846
     
    7) simple precipitation (i.e., crystallization)
     
    Note: this does not preclude the use of other physical phase separation or
    concentration techniques such as decantation, filtration (including ultrafiltration),
    and centrifugation, when used in conjunction with the above listed recovery
    technologies.
     
    RORGS Recovery of organics utilizing one or more of the following technologies:
     
    1) Distillation;
     
    2) thin film evaporation;
     
    3) steam stripping;
     
    4) carbon adsorption;
     
    5) critical fluid extraction;
     
    6) liquid-liquid extraction;
     
    7) precipitation or crystallization (including freeze crystallization); or
     
    8) chemical phase separation techniques (i.e., addition of acids, bases,
    demulsifiers, or similar chemicals).
     
    Note: This does not preclude the use of other physical phase separation
    techniques such as decantation, filtration (including ultrafiltration), and
    centrifugation, when used in conjunction with the above listed recovery
    technologies.
     
    RTHRM Thermal recovery of metals or inorganics from nonwastewaters in units defined as
    cement kilns, blast furnaces, smelting, melting and refining furnaces, combustion
    devices used to recover sulfur values from spent sulfuric acid and “other devices”
    determined by the Agency pursuant to 35 Ill. Adm. Code 720.110, the definition
    of “industrial furnace.”
     
    RZINC Resmelting in high temperature metal recovery units for the purpose of recovery
    of zinc.
     
    STABL Stabilization with the following reagents (or waste reagents) or combinations of
    reagents:
     
    1) Portland cement; or
     

     
    847
    2) lime or pozzolans (e.g., fly ash and cement kiln dust)--this does not
    preclude the addition of reagents (e.g., iron salts, silicates, and clays)
    designed to enhance the set or cure time or compressive strength, or to
    overall reduce the leachability of the metal or inorganic.
     
    SSTRP Steam stripping of organics from liquid wastes utilizing direct application of
    steam to the wastes operated such that liquid and vapor flow rates, as well as,
    temperature and pressure ranges have been optimized, monitored, and
    maintained. These operating parameters are dependent upon the design
    parameters of the unit such as, the number of separation stages and the internal
    column design. Thus, resulting in a condensed extract high in organics that must
    undergo either incineration, reuse as a fuel, or other recovery or reuse and an
    extracted wastewater that must undergo further treatment as specified in the
    standard.
     
    WETOX Wet air oxidation performed in units operated such that a surrogate compound or
    indicator parameter has been substantially reduced in concentration in the
    residuals (e.g., total organic carbon (TOC) can often be used as an indicator
    parameter for the oxidation of many organic constituents that cannot be directly
    analyzed in wastewater residues).
     
    WTRRX Controlled reaction with water for highly reactive inorganic or organic chemicals
    with precautionary controls for protection of workers from potential violent
    reactions as well as precautionary controls for potential emissions of toxic or
    ignitable levels of gases released during the reaction.
     
    Note 1: When a combination of these technologies (i.e., a treatment train) is specified as a
    single treatment standard, the order of application is specified in Table T to this
    Part by indicating the five letter technology code that must be applied first, then
    the designation “fb.” (an abbreviation for “followed by”), then the five letter
    technology code for the technology that must be applied next, and so on.
     
    Note 2: When more than one technology (or treatment train) are specified as alternative
    treatment standards, the five letter technology codes (or the treatment trains) are
    separated by a semicolon (;) with the last technology preceded by the word
    “OR.” This indicates that any one of these BDAT technologies or treatment
    trains can be used for compliance with the standard.
     
    BOARD NOTE: Derived from Table I in 40 CFR 268.42, Table 1 (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.Table H Wastes Excluded from CCW Treatment Standards
     
    The following facilities are excluded from the treatment standard under Section 728.143(a) and
    Table B to this Part, and are subject to the following constituent concentrations. These facilities

     
    848
    have received a treatability exception by regulatory action from USEPA pursuant to 40 CFR 268.44
    (2002), and have demonstrated that the Board needs to adopt the treatability exception as part of the
    Illinois RCRA program. The Board may also grant an “adjusted treatment standard” pursuant to
    Section 728.144.
     
    Facility name
    and address
    Waste
    Code
    See
    Also
    Regulated
    hazardous
    constituent
    Wastewaters
    Concentration
    (mg/Lmg/
    ) Notes
    Nonwaste-
    waters
    Concentration
    (mg/Lmg/kg) Notes
     
    Craftsman
    Plating and
    Tinning Corp.,
    Chicago, IL
    F006 Section
    728.140
    Cyanides
    (Total)
    1.2 B 18001,800 D
    Cyanides
    (amenable)
    0.86 B and
    C
    30 D
    Cadmium 1.6 NA
    Chromium 0.32 NA
    Lead 0.40 NA
    Nickel 0.44 NA
     
    Northwestern
    Plating Works,
    Inc., Chicago,
    IL
    F006 Section
    728.140
    Cyanides
    (Total)
    1.2 B 970 D
    Cyanides
    (amenable)
    0.86 B and
    C
    30 D
    Cadmium 1.6 NA
    Chromium 0.32 NA
    Lead 0.40 NA
    Nickel 0.44 NA
     
    Notes:
     
    A An owner or operator may certify compliance with these treatment standards according to
    the provisions of Section 728.107.
     
    B Cyanide wastewater standards for F006 are based on analysis of composite samples.
     
    C These owners and operators must comply with 0.86 mg/Lmg/
    for amenable cyanides in the
    wastewater exiting the alkaline chlorination system. These owners and operators must also
    comply with Section 728.107(a)(4) for appropriate monitoring frequency consistent with the
    facilities’ waste analysis plan.
     
    D Cyanide nonwastewaters are analyzed using SW-846 Method 9010 9010C (Total and
    Amenable Cyanide: Distillation) or 9012 9012B (Total and Amenable Cyanide

     
    849
    (Automated Colorimetric, with Off-Line Distillation)) in “Test Methods for Evaluating
    Solid Waste, Physical/Chemical Methods,” USEPA publication number EPA530/SW-
    846, incorporated by reference in 35 Ill. Adm. Code 720.111(b), with a sample size 10 g,
    distillation time one hour and fifteen minutes. SW-846 is incorporated by reference in 35
    Ill. Adm. Code 720.111.
     
    NA Not applicable.
     
    BOARD NOTE: Derived from table to 40 CFR 268.44(o) (2002) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 728.Table T Treatment Standards for Hazardous Wastes
     
    Note: The treatment standards that heretofore appeared in tables in Sections 728.141, 728.142,
    and 728.143 have been consolidated into this table.
     
    Waste Code
    Waste Description and Treatment or Regulatory Subcategory
    1
     
    Regulated Hazardous Constituent Wastewaters Nonwastewaters
    Common Name CAS
    2
    Number
    Concentration in
    mg/lmg/
    3
    ; or
    Technology Code
    4
     
    Concentration in
    mg/kg
    5
    unless
    noted as
    “mg/lmg/
    TCLP”;
    or Technology
    Code
    4
     
    D001
    9
     
    Ignitable Characteristic Wastes, except for the 35 Ill. Adm. Code 721.121(a)(1) High TOC
    Subcategory.
    NA NA DEACT and meet
    Section 728.148
    standards
    8
    ; or
    RORGS; or
    CMBST
    DEACT and meet
    Section 728.148
    standards
    8
    ; or
    RORGS; or
    CMBST
     
    D001
    9
     
    High TOC Ignitable Characteristic Liquids Subcategory based on 35 Ill. Adm. Code
    721.121(a)(1) - Greater than or equal to 10 percent total organic carbon.
    (Note: This subcategory consists of nonwastewaters only.)
    NA NA NA RORGS; CMBST;
    or POLYM
     

     
    850
    D002
    9
     
    Corrosive Characteristic Wastes.
    NA NA DEACT and meet
    Section 728.148
    standards
    8
     
    DEACT and meet
    Section 728.148
    standards
    8
     
     
    D002, D004, D005, D006, D007, D008, D009, D010, D011
    Radioactive high level wastes generated during the reprocessing of fuel rods.
    (Note: This subcategory consists of nonwastewaters only.)
    Corrosivity (pH) NA NA HLVIT
    Arsenic 7440-38-2 NA HLVIT
    Barium 7440-39-3 NA HLVIT
    Cadmium 7440-43-9 NA HLVIT
    Chromium (Total) 7440-47-3 NA HLVIT
    Lead 7439-92-1 NA HLVIT
    Mercury 7439-97-6 NA HLVIT
    Selenium 7782-49-2 NA HLVIT
    Silver 7440-22-4 NA HLVIT
     
    D003
    9
     
    Reactive Sulfides Subcategory based on 35 Ill. Adm. Code 721.123(a)(5).
    NA NA DEACT DEACT
     
    D003
    9
     
    Explosive subcategory based on 35 Ill. Adm. Code 721.123(a)(6), (a)(7), and (a)(8).
    NA NA DEACT and meet
    Section 728.148
    standards
    8
     
    DEACT and meet
    Section 728.148
    standards
    8
     
     
    D003
    9
     
    Unexploded ordnance and other explosive devices that have been the subject of an emergency
    response.
    NA NA DEACT DEACT
     
    D003
    9
     
    Other Reactives Subcategory based on 35 Ill. Adm. Code 721.123(a)(1).
    NA NA DEACT and meet
    Section 728.148
    standards
    8
     
    DEACT and meet
    Section 728.148
    standards
    8
     
     
    D003
    9
     
    Water Reactive Subcategory based on 35 Ill. Adm. Code 721.123(a)(2), (a)(3), and (a)(4).
    (Note: This subcategory consists of nonwastewaters only.)
    NA NA NA DEACT and meet
    Section 728.148
    standards
    8
     

     
    851
     
    D003
    9
     
    Reactive Cyanides Subcategory based on 35 Ill. Adm. Code 721.123(a)(5).
    Cyanides (Total)
    7
    57-12-5 -- 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
     
    D004
    9
     
    Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for arsenic based on
    the toxicity characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching
    Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”
    USEPA publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill.
    Adm. Code 720.111(a).
    Arsenic 7440-38-2 1.4 and meet
    Section 728.148
    standards
    8
     
    5.0 mg/lmg/
     
    TCLP and meet
    Section 728.148
    standards
    8
     
     
    D005
    9
     
    Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for barium based on
    the toxicity characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching
    Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”
    USEPA publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill.
    Adm. Code 720.111(a).
    Barium 7440-39-3 1.2 and meet
    Section 728.148
    standards
    8
     
    21 mg/lmg/
    TCLP
    and meet Section
    728.148 standards
    8
     
     
    D006
    9
     
    Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for cadmium based
    on the toxicity characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching
    Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”
    USEPA publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill.
    Adm. Code 720.111(a).
    Cadmium 7440-43-9 0.69 and meet
    Section 728.148
    standards
    8
     
    0.11 mg/lmg/
     
    TCLP and meet
    Section 728.148
    standards
    8
     
     
    D006
    9
     
    Cadmium-Containing Batteries Subcategory.
    (Note: This subcategory consists of nonwastewaters only.)
    Cadmium 7440-43-9 NA RTHRM
     

     
    852
    D006
    9
     
    Radioactively contaminated cadmium-containing batteries.
    (Note: This subcategory consists of nonwastewaters only.)
    Cadmium 7440-43-9 NA Macroencapsula-
    tion in accordance
    with Section
    728.145
     
    D007
    9
     
    Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for chromium based
    on the toxicity characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching
    Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”
    USEPA publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill.
    Adm. Code 720.111(a).
    Chromium (Total) 7440-47-3 2.77 and meet
    Section 728.148
    standards
    8
     
    0.60 mg/lmg/
     
    TCLP and meet
    Section 728.148
    standards
    8
     
     
    D008
    9
     
    Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for lead based on the
    toxicity characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching
    Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”
    USEPA publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill.
    Adm. Code 720.111(a).
    Lead 7439-92-1 0.69 and meet
    Section 728.148
    standards
    8
     
    0.75 mg/lmg/
     
    TCLP and meet
    Section 728.148
    standards
    8
     
     
    D008
    9
     
    Lead Acid Batteries Subcategory
    (Note: This standard only applies to lead acid batteries that are identified as RCRA hazardous
    wastes and that are not excluded elsewhere from regulation under the land disposal restrictions
    of this Part or exempted under other regulations (see 35 Ill. Adm. Code 726.180). This
    subcategory consists of nonwastewaters only.)
    Lead 7439-92-1 NA RLEAD
     
    D008
    9
     
    Radioactive Lead Solids Subcategory
    (Note: These lead solids include, but are not limited to, all forms of lead shielding and other
    elemental forms of lead. These lead solids do not include treatment residuals such as hydroxide
    sludges, other wastewater treatment residuals, or incinerator ashes that can undergo conventional
    pozzolanic stabilization, nor do they include organo-lead materials that can be incinerated and
    stabilized as ash. This subcategory consists of nonwastewaters only.)
    Lead 7439-92-1 NA MACRO

     
    853
     
    D009
    9
     
    Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury
    based on the toxicity characteristic leaching procedure Method 1311 (Toxicity Characteristic
    Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical
    Methods,” USEPA publication number EPA530/SW-846 Method 1311, incorporated by
    reference in 35 Ill. Adm. Code 720.111(a); and contain greater than or equal to 260 mg/kg total
    mercury that also contain organics and are not incinerator residues. (High Mercury-Organic
    Subcategory)
    Mercury 7439-97-6 NA IMERC; or
    RMERC
     
    D009
    9
     
    Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury
    based on the toxicity characteristic leaching procedure Method 1311 (Toxicity Characteristic
    Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical
    Methods,” USEPA publication number EPA530/SW-846 Method 1311, incorporated by
    reference in 35 Ill. Adm. Code 720.111(a); and contain greater than or equal to 260 mg/kg total
    mercury that are inorganic, including incinerator residues and residues from RMERC. (High
    Mercury-Inorganic Subcategory)
    Mercury 7439-97-6 NA RMERC
     
    D009
    9
     
    Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury
    based on the toxicity characteristic leaching procedure Method 1311 (Toxicity Characteristic
    Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical
    Methods,” USEPA publication number EPA530/SW-846 Method 1311, incorporated by
    reference in 35 Ill. Adm. Code 720.111(a); and contain less than 260 mg/kg total mercury. (Low
    Mercury Subcategory)
    Mercury 7439-97-6 NA 0.20 mg/lmg/
     
    TCLP and meet
    Section 728.148
    standards
    8
     
     
    D009
    9
     
    All other nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for
    mercury based on the toxicity characteristic leaching procedure Method 1311 (Toxicity
    Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods,” USEPA publication number EPA530/SW-846 Method 1311,
    incorporated by reference in 35 Ill. Adm. Code 720.111(a); and contain less than 260 mg/kg total
    mercury and that are not residues from RMERC. (Low Mercury Subcategory)
    Mercury 7439-97-6 NA 0.025 mg/lmg/
     
    TCLP and meet
    Section 728.148
    standards
    8
     
     

     
    854
    D009
    9
     
    All D009 wastewaters.
    Mercury 7439-97-6 0.15 and meet
    Section 728.148
    standards
    8
     
    NA
     
    D009
    9
     
    Elemental mercury contaminated with radioactive materials.
    (Note: This subcategory consists of nonwastewaters only.)
    Mercury 7439-97-6 NA AMLGM
     
    D009
    9
     
    Hydraulic oil contaminated with Mercury Radioactive Materials Subcategory.
    (Note: This subcategory consists of nonwastewaters only.)
    Mercury 7439-97-6 NA IMERC
     
    D009
    9
     
    Radioactively contaminated mercury-containing batteries.
    (Note: This subcategory consists of nonwastewaters only.)
    Mercury 7439-97-6 NA Macroencapsula-
    tion in accordance
    with Section
    728.145
     
    D010
    9
     
    Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for selenium based
    on the toxicity characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching
    Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”
    USEPA publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill.
    Adm. Code 720.111(a).
    Selenium 7782-49-2 0.82 5.7 mg/lmg/
     
    TCLP and meet
    Section 728.148
    standards
    8
     
     
    D011
    9
     
    Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for silver based on
    the toxicity characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching
    Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”
    USEPA publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill.
    Adm. Code 720.111(a).
    Silver 7440-22-4 0.43 0.14 mg/lmg/
     
    TCLP and meet
    Section 728.148
    standards
    8
     
     

     
    855
    D011
    9
     
    Radioactively contaminated silver-containing batteries.
    (Note: This subcategory consists of nonwastewaters only.)
    Silver 7440-22-4 NA Macroencapsula-
    tion in accordance
    with Section
    728.145
     
    D012
    9
     
    Wastes that are TC for Endrin endrin based on the toxicity characteristic leaching procedure
    Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Endrin 72-20-8 BIODG; or
    CMBST
    0.13 and meet
    Section 728.148
    standards
    8
     
    Endrin aldehyde 7421-93-4 BIODG; or
    CMBST
    0.13 and meet
    Section 728.148
    standards
    8
     
     
    D013
    9
     
    Wastes that are TC for Lindane lindane based on the toxicity characteristic leaching procedure
    Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    α
    -BHC
    319-84-6 CARBN; or
    CMBST
    0.066 and meet
    Section 728.148
    standards
    8
     
    β
    -BHC
    319-85-7 CARBN; or
    CMBST
    0.066 and meet
    Section 728.148
    standards
    8
     
    δ
    -BHC
    319-86-8 CARBN; or
    CMBST
    0.066 and meet
    Section 728.148
    standards
    8
     
    γ
    -BHC (Lindane)
    58-89-9 CARBN; or
    CMBST
    0.066 and meet
    Section 728.148
    standards
    8
     
     
    D014
    9
     
    Wastes that are TC for Methoxychlor based on the toxicity characteristic leaching procedure
    Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Methoxychlor 72-43-5 WETOX or
    CMBST
    0.18 and meet
    Section 728.148
    standards
    8
     

     
    856
     
    D015
    9
     
    Wastes that are TC for Toxaphene based on the toxicity characteristic leaching procedure
    Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Toxaphene 8001-35-2 BIODG or
    CMBST
    2.6 and meet
    Section 728.148
    standards
    8
     
     
    D016
    9
     
    Wastes that are TC for 2,4-D (2,4-Dichlorophenoxyacetic Acid2,4-dichlorophenoxyacetic acid)
    based on the toxicity characteristic leaching procedure Method 1311 (Toxicity Characteristic
    Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical
    Methods,” USEPA publication number EPA530/SW-846 Method 1311, incorporated by
    reference in 35 Ill. Adm. Code 720.111(a).
    2,4-D (2,4-Dichloro-
    phenoxyacetic Acid
    2,4-dichlorophenoxyacetic acid)
    94-75-7 CHOXD; BIODG;
    or CMBST
    10 and meet
    Section 728.148
    standards
    8
     
     
    D017
    9
     
    Wastes that are TC for 2,4,5-TP (Silvex) based on the toxicity characteristic leaching procedure
    Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    2,4,5-TP (Silvex) 93-72-1 CHOXD or
    CMBST
    7.9 and meet
    Section 728.148
    standards
    8
     
     
    D018
    9
     
    Wastes that are TC for Benzene benzene based on the toxicity characteristic leaching procedure
    Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Benzene 71-43-2 0.14 and meet
    Section 728.148
    standards
    8
     
    10 and meet
    Section 728.148
    standards
    8
     
     
    D019
    9
     
    Wastes that are TC for Carbon carbon tetrachloride based on the toxicity characteristic leaching
    procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods
    for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Carbon tetrachloride 56-23-5 0.057 and meet
    Section 728.148
    standards
    8
     
    6.0 and meet
    Section 728.148
    standards
    8
     

     
    857
     
    D020
    9
     
    Wastes that are TC for Chlordane chlordane based on the toxicity characteristic leaching
    procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods
    for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Chlordane (
    α
    and
    χ
    isomers)
    57-74-9 0.0033 and meet
    Section 728.148
    standards
    8
     
    0.26 and meet
    Section 728.148
    standards
    8
     
     
    D021
    9
     
    Wastes that are TC for Chlorobenzene chlorobenzene based on the toxicity characteristic
    leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test
    Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Chlorobenzene 108-90-7 0.057 and meet
    Section 728.148
    standards
    8
     
    6.0 and meet
    Section 728.148
    standards
    8
     
     
    D022
    9
     
    Wastes that are TC for Chloroform chloroform based on the toxicity characteristic leaching
    procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods
    for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Chloroform 67-66-3 0.046 and meet
    Section 728.148
    standards
    8
     
    6.0 and meet
    Section 728.148
    standards
    8
     
     
    D023
    9
     
    Wastes that are TC for o-Cresol o-cresol based on the toxicity characteristic leaching procedure
    Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    o-Cresol 95-48-7 0.11 and meet
    Section 728.148
    standards
    8
     
    5.6 and meet
    Section 728.148
    standards
    8
     
     
    D024
    9
     
    Wastes that are TC for m-Cresol m-cresol based on the toxicity characteristic leaching procedure
    Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    m-Cresol
    (difficult to distinguish from p-
    cresol)
    108-39-4 0.77 and meet
    Section 728.148
    standards
    8
     
    5.6 and meet
    Section 728.148
    standards
    8
     
     

     
    858
    D025
    9
     
    Wastes that are TC for p-Cresol p-cresol based on the toxicity characteristic leaching procedure
    Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    p-Cresol
    (difficult to distinguish from m-
    cresol)
    106-44-5 0.77 and meet
    Section 728.148
    standards
    8
     
    5.6 and meet
    Section 728.148
    standards
    8
     
     
    D026
    9
     
    Wastes that are TC for Cresols (Total) cresols (total) based on the toxicity characteristic leaching
    procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods
    for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Cresol-mixed isomers (Cresylic
    acid)
    (sum of o-, m-, and p-cresol
    concentrations)
    1319-77-3 0.88 and meet
    Section 728.148
    standards
    8
     
    11.2 and meet
    Section 728.148
    standards
    8
     
     
    D027
    9
     
    Wastes that are TC for p-Dichlorobenzene p-dichlorobenzene based on the toxicity characteristic
    leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test
    Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    p-Dichlorobenzene (1,4-
    Dichlorobenzene)
    106-46-7 0.090 and meet
    Section 728.148
    standards
    8
     
    6.0 and meet
    Section 728.148
    standards
    8
     
     
    D028
    9
     
    Wastes that are TC for 1,2-Dichloroethane 1,2-dichloroethane based on the toxicity
    characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure
    (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm.
    Code 720.111(a).
    1,2-Dichloroethane 107-06-2 0.21 and meet
    Section 728.148
    standards
    8
     
    6.0 and meet
    Section 728.148
    standards
    8
     
     

     
    859
    D029
    9
     
    Wastes that are TC for 1,1-Dichloroethylene 1,1-dichloroethylene based on the toxicity
    characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure
    (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm.
    Code 720.111(a).
    1,1-Dichloroethylene 75-35-4 0.025 and meet
    Section 728.148
    standards
    8
     
    6.0 and meet
    Section 728.148
    standards
    8
     
     
    D030
    9
     
    Wastes that are TC for 2,4-Dinitrotoluene 2,4-dinitrotoluene based on the toxicity characteristic
    leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test
    Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    2,4-Dinitrotoluene 121-14-2 0.32 and meet
    Section 728.148
    standards
    8
     
    140 and meet
    Section 728.148
    standards
    8
     
     
    D031
    9
     
    Wastes that are TC for Heptachlor heptachlor based on the toxicity characteristic leaching
    procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods
    for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Heptachlor 76-44-8 0.0012 and meet
    Section 728.148
    standards
    8
     
    0.066 and meet
    Section 728.148
    standards
    8
     
    Heptachlor epoxide 1024-57-3 0.016 and meet
    Section 728.148
    standards
    8
     
    0.066 and meet
    Section 728.148
    standards
    8
     
     
    D032
    9
     
    Wastes that are TC for Hexachlorobenzene hexachlorobenzene based on the toxicity
    characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure
    (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm.
    Code 720.111(a).
    Hexachlorobenzene 118-74-1 0.055 and meet
    Section 728.148
    standards
    8
     
    10 and meet
    Section 728.148
    standards
    8
     
     
    D033
    9
     
    Wastes that are TC for Hexachlorobutadiene hexachlorobutadiene based on the toxicity
    characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure
    (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm.

     
    860
    Code 720.111(a).
    Hexachlorobutadiene 87-68-3 0.055 and meet
    Section 728.148
    standards
    8
     
    5.6 and meet
    Section 728.148
    standards
    8
     
     
    D034
    9
     
    Wastes that are TC for Hexachloroethane hexachloroethane based on the toxicity characteristic
    leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test
    Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Hexachloroethane 67-72-1 0.055 and meet
    Section 728.148
    standards
    8
     
    30 and meet
    Section 728.148
    standards
    8
     
     
    D035
    9
     
    Wastes that are TC for Methyl methyl ethyl ketone based on the toxicity characteristic leaching
    procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods
    for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Methyl ethyl ketone 78-93-3 0.28 and meet
    Section 728.148
    standards
    8
     
    36 and meet
    Section 728.148
    standards
    8
     
     
    D036
    9
     
    Wastes that are TC for Nitrobenzene nitrobenzene based on the toxicity characteristic leaching
    procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods
    for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Nitrobenzene 98-95-3 0.068 and meet
    Section 728.148
    standards
    8
     
    14 and meet
    Section 728.148
    standards
    8
     
     
    D037
    9
     
    Wastes that are TC for Pentachlorophenol pentachlorophenol based on the toxicity characteristic
    leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test
    Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Pentachlorophenol 87-86-5 0.089 and meet
    Section 728.148
    standards
    8
     
    7.4 and meet
    Section 728.148
    standards
    8
     
     

     
    861
    D038
    9
     
    Wastes that are TC for Pyridine pyridine based on the toxicity characteristic leaching procedure
    Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Pyridine 110-86-1 0.014 and meet
    Section 728.148
    standards
    8
     
    16 and meet
    Section 728.148
    standards
    8
     
     
    D039
    9
     
    Wastes that are TC for Tetrachloroethylene tetrachloroethylene based on the toxicity
    characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure
    (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm.
    Code 720.111(a).
    Tetrachloroethylene 127-18-4 0.056 and meet
    Section 728.148
    standards
    8
     
    6.0 and meet
    Section 728.148
    standards
    8
     
     
    D040
    9
     
    Wastes that are TC for Trichloroethylene trichloroethylene based on the toxicity characteristic
    leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test
    Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Trichloroethylene 79-01-6 0.054 and meet
    Section 728.148
    standards
    8
     
    6.0 and meet
    Section 728.148
    standards
    8
     
     
    D041
    9
     
    Wastes that are TC for 2,4,5-Trichlorophenol 2,4,5-trichlorophenol based on the toxicity
    characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure
    (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm.
    Code 720.111(a).
    2,4,5-Trichlorophenol 95-95-4 0.18 and meet
    Section 728.148
    standards
    8
     
    7.4 and meet
    Section 728.148
    standards
    8
     
     

     
    862
    D042
    9
     
    Wastes that are TC for 2,4,6-Trichlorophenol 2,4,6-trichlorophenol based on the toxicity
    characteristic leaching procedure Method 1311 (Toxicity Characteristic Leaching Procedure
    (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA
    publication number EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm.
    Code 720.111(a).
    2,4,6-Trichlorophenol 88-06-2 0.035 and meet
    Section 728.148
    standards
    8
     
    7.4 and meet
    Section 728.148
    standards
    8
     
     
    D043
    9
     
    Wastes that are TC for Vinyl vinyl chloride based on the toxicity characteristic leaching
    procedure Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods
    for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number
    EPA530/SW-846 Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
    Vinyl chloride 75-01-4 0.27 and meet
    Section 728.148
    standards
    8
     
    6.0 and meet
    Section 728.148
    standards
    8
     
     
    F001, F002, F003, F004 & F005
    F001, F002, F003, F004, or F005 solvent wastes that contain any combination of one or more of
    the following spent solvents: acetone, benzene, n-butyl alcohol, carbon disulfide, carbon tetra-
    chloride, chlorinated fluorocarbons, chlorobenzene, o-cresol, m-cresol, p-cresol, cyclohexanone,
    o-dichlorobenzene, 2-ethoxyethanol, ethyl acetate, ethyl benzene, ethyl ether, isobutyl alcohol,
    methanol, methylene chloride, methyl ethyl ketone, methyl isobutyl ketone, nitrobenzene, 2-
    nitropropane, pyridine, tetrachloroethylene, toluene, 1,1,1-trichloroethane, 1,1,2-trichloroethane,
    1,1,2-trichloro-1,2,2-trifluoroethane, trichloroethylene, trichloromonofluoromethane, or xylenes
    (except as specifically noted in other subcategories). See further details of these listings in 35
    Ill. Adm. Code 721.131.
    Acetone 67-64-1 0.28 160
    Benzene 71-43-2 0.14 10
    n-Butyl alcohol 71-36-3 5.6 2.6
    Carbon disulfide 75-15-0 3.8 NA
    Carbon tetrachloride 56-23-5 0.057 6.0
    Chlorobenzene 108-90-7 0.057 6.0
    o-Cresol 95-48-7 0.11 5.6
    m-Cresol
    (difficult to distinguish from p-
    cresol)
    108-39-4 0.77 5.6
    p-Cresol
    (difficult to distinguish from m-
    cresol)
    106-44-5 0.77 5.6
    Cresol-mixed isomers (Cresylic
    acid)
    (sum of o-, m-, and p-cresol
    concentrations)
    1319-77-3 0.88 11.2

     
    863
    Cyclohexanone 108-94-1 0.36 NA
    o-Dichlorobenzene 95-50-1 0.088 6.0
    Ethyl acetate 141-78-6 0.34 33
    Ethyl benzene 100-41-4 0.057 10
    Ethyl ether 60-29-7 0.12 160
    Isobutyl alcohol 78-83-1 5.6 170
    Methanol 67-56-1 5.6 NA
    Methylene chloride 75-9-2 0.089 30
    Methyl ethyl ketone 78-93-3 0.28 36
    Methyl isobutyl ketone 108-10-1 0.14 33
    Nitrobenzene 98-95-3 0.068 14
    Pyridine 110-86-1 0.014 16
    Tetrachloroethylene 127-18-4 0.056 6.0
    Toluene 108-88-3 0.080 10
    1,1,1-Trichloroethane 71-55-6 0.054 6.0
    1,1,2-Trichloroethane 79-00-5 0.054 6.0
    1,1,2-Trichloro-1,2,2-trifluoro-
    ethane
    76-13-1 0.057 30
    Trichloroethylene 79-01-6 0.054 6.0
    Trichloromonofluoromethane 75-69-4 0.020 30
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30
     
    F001, F002, F003, F004 & F005
    F003 and F005 solvent wastes that contain any combination of one or more of the following
    three solvents as the only listed F001 through F005 solvents: carbon disulfide, cyclohexanone,
    or methanol. (Formerly Section 728.141(c)).
    Carbon disulfide 75-15-0 3.8 4.8 mg/lmg/
     
    TCLP
    Cyclohexanone 108-94-1 0.36 0.75 mg/lmg/
     
    TCLP
    Methanol 67-56-1 5.6 0.75 mg/lmg/
     
    TCLP
     
    F001, F002, F003, F004 & F005
    F005 solvent waste containing 2-Nitropropane as the only listed F001 through F005 solvent.
    2-Nitropropane 79-46-9 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    F001, F002, F003, F004 & F005
    F005 solvent waste containing 2-Ethoxyethanol as the only listed F001 through F005 solvent.
    2-Ethoxyethanol 110-80-5 BIODG; or
    CMBST
    CMBST

     
    864
     
    F006
    Wastewater treatment sludges from electroplating operations except from the following
    processes: (1) Sulfuric acid anodizing of aluminum; (2) tin plating on carbon steel; (3) zinc
    plating (segregated basis) on carbon steel; (4) aluminum or zinc-aluminum plating on carbon
    steel; (5) cleaning or stripping associated with tin, zinc, and aluminum plating on carbon steel;
    and (6) chemical etching and milling of aluminum.
    Cadmium 7440-43-9 0.69 0.11 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
    Silver 7440-22-4 NA 0.14 mg/lmg/
     
    TCLP
     
    F007
    Spent cyanide plating bath solutions from electroplating operations.
    Cadmium 7440-43-9 NA 0.11 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
    Silver 7440-22-4 NA 0.14 mg/lmg/
     
    TCLP
     
    F008
    Plating bath residues from the bottom of plating baths from electroplating operations where
    cyanides are used in the process.
    Cadmium 7440-43-9 NA 0.11 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP

     
    865
    Silver 7440-22-4 NA 0.14 mg/lmg/
     
    TCLP
     
    F009
    Spent stripping and cleaning bath solutions from electroplating operations where cyanides are
    used in the process.
    Cadmium 7440-43-9 NA 0.11 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
    Silver 7440-22-4 NA 0.14 mg/lmg/
     
    TCLP
     
    F010
    Quenching bath residues from oil baths from metal heat-treating operations where cyanides are
    used in the process.
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 NA
     
    F011
    Spent cyanide solutions from salt bath pot cleaning from metal heat-treating operations.
    Cadmium 7440-43-9 NA 0.11 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
    Silver 7440-22-4 NA 0.14 mg/lmg/
     
    TCLP
     
    F012
    Quenching wastewater treatment sludges from metal heat-treating operations where cyanides are
    used in the process.
    Cadmium 7440-43-9 NA 0.11 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590

     
    866
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
    Silver 7440-22-4 NA 0.14 mg/lmg/
     
    TCLP
     
    F019
    Wastewater treatment sludges from the chemical conversion coating of aluminum, except from
    zirconium phosphating in aluminum can washing when such phosphating is an exclusive
    conversion coating process.
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
     
    F020, F021, F022, F023, F026
    Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the
    production or manufacturing use (as a reactant, chemical intermediate, or component in a
    formulating process) of: (1) tri- or tetrachlorophenol, or of intermediates used to produce their
    pesticide derivatives, excluding wastes from the production of Hexachlorophene from highly
    purified 2,4,5-trichlorophenol (i.e., F020); (2) pentachlorophenol, or of intermediates used to
    produce its derivatives (i.e., F021); (3) tetra-, penta-, or hexachlorobenzenes under alkaline
    conditions (i.e., F022) and wastes (except wastewater and spent carbon from hydrogen chloride
    purification) from the production of materials on equipment previously used for the production
    or manufacturing use (as a reactant, chemical intermediate, or component in a formulating
    process) of: (1) tri- or tetrachlorophenols, excluding wastes from equipment used only for the
    production of Hexachlorophene from highly purified 2,4,5-trichlorophenol (F023) or (2) tetra-,
    penta-, or hexachlorobenzenes under alkaline conditions (i.e., F026).
    HxCDDs (All Hexachloro-
    dibenzo-p-dioxins)
    NA 0.000063 0.001
    HxCDFs (All Hexachloro-
    dibenzofurans)
    55684-94-1 0.000063 0.001
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    36088-22-9 0.000063 0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    30402-15-4 0.000035 0.001
    Pentachlorophenol 87-86-5 0.089 7.4
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    41903-57-5 0.000063 0.001
    TCDFs (All Tetrachloro-
    dibenzofurans)
    55722-27-5 0.000063 0.001
    2,4,5-Trichlorophenol 95-95-4 0.18 7.4
    2,4,6-Trichlorophenol 88-06-2 0.035 7.4
    2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4
     

     
    867
    F024
    Process wastes, including but not limited to, distillation residues, heavy ends, tars, and reactor
    clean-out wastes, from the production of certain chlorinated aliphatic hydrocarbons by free
    radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon
    chain lengths ranging from one to and including five, with varying amounts and positions of
    chlorine substitution. (This listing does not include wastewaters, wastewater treatment sludges,
    spent catalysts, and wastes listed in 35 Ill. Adm. Code 721.131 or 721.132.)
    All F024 wastes NA CMBST
    11
    CMBST
    11
     
    2-Chloro-1,3-butadiene 126-99-8 0.057 0.28
    3-Chloropropylene 107-05-1 0.036 30
    1,1-Dichloroethane 75-34-3 0.059 6.0
    1,2-Dichloroethane 107-06-2 0.21 6.0
    1,2-Dichloropropane 78-87-5 0.85 18
    cis-1,3-Dichloropropylene 10061-01-5 0.036 18
    trans-1,3-Dichloropropylene 10061-02-6 0.036 18
    bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28
    Hexachloroethane 67-72-1 0.055 30
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
     
    F025
    Condensed light ends from the production of certain chlorinated aliphatic hydrocarbons by free
    radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon
    chain lengths ranging from one up to and including five, with varying amounts and positions of
    chlorine substitution. F025--Light Ends Subcategory.
    Carbon tetrachloride 56-23-5 0.057 6.0
    Chloroform 67-66-3 0.046 6.0
    1,2-Dichloroethane 107-06-2 0.21 6.0
    1,1-Dichloroethylene 75-35-4 0.025 6.0
    Methylene chloride 75-9-2 0.089 30
    1,1,2-Trichloroethane 79-00-5 0.054 6.0
    Trichloroethylene 79-01-6 0.054 6.0
    Vinyl chloride 75-01-4 0.27 6.0
     
    F025
    Spent filters and filter aids, and spent desiccant wastes from the production of certain chlorinated
    aliphatic hydrocarbons by free radical catalyzed processes. These chlorinated aliphatic
    hydrocarbons are those having carbon chain lengths ranging from one to and including five, with
    varying amounts and positions of chlorine substitution. F025--Spent Filters/Aids and Desiccants
    Subcategory.
    Carbon tetrachloride 56-23-5 0.057 6.0
    Chloroform 67-66-3 0.046 6.0
    Hexachlorobenzene 118-74-1 0.055 10
    Hexachlorobutadiene 87-68-3 0.055 5.6
    Hexachloroethane 67-72-1 0.055 30

     
    868
    Methylene chloride 75-9-2 0.089 30
    1,1,2-Trichloroethane 79-00-5 0.054 6.0
    Trichloroethylene 79-01-6 0.054 6.0
    Vinyl chloride 75-01-4 0.27 6.0
     
    F027
    Discarded unused formulations containing tri-, tetra-, or pentachlorophenol or discarded unused
    formulations containing compounds derived from these chlorophenols. (This listing does not
    include formulations containing hexachlorophene synthesized from prepurified 2,4,5-trichloro-
    phenol as the sole component.)
    HxCDDs (All Hexachloro-
    dibenzo-p-dioxins)
    NA 0.000063 0.001
    HxCDFs (All Hexachloro-
    dibenzofurans)
    55684-94-1 0.000063 0.001
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    36088-22-9 0.000063 0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    30402-15-4 0.000035 0.001
    Pentachlorophenol 87-86-5 0.089 7.4
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    41903-57-5 0.000063 0.001
    TCDFs (All Tetrachloro-
    dibenzofurans)
    55722-27-5 0.000063 0.001
    2,4,5-Trichlorophenol 95-95-4 0.18 7.4
    2,4,6-Trichlorophenol 88-06-2 0.035 7.4
    2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4
     
    F028
    Residues resulting from the incineration or thermal treatment of soil contaminated with USEPA
    hazardous waste numbers F020, F021, F023, F026, and F027.
    HxCDDs (All Hexachloro-
    dibenzo-p-dioxins)
    NA 0.000063 0.001
    HxCDFs (All Hexachloro-
    dibenzofurans)
    55684-94-1 0.000063 0.001
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    36088-22-9 0.000063 0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    30402-15-4 0.000035 0.001
    Pentachlorophenol 87-86-5 0.089 7.4
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    41903-57-5 0.000063 0.001
    TCDFs (All Tetrachloro-
    dibenzofurans)
    55722-27-5 0.000063 0.001
    2,4,5-Trichlorophenol 95-95-4 0.18 7.4
    2,4,6-Trichlorophenol 88-06-2 0.035 7.4
    2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4

     
    869
     
    F032
    Wastewaters (except those that have not come into contact with process contaminants), process
    residuals, preservative drippage, and spent formulations from wood preserving processes
    generated at plants that currently use or have previously used chlorophenolic formulations
    (except potentially cross-contaminated wastes that have had the F032 waste code deleted in
    accordance with 35 Ill. Adm. Code 721.135 or potentially cross-contaminated wastes that are
    otherwise currently regulated as hazardous wastes (i.e., F034 or F035), where the generator does
    not resume or initiate use of chlorophenolic formulations). This listing does not include K001
    bottom sediment sludge from the treatment of wastewater from wood preserving processes that
    use creosote or penta-chlorophenol.
    Acenaphthene 83-32-9 0.059 3.4
    Anthracene 120-12-7 0.059 3.4
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzo(b)fluoranthene (difficult
    to distinguish from benzo(k)
    fluoranthene)
    205-99-2 0.11 6.8
    Benzo(k)fluoranthene (difficult
    to distinguish from benzo(b)
    fluoranthene)
    207-08-9 0.11 6.8
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Chrysene 218-01-9 0.059 3.4
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
    2-4-Dimethyl phenol 105-67-9 0.036 14
    Fluorene 86-73-7 0.059 3.4
    Hexachlorodibenzo-p-dioxins NA 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    Hexachlorodibenzofurans NA 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    Indeno (1,2,3-c,d) pyrene 193-39-5 0.0055 3.4
    Naphthalene 91-20-3 0.059 5.6
    Pentachlorodibenzo-p-dioxins NA 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    Pentachlorodibenzofurans NA 0.000035 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    Pentachlorophenol 87-86-5 0.089 7.4
    Phenanthrene 85-01-8 0.059 5.6
    Phenol 108-95-2 0.039 6.2
    Pyrene 129-00-0 0.067 8.2
    Tetrachlorodibenzo-p-dioxins NA 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    Tetrachlorodibenzofurans NA 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4
    2,4,6-Trichlorophenol 88-06-2 0.035 7.4

     
    870
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
     
    F034
    Wastewaters (except those that have not come into contact with process contaminants), process
    residuals, preservative drippage, and spent formulations from wood preserving processes
    generated at plants that use creosote formulations. This listing does not include K001 bottom
    sediment sludge from the treatment of wastewater from wood preserving processes that use
    creosote or pentachlorophenol.
    Acenaphthene 83-32-9 0.059 3.4
    Anthracene 120-12-7 0.059 3.4
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzo(b)fluoranthene (difficult
    to distinguish from
    benzo(k)fluoranthene)
    205-99-2 0.11 6.8
    Benzo(k)fluoranthene (difficult
    to distinguish from
    benzo(b)fluoranthene)
    207-08-9 0.11 6.8
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Chrysene 218-01-9 0.059 3.4
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
    Fluorene 86-73-7 0.059 3.4
    Indeno (1,2,3-c,d) pyrene 193-39-5 0.0055 3.4
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 85-01-8 0.059 5.6
    Pyrene 129-00-0 0.067 8.2
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
     
    F035
    Wastewaters (except those that have not come into contact with process contaminants), process
    residuals, preservative drippage, and spent formulations from wood preserving processes that are
    generated at plants that use inorganic preservatives containing arsenic or chromium. This listing
    does not include K001 bottom sediment sludge from the treatment of wastewater from wood
    preserving processes that use creosote or pentachlorophenol.
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
     
    F037
    Petroleum refinery primary oil/water/solids separation sludge--Any sludge generated from the

     
    871
    gravitational separation of oil/water/solids during the storage or treatment of process
    wastewaters and oily cooling wastewaters from petroleum refineries. Such sludges include, but
    are not limited to, those generated in: oil/water/solids separators; tanks, and impoundments;
    ditches, and other conveyances; sumps; and stormwater units receiving dry weather flow.
    Sludge generated in stormwater units that do not receive dry weather flow, sludges generated
    from non-contact once-through cooling waters segregated for treatment from other process or
    oily cooling waters, sludges generated in aggressive biological treatment units as defined in 35
    Ill. Adm. Code 721.131(b)(2) (including sludges generated in one or more additional units after
    wastewaters have been treated in aggressive biological treatment units) and K051 wastes are not
    included in this listing.
    Acenaphthene 83-32-9 0.059 NA
    Anthracene 120-12-7 0.059 3.4
    Benzene 71-43-2 0.14 10
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzo(a)pyrene 50-32-8 0.061 3.4
    bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28
    Chrysene 218-01-9 0.059 3.4
    Di-n-butyl phthalate 84-74-2 0.057 28
    Ethylbenzene 100-41-4 0.057 10
    Fluorene 86-73-7 0.059 NA
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 85-01-8 0.059 5.6
    Phenol 108-95-2 0.039 6.2
    Pyrene 129-00-0 0.067 8.2
    Toluene 108-88-3 0.080 10
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Lead 7439-92-1 0.69 NA
    Nickel 7440-02-0 NA 11 mg/lmg/
    TCLP
     
    F038
    Petroleum refinery secondary (emulsified) oil/water/solids separation sludge or float generated
    from the physical or chemical separation of oil/water/solids in process wastewaters and oily
    cooling wastewaters from petroleum refineries. Such wastes include, but are not limited to, all
    sludges and floats generated in: induced air floatation (IAF) units, tanks, and impoundments,
    and all sludges generated in DAF units. Sludges generated in stormwater units that do not
    receive dry weather flow, sludges generated from non-contact once-through cooling waters
    segregated for treatment from other process or oily cooling waters, sludges, and floats generated
    in aggressive biological treatment units as defined in 35 Ill. Adm. Code 721.131(b)(2) (including
    sludges and floats generated in one or more additional units after wastewaters have been treated
    in aggressive biological units) and F037, K048, and K051 are not included in this listing.
    Benzene 71-43-2 0.14 10

     
    872
    Benzo(a)pyrene 50-32-8 0.061 3.4
    bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28
    Chrysene 218-01-9 0.059 3.4
    Di-n-butyl phthalate 84-74-2 0.057 28
    Ethylbenzene 100-41-4 0.057 10
    Fluorene 86-73-7 0.059 NA
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 85-01-8 0.059 5.6
    Phenol 108-95-2 0.039 6.2
    Pyrene 129-00-0 0.067 8.2
    Toluene 108-88-3 0.080 10
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Lead 7439-92-1 0.69 NA
    Nickel 7440-02-0 NA 11 mg/lmg/
    TCLP
     
    F039
    Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal
    of more than one restricted waste classified as hazardous under Subpart D of this Part. (Leachate
    resulting from the disposal of one or more of the following USEPA hazardous wastes and no
    other hazardous wastes retains its USEPA hazardous waste numbers: F020, F021, F022, F026,
    F027, or F028.).
    Acenaphthylene 208-96-8 0.059 3.4
    Acenaphthene 83-32-9 0.059 3.4
    Acetone 67-64-1 0.28 160
    Acetonitrile 75-05-8 5.6 NA
    Acetophenone 96-86-2 0.010 9.7
    2-Acetylaminofluorene 53-96-3 0.059 140
    Acrolein 107-02-8 0.29 NA
    Acrylonitrile 107-13-1 0.24 84
    Aldrin 309-00-2 0.021 0.066
    4-Aminobiphenyl 92-67-1 0.13 NA
    Aniline 62-53-3 0.81 14
    o-Anisidine (2-methoxyaniline) 90-04-0 0.010 0.66
    Anthracene 120-12-7 0.059 3.4
    Aramite 140-57-8 0.36 NA
    α
    -BHC
    319-84-6 0.00014 0.066
    β
    -BHC
    319-85-7 0.00014 0.066
    δ
    -BHC
    319-86-8 0.023 0.066
    γ
    -BHC
    58-89-9 0.0017 0.066
    Benzene 71-43-2 0.14 10
    Benz(a)anthracene 56-55-3 0.059 3.4

     
    873
    Benzo(b)fluoranthene (difficult
    to distinguish from benzo(k)-
    fluoranthene)
    205-99-2 0.11 6.8
    Benzo(k)fluoranthene (difficult
    to distinguish from benzo(b)-
    fluoranthene)
    207-08-9 0.11 6.8
    Benzo(g,h,i)perylene 191-24-2 0.0055 1.8
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Bromodichloromethane 75-27-4 0.35 15
    Methyl bromide (Bromo-
    methane)
    74-83-9 0.11 15
    4-Bromophenyl phenyl ether 101-55-3 0.055 15
    n-Butyl alcohol 71-36-3 5.6 2.6
    Butyl benzyl phthalate 85-68-7 0.017 28
    2-sec-Butyl-4,6-dinitrophenol
    (Dinoseb)
    88-85-7 0.066 2.5
    Carbon disulfide 75-15-0 3.8 NA
    Carbon tetrachloride 56-23-5 0.057 6.0
    Chlordane (
    α
    and
    χ
    isomers)
    57-74-9 0.0033 0.26
    p-Chloroaniline 106-47-8 0.46 16
    Chlorobenzene 108-90-7 0.057 6.0
    Chlorobenzilate 510-15-6 0.10 NA
    2-Chloro-1,3-butadiene 126-99-8 0.057 NA
    Chlorodibromomethane 124-48-1 0.057 15
    Chloroethane 75-00-3 0.27 6.0
    bis(2-Chloroethoxy)methane 111-91-1 0.036 7.2
    bis(2-Chloroethyl)ether 111-44-4 0.033 6.0
    Chloroform 67-66-3 0.046 6.0
    bis(2-Chloroisopropyl)ether 39638-32-9 0.055 7.2
    p-Chloro-m-cresol 59-50-7 0.018 14
    Chloromethane (Methyl
    chloride)
    74-87-3 0.19 30
    2-Chloronaphthalene 91-58-7 0.055 5.6
    2-Chlorophenol 95-57-8 0.044 5.7
    3-Chloropropylene 107-05-1 0.036 30
    Chrysene 218-01-9 0.059 3.4
    p-Cresidine 120-71-8 0.010 0.66
    o-Cresol 95-48-7 0.11 5.6
    m-Cresol
    (difficult to distinguish from p-
    cresol)
    108-39-4 0.77 5.6
    p-Cresol
    (difficult to distinguish from m-
    cresol)
    106-44-5 0.77 5.6
    Cyclohexanone 108-94-1 0.36 NA
    1,2-Dibromo-3-chloropropane 96-12-8 0.11 15

     
    874
    Ethylene dibromide (1,2-
    Dibromoethane)
    106-93-4 0.028 15
    Dibromomethane 74-95-3 0.11 15
    2,4-D (2,4-Dichlorophenoxy-
    acetic acid)
    94-75-7 0.72 10
    o,p'-DDD 53-19-0 0.023 0.087
    p,p'-DDD 72-54-8 0.023 0.087
    o,p'-DDE 3424-82-6 0.031 0.087
    p,p'-DDE 72-55-9 0.031 0.087
    o,p'-DDT 789-02-6 0.0039 0.087
    p,p'-DDT 50-29-3 0.0039 0.087
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
    Dibenz(a,e)pyrene 192-65-4 0.061 NA
    m-Dichlorobenzene 541-73-1 0.036 6.0
    o-Dichlorobenzene 95-50-1 0.088 6.0
    p-Dichlorobenzene 106-46-7 0.090 6.0
    Dichlorodifluoromethane 75-71-8 0.23 7.2
    1,1-Dichloroethane 75-34-3 0.059 6.0
    1,2-Dichloroethane 107-06-2 0.21 6.0
    1,1-Dichloroethylene 75-35-4 0.025 6.0
    trans-1,2-Dichloroethylene 156-60-5 0.054 30
    2,4-Dichlorophenol 120-83-2 0.044 14
    2,6-Dichlorophenol 87-65-0 0.044 14
    1,2-Dichloropropane 78-87-5 0.85 18
    cis-1,3-Dichloropropylene 10061-01-5 0.036 18
    trans-1,3-Dichloropropylene 10061-02-6 0.036 18
    Dieldrin 60-57-1 0.017 0.13
    2,4-Dimethylaniline (2,4-
    xylidine)
    95-68-1 0.010 0.66
    Diethyl phthalate 84-66-2 0.20 28
    2-4-Dimethyl phenol 105-67-9 0.036 14
    Dimethyl phthalate 131-11-3 0.047 28
    Di-n-butyl phthalate 84-74-2 0.057 28
    1,4-Dinitrobenzene 100-25-4 0.32 2.3
    4,6-Dinitro-o-cresol 534-52-1 0.28 160
    2,4-Dinitrophenol 51-28-5 0.12 160
    2,4-Dinitrotoluene 121-14-2 0.32 140
    2,6-Dinitrotoluene 606-20-2 0.55 28
    Di-n-octyl phthalate 117-84-0 0.017 28
    Di-n-propylnitrosamine 621-64-7 0.40 14
    1,4-Dioxane 123-91-1 12.0 170
    Diphenylamine (difficult to
    distinguish from diphenylnitros-
    amine)
    122-39-4 0.92 NA

     
    875
    Diphenylnitrosamine (difficult
    to distinguish from diphenyl-
    amine)
    86-30-6 0.92 NA
    1,2-Diphenylhydrazine 122-66-7 0.087 NA
    Disulfoton 298-04-4 0.017 6.2
    Endosulfan I 939-98-8 0.023 0.066
    Endosulfan II 33213-6-5 0.029 0.13
    Endosulfan sulfate 1031-07-8 0.029 0.13
    Endrin 72-20-8 0.0028 0.13
    Endrin aldehyde 7421-93-4 0.025 0.13
    Ethyl acetate 141-78-6 0.34 33
    Ethyl cyanide (Propanenitrile) 107-12-0 0.24 360
    Ethyl benzene 100-41-4 0.057 10
    Ethyl ether 60-29-7 0.12 160
    bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28
    Ethyl methacrylate 97-63-2 0.14 160
    Ethylene oxide 75-21-8 0.12 NA
    Famphur 52-85-7 0.017 15
    Fluoranthene 206-44-0 0.068 3.4
    Fluorene 86-73-7 0.059 3.4
    Heptachlor 76-44-8 0.0012 0.066
    1,2,3,4,6,7,8-Heptachloro-
    dibenzo-p-dioxin (1,2,3,4,6,7,8-
    HpCDD)
    35822-46-9 0.000035 0.0025
    1,2,3,4,6,7,8-Heptachloro-
    dibenzofuran (1,2,3,4,6,7,8-
    HpCDF)
    67562-39-4 0.000035 0.0025
    1,2,3,4,7,8,9-Heptachloro-
    dibenzofuran (1,2,3,4,7,8,9-
    HpCDF)
    55673-89-7 0.000035 0.0025
    Heptachlor epoxide 1024-57-3 0.016 0.066
    Hexachlorobenzene 118-74-1 0.055 10
    Hexachlorobutadiene 87-68-3 0.055 5.6
    Hexachlorocyclopentadiene 77-47-4 0.057 2.4
    HxCDDs (All Hexachloro-
    dibenzo-p-dioxins)
    NA 0.000063 0.001
    HxCDFs (All Hexachloro-
    dibenzofurans)
    55684-94-1 0.000063 0.001
    Hexachloroethane 67-72-1 0.055 30
    Hexachloropropylene 1888-71-7 0.035 30
    Indeno (1,2,3-c,d) pyrene 193-39-5 0.0055 3.4
    Iodomethane 74-88-4 0.19 65
    Isobutyl alcohol 78-83-1 5.6 170
    Isodrin 465-73-6 0.021 0.066
    Isosafrole 120-58-1 0.081 2.6
    Kepone 143-50-8 0.0011 0.13

     
    876
    Methacrylonitrile 126-98-7 0.24 84
    Methanol 67-56-1 5.6 NA
    Methapyrilene 91-80-5 0.081 1.5
    Methoxychlor 72-43-5 0.25 0.18
    3-Methylcholanthrene 56-49-5 0.0055 15
    4,4-Methylene bis(2-chloro-
    aniline)
    101-14-4 0.50 30
    Methylene chloride 75-09-2 0.089 30
    Methyl ethyl ketone 78-93-3 0.28 36
    Methyl isobutyl ketone 108-10-1 0.14 33
    Methyl methacrylate 80-62-6 0.14 160
    Methyl methansulfonate 66-27-3 0.018 NA
    Methyl parathion 298-00-0 0.014 4.6
    Naphthalene 91-20-3 0.059 5.6
    2-Naphthylamine 91-59-8 0.52 NA
    p-Nitroaniline 100-01-6 0.028 28
    Nitrobenzene 98-95-3 0.068 14
    5-Nitro-o-toluidine 99-55-8 0.32 28
    p-Nitrophenol 100-02-7 0.12 29
    N-Nitrosodiethylamine 55-18-5 0.40 28
    N-Nitrosodimethylamine 62-75-9 0.40 NA
    N-Nitroso-di-n-butylamine 924-16-3 0.40 17
    N-Nitrosomethylethylamine 10595-95-6 0.40 2.3
    N-Nitrosomorpholine 59-89-2 0.40 2.3
    N-Nitrosopiperidine 100-75-4 0.013 35
    N-Nitrosopyrrolidine 930-55-2 0.013 35
    1,2,3,4,6,7,8,9-Octachloro-
    dibenzo-p-dioxin
    (1,2,3,4,6,7,8,9-OCDD)
    3268-87-9 0.000063 0.0025
    Parathion 56-38-2 0.014 4.6
    Total PCBs
    (sum of all PCB isomers, or all
    Aroclors)
    1336-36-3 0.10 10
    Pentachlorobenzene 608-93-5 0.055 10
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    36088-22-9 0.000063 0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    30402-15-4 0.000035 0.001
    Pentachloronitrobenzene 82-68-8 0.055 4.8
    Pentachlorophenol 87-86-5 0.089 7.4
    Phenacetin 62-44-2 0.081 16
    Phenanthrene 85-01-8 0.059 5.6
    Phenol 108-95-2 0.039 6.2
    1,3-Phenylenediamine 108-45-2 0.010 0.66
    Phorate 298-02-2 0.021 4.6
    Phthalic anhydride 85-44-9 0.055 NA

     
    877
    Pronamide 23950-58-5 0.093 1.5
    Pyrene 129-00-0 0.067 8.2
    Pyridine 110-86-1 0.014 16
    Safrole 94-59-7 0.081 22
    Silvex (2,4,5-TP) 93-72-1 0.72 7.9
    2,4,5-T 93-76-5 0.72 7.9
    1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    41903-57-5 0.000063 0.001
    TCDFs (All Tetrachloro-
    dibenzofurans)
    55722-27-5 0.000063 0.001
    1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0
    1,1,2,2-Tetrachloroethane 79-34-6 0.057 6.0
    Tetrachloroethylene 127-18-4 0.056 6.0
    2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4
    Toluene 108-88-3 0.080 10
    Toxaphene 8001-35-2 0.0095 2.6
    Bromoform (Tribromomethane) 75-25-2 0.63 15
    1,2,4-Trichlorobenzene 120-82-1 0.055 19
    1,1,1-Trichloroethane 71-55-6 0.054 6.0
    1,1,2-Trichloroethane 79-00-5 0.054 6.0
    Trichloroethylene 79-01-6 0.054 6.0
    Trichloromonofluoromethane 75-69-4 0.020 30
    2,4,5-Trichlorophenol 95-95-4 0.18 7.4
    2,4,6-Trichlorophenol 88-06-2 0.035 7.4
    1,2,3-Trichloropropane 96-18-4 0.85 30
    1,1,2-Trichloro-1,2,2-trifluoro-
    ethane
    76-13-1 0.057 30
    tris(2,3-Dibromopropyl)
    phosphate
    126-72-7 0.11 NA
    Vinyl chloride 75-01-4 0.27 6.0
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30
    Antimony 7440-36-0 1.9 1.15 mg/lmg/
     
    TCLP
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
    Barium 7440-39-3 1.2 21 mg/lmg/
    TCLP
    Beryllium 7440-41-7 0.82 NA
    Cadmium 7440-43-9 0.69 0.11 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 NA

     
    878
    Fluoride 16964-48-8 35 NA
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Mercury 7439-97-6 0.15 0.025 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
    Selenium 7782-49-2 0.82 5.7 mg/lmg/
     
    TCLP
    Silver 7440-22-4 0.43 0.14 mg/lmg/
     
    TCLP
    Sulfide 8496-25-8 14 NA
    Thallium 7440-28-0 1.4 NA
    Vanadium 7440-62-2 4.3 NA
     
    K001
    Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that
    use creosote or pentachlorophenol.
    Naphthalene 91-20-3 0.059 5.6
    Pentachlorophenol 87-86-5 0.089 7.4
    Phenanthrene 85-01-8 0.059 5.6
    Pyrene 129-00-0 0.067 8.2
    Toluene 108-88-3 0.080 10
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    K002
    Wastewater treatment sludge from the production of chrome yellow and orange pigments.
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    K003
    Wastewater treatment sludge from the production of molybdate orange pigments.
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    K004
    Wastewater treatment sludge from the production of zinc yellow pigments.
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP

     
    879
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    K005
    Wastewater treatment sludge from the production of chrome green pigments.
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
     
    K006
    Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous).
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    K006
    Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated).
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 NA
     
    K007
    Wastewater treatment sludge from the production of iron blue pigments.
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
     
    K008
    Oven residue from the production of chrome oxide green pigments.
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    K009
    Distillation bottoms from the production of acetaldehyde from ethylene.
    Chloroform 67-66-3 0.046 6.0
     
    K010
    Distillation side cuts from the production of acetaldehyde from ethylene.
    Chloroform 67-66-3 0.046 6.0

     
    880
     
    K011
    Bottom stream from the wastewater stripper in the production of acrylonitrile.
    Acetonitrile 75-05-8 5.6 38
    Acrylonitrile 107-13-1 0.24 84
    Acrylamide 79-06-1 19 23
    Benzene 71-43-2 0.14 10
    Cyanide (Total) 57-12-5 1.2 590
     
    K013
    Bottom stream from the acetonitrile column in the production of acrylonitrile.
    Acetonitrile 75-05-8 5.6 38
    Acrylonitrile 107-13-1 0.24 84
    Acrylamide 79-06-1 19 23
    Benzene 71-43-2 0.14 10
    Cyanide (Total) 57-12-5 1.2 590
     
    K014
    Bottoms from the acetonitrile purification column in the production of acrylonitrile.
    Acetonitrile 75-05-8 5.6 38
    Acrylonitrile 107-13-1 0.24 84
    Acrylamide 79-06-1 19 23
    Benzene 71-43-2 0.14 10
    Cyanide (Total) 57-12-5 1.2 590
     
    K015
    Still bottoms from the distillation of benzyl chloride.
    Anthracene 120-12-7 0.059 3.4
    Benzal chloride 98-87-3 0.055 6.0
    Benzo(b)fluoranthene (difficult
    to distinguish from benzo(k)-
    fluoranthene)
    205-99-2 0.11 6.8
    Benzo(k)fluoranthene (difficult
    to distinguish from benzo(b)-
    fluoranthene)
    207-08-9 0.11 6.8
    Phenanthrene 85-01-8 0.059 5.6
    Toluene 108-88-3 0.080 10
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
     
    K016
    Heavy ends or distillation residues from the production of carbon tetrachloride.
    Hexachlorobenzene 118-74-1 0.055 10
    Hexachlorobutadiene 87-68-3 0.055 5.6
    Hexachlorocyclopentadiene 77-47-4 0.057 2.4

     
    881
    Hexachloroethane 67-72-1 0.055 30
    Tetrachloroethylene 127-18-4 0.056 6.0
     
    K017
    Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.
    bis(2-Chloroethyl)ether 111-44-4 0.033 6.0
    1,2-Dichloropropane 78-87-5 0.85 18
    1,2,3-Trichloropropane 96-18-4 0.85 30
     
    K018
    Heavy ends from the fractionation column in ethyl chloride production.
    Chloroethane 75-00-3 0.27 6.0
    Chloromethane 74-87-3 0.19 NA
    1,1-Dichloroethane 75-34-3 0.059 6.0
    1,2-Dichloroethane 107-06-2 0.21 6.0
    Hexachlorobenzene 118-74-1 0.055 10
    Hexachlorobutadiene 87-68-3 0.055 5.6
    Hexachloroethane 67-72-1 0.055 30
    Pentachloroethane 76-01-7 NA 6.0
    1,1,1-Trichloroethane 71-55-6 0.054 6.0
     
    K019
    Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production.
    bis(2-Chloroethyl)ether 111-44-4 0.033 6.0
    Chlorobenzene 108-90-7 0.057 6.0
    Chloroform 67-66-3 0.046 6.0
    p-Dichlorobenzene 106-46-7 0.090 NA
    1,2-Dichloroethane 107-06-2 0.21 6.0
    Fluorene 86-73-7 0.059 NA
    Hexachloroethane 67-72-1 0.055 30
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 85-01-8 0.059 5.6
    1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 NA
    Tetrachloroethylene 127-18-4 0.056 6.0
    1,2,4-Trichlorobenzene 120-82-1 0.055 19
    1,1,1-Trichloroethane 71-55-6 0.054 6.0
     
    K020
    Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.
    1,2-Dichloroethane 107-06-2 0.21 6.0
    1,1,2,2-Tetrachloroethane 79-34-6 0.057 6.0
    Tetrachloroethylene 127-18-4 0.056 6.0
     
    K021
    Aqueous spent antimony catalyst waste from fluoromethanes production.
    Carbon tetrachloride 56-23-5 0.057 6.0

     
    882
    Chloroform 67-66-3 0.046 6.0
    Antimony 7440-36-0 1.9 1.15 mg/lmg/
     
    TCLP
     
    K022
    Distillation bottom tars from the production of phenol or acetone from cumene.
    Toluene 108-88-3 0.080 10
    Acetophenone 96-86-2 0.010 9.7
    Diphenylamine (difficult to
    distinguish from diphenylnitros-
    amine)
    122-39-4 0.92 13
    Diphenylnitrosamine (difficult
    to distinguish from diphenyl-
    amine)
    86-30-6 0.92 13
    Phenol 108-95-2 0.039 6.2
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
     
    K023
    Distillation light ends from the production of phthalic anhydride from naphthalene.
    Phthalic anhydride (measured as
    Phthalic acid or Terephthalic
    acid)
    100-21-0 0.055 28
    Phthalic anhydride (measured as
    Phthalic acid or Terephthalic
    acid)
    85-44-9 0.055 28
     
    K024
    Distillation bottoms from the production of phthalic anhydride from naphthalene.
    Phthalic anhydride (measured as
    Phthalic acid or Terephthalic
    acid)
    100-21-0 0.055 28
    Phthalic anhydride (measured as
    Phthalic acid or Terephthalic
    acid)
    85-44-9 0.055 28
     
    K025
    Distillation bottoms from the production of nitrobenzene by the nitration of benzene.
    NA NA LLEXT fb SSTRP
    fb CARBN; or
    CMBST
    CMBST
     
    K026
    Stripping still tails from the production of methyl ethyl pyridines.
    NA NA CMBST CMBST

     
    883
     
    K027
    Centrifuge and distillation residues from toluene diisocyanate production.
    NA NA CARBN; or
    CMBST
    CMBST
     
    K028
    Spent catalyst from the hydrochlorinator reactor in the production of 1,1,1-trichloroethane.
    1,1-Dichloroethane 75-34-3 0.059 6.0
    trans-1,2-Dichloroethylene 156-60-5 0.054 30
    Hexachlorobutadiene 87-68-3 0.055 5.6
    Hexachloroethane 67-72-1 0.055 30
    Pentachloroethane 76-01-7 NA 6.0
    1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0
    1,1,2,2-Tetrachloroethane 79-34-6 0.057 6.0
    Tetrachloroethylene 127-18-4 0.056 6.0
    1,1,1-Trichloroethane 71-55-6 0.054 6.0
    1,1,2-Trichloroethane 79-00-5 0.054 6.0
    Cadmium 7440-43-9 0.69 NA
    Chromium(Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
     
    K029
    Waste from the product steam stripper in the production of 1,1,1-trichloroethane.
    Chloroform 67-66-3 0.046 6.0
    1,2-Dichloroethane 107-06-2 0.21 6.0
    1,1-Dichloroethylene 75-35-4 0.025 6.0
    1,1,1-Trichloroethane 71-55-6 0.054 6.0
    Vinyl chloride 75-01-4 0.27 6.0
     
    K030
    Column bodies or heavy ends from the combined production of trichloroethylene and perchloro-
    ethylene.
    o-Dichlorobenzene 95-50-1 0.088 NA
    p-Dichlorobenzene 106-46-7 0.090 NA
    Hexachlorobutadiene 87-68-3 0.055 5.6
    Hexachloroethane 67-72-1 0.055 30
    Hexachloropropylene 1888-71-7 NA 30
    Pentachlorobenzene 608-93-5 NA 10
    Pentachloroethane 76-01-7 NA 6.0
    1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14
    Tetrachloroethylene 127-18-4 0.056 6.0
    1,2,4-Trichlorobenzene 120-82-1 0.055 19

     
    884
     
    K031
    By-product salts generated in the production of MSMA and cacodylic acid.
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
     
    K032
    Wastewater treatment sludge from the production of chlordane.
    Hexachlorocyclopentadiene 77-47-4 0.057 2.4
    Chlordane (
    α
    and
    γ
    isomers)
    57-74-9 0.0033 0.26
    Heptachlor 76-44-8 0.0012 0.066
    Heptachlor epoxide 1024-57-3 0.016 0.066
     
    K033
    Wastewater and scrub water from the chlorination of cyclopentadiene in the production of
    chlordane.
    Hexachlorocyclopentadiene 77-47-4 0.057 2.4
     
    K034
    Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.
    Hexachlorocyclopentadiene 77-47-4 0.057 2.4
     
    K035
    Wastewater treatment sludges generated in the production of creosote.
    Acenaphthene 83-32-9 NA 3.4
    Anthracene 120-12-7 NA 3.4
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Chrysene 218-01-9 0.059 3.4
    o-Cresol 95-48-7 0.11 5.6
    m-Cresol
    (difficult to distinguish from p-
    cresol)
    108-39-4 0.77 5.6
    p-Cresol
    (difficult to distinguish from m-
    cresol)
    106-44-5 0.77 5.6
    Dibenz(a,h)anthracene 53-70-3 NA 8.2
    Fluoranthene 206-44-0 0.068 3.4
    Fluorene 86-73-7 NA 3.4
    Indeno(1,2,3-cd)pyrene 193-39-5 NA 3.4
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 85-01-8 0.059 5.6
    Phenol 108-95-2 0.039 6.2
    Pyrene 129-00-0 0.067 8.2
     

     
    885
    K036
    Still bottoms from toluene reclamation distillaiton in the production of disulfoton.
    Disulfoton 298-04-4 0.017 6.2
     
    K037
    Wastewater treatment sludges from the production of disulfoton.
    Disulfoton 298-04-4 0.017 6.2
    Toluene 108-88-3 0.080 10
     
    K038
    Wastewater from the washing and stripping of phorate production.
    Phorate 298-02-2 0.021 4.6
     
    K039
    Filter cake from the filtration of diethylphosphorodithioic acid in the production of phorate.
    NA NA CARBN; or
    CMBST
    CMBST
     
    K040
    Wastewater treatment sludge from the production of phorate.
    Phorate 298-02-2 0.021 4.6
     
    K041
    Wastewater treatment sludge from the production of toxaphene.
    Toxaphene 8001-35-2 0.0095 2.6
     
    K042
    Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production
    of 2,4,5-T.
    o-Dichlorobenzene 95-50-1 0.088 6.0
    p-Dichlorobenzene 106-46-7 0.090 6.0
    Pentachlorobenzene 608-93-5 0.055 10
    1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14
    1,2,4-Trichlorobenzene 120-82-1 0.055 19
     
    K043
    2,6-Dichlorophenol waste from the production of 2,4-D.
    2,4-Dichlorophenol 120-83-2 0.044 14
    2,6-Dichlorophenol 187-65-0 0.044 14
    2,4,5-Trichlorophenol 95-95-4 0.18 7.4
    2,4,6-Trichlorophenol 88-06-2 0.035 7.4
    2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4
    Pentachlorophenol 87-86-5 0.089 7.4
    Tetrachloroethylene 127-18-4 0.056 6.0
    HxCDDs (All Hexachloro-
    dibenzo-p-dioxins)
    NA 0.000063 0.001

     
    886
    HxCDFs (All Hexachloro-
    dibenzofurans)
    55684-94-1 0.000063 0.001
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    36088-22-9 0.000063 0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    30402-15-4 0.000035 0.001
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    41903-57-5 0.000063 0.001
    TCDFs (All Tetrachloro-
    dibenzofurans)
    55722-27-5 0.000063 0.001
     
    K044
    Wastewater treatment sludges from the manufacturing and processing of explosives.
    NA NA DEACT DEACT
     
    K045
    Spent carbon from the treatment of wastewater containing explosives.
    NA NA DEACT DEACT
     
    K046
    Wastewater treatment sludges from the manufacturing, formulation and loading of lead-based
    initiating compounds.
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    K047
    Pink or red water from TNT operations.
    NA NA DEACT DEACT
     
    K048
    Dissolved air flotation (DAF) float from the petroleum refining industry.
    Benzene 71-43-2 0.14 10
    Benzo(a)pyrene 50-32-8 0.061 3.4
    bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28
    Chrysene 218-01-9 0.059 3.4
    Di-n-butyl phthalate 84-74-2 0.057 28
    Ethylbenzene 100-41-4 0.057 10
    Fluorene 86-73-7 0.059 NA
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 85-01-8 0.059 5.6
    Phenol 108-95-2 0.039 6.2
    Pyrene 129-00-0 0.067 8.2
    Toluene 108-88-33 0.080 10
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30

     
    887
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Lead 7439-92-1 0.69 NA
    Nickel 7440-02-0 NA 11 mg/lmg/
    TCLP
     
    K049
    Slop oil emulsion solids from the petroleum refining industry.
    Anthracene 120-12-7 0.059 3.4
    Benzene 71-43-2 0.14 10
    Benzo(a)pyrene 50-32-8 0.061 3.4
    bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28
    Carbon disulfide 75-15-0 3.8 NA
    Chrysene 2218-01-9 0.059 3.4
    2,4-Dimethylphenol 105-67-9 0.036 NA
    Ethylbenzene 100-41-4 0.057 10
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 85-01-8 0.059 5.6
    Phenol 108-95-2 0.039 6.2
    Pyrene 129-00-0 0.067 8.2
    Toluene 108-88-3 0.080 10
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 NA
    Nickel 7440-02-0 NA 11 mg/lmg/
    TCLP
     
    K050
    Heat exchanger bundle cleaning sludge from the petroleum refining industry.
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Phenol 108-95-2 0.039 6.2
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 NA
    Nickel 7440-02-0 NA 11 mg/lmg/
    TCLP
     
    K051
    API separator sludge from the petroleum refining industry.
    Acenaphthene 83-32-9 0.059 NA
    Anthracene 120-12-7 0.059 3.4
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzene 71-43-2 0.14 10

     
    888
    Benzo(a)pyrene 50-32-8 0.061 3.4
    bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28
    Chrysene 2218-01-9 0.059 3.4
    Di-n-butyl phthalate 105-67-9 0.057 28
    Ethylbenzene 100-41-4 0.057 10
    Fluorene 86-73-7 0.059 NA
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 85-01-8 0.059 5.6
    Phenol 108-95-2 0.039 6.2
    Pyrene 129-00-0 0.067 8.2
    Toluene 108-88-3 0.08 10
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 NA
    Nickel 7440-02-0 NA 11 mg/lmg/
    TCLP
     
    K052
    Tank bottoms (leaded) from the petroleum refining industry.
    Benzene 71-43-2 0.14 10
    Benzo(a)pyrene 50-32-8 0.061 3.4
    o-Cresol 95-48-7 0.11 5.6
    m-Cresol
    (difficult to distinguish from p-
    cresol)
    108-39-4 0.77 5.6
    p-Cresol
    (difficult to distinguish from m-
    cresol)
    106-44-5 0.77 5.6
    2,4-Dimethylphenol 105-67-9 0.036 NA
    Ethylbenzene 100-41-4 0.057 10
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 85-01-8 0.059 5.6
    Phenol 108-95-2 0.039 6.2
    Toluene 108-88-3 0.08 10
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Lead 7439-92-1 0.69 NA
    Nickel 7440-02-0 NA 11 mg/lmg/
    TCLP
     

     
    889
    K060
    Ammonia still lime sludge from coking operations.
    Benzene 71-43-2 0.14 10
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Naphthalene 91-20-3 0.059 5.6
    Phenol 108-95-2 0.039 6.2
    Cyanides (Total)
    7
    57-12-5 1.2 590
     
    K061
    Emission control dust or sludge from the primary production of steel in electric furnaces.
    Antimony 7440-36-0 NA 1.15 mg/lmg/
     
    TCLP
    Arsenic 7440-38-2 NA 5.0 mg/lmg/
     
    TCLP
    Barium 7440-39-3 NA 21 mg/lmg/
    TCLP
    Beryllium 7440-41-7 NA 1.22 mg/lmg/
     
    TCLP
    Cadmium 7440-43-9 0.69 0.11 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Mercury 7439-97-6 NA 0.025 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
    Selenium 7782-49-2 NA 5.7 mg/lmg/
     
    TCLP
    Silver 7440-22-4 NA 0.14 mg/lmg/
     
    TCLP
    Thallium 7440-28-0 NA 0.20 mg/lmg/
     
    TCLP
    Zinc 7440-66-6 NA 4.3 mg/lmg/
     
    TCLP
     
    K062
    Spent pickle liquor generated by steel finishing operations of facilities within the iron and steel
    industry (SIC Codes 331 and 332).
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 NA
     
    K069
    Emission control dust or sludge from secondary lead smelting - Calcium sulfate (Low Lead)

     
    890
    Subcategory.
    Cadmium 7440-43-9 0.69 0.11 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    K069
    Emission control dust or sludge from secondary lead smelting - Non-Calcium sulfate (High
    Lead) Subcategory.
    NA NA NA RLEAD
     
    K071
    K071 (Brine purification muds from the mercury cell process in chlorine production, where
    separately prepurified brine is not used) nonwastewaters that are residues from RMERC.
    Mercury 7439-97-6 NA 0.20 mg/lmg/
     
    TCLP
     
    K071
    K071 (Brine purification muds from the mercury cell process in chlorine production, where
    separately prepurified brine is not used) nonwastewaters that are not residues from RMERC.
    Mercury 7439-97-6 NA 0.025 mg/lmg/
     
    TCLP
     
    K071
    All K071 wastewaters.
    Mercury 7439-97-6 0.15 NA
     
    K073
    Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using
    graphite anodes in chlorine production.
    Carbon tetrachloride 56-23-5 0.057 6.0
    Chloroform 67-66-3 0.046 6.0
    Hexachloroethane 67-72-1 0.055 30
    Tetrachloroethylene 127-18-4 0.056 6.0
    1,1,1-Trichloroethane 71-55-6 0.054 6.0
     
    K083
    Distillation bottoms from aniline production.
    Aniline 62-53-3 0.81 14
    Benzene 71-43-2 0.14 10
    Cyclohexanone 108-94-1 0.36 NA
    Diphenylamine
    (difficult to distinguish from
    diphenylnitrosamine)
    122-39-4 0.92 13

     
    891
    Diphenylnitrosamine (difficult
    to distinguish from diphenyl-
    amine)
    86-30-6 0.92 13
    Nitrobenzene 98-95-3 0.068 14
    Phenol 108-95-2 0.039 6.2
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
     
    K084
    Wastewater treatment sludges generated during the production of veterinary pharmaceuticals
    from arsenic or organo-arsenic compounds.
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
     
    K085
    Distillation or fractionation column bottoms from the production of chlorobenzenes.
    Benzene 71-43-2 0.14 10
    Chlorobenzene 108-90-7 0.057 6.0
    m-Dichlorobenzene 541-73-1 0.036 6.0
    o-Dichlorobenzene 95-50-1 0.088 6.0
    p-Dichlorobenzene 106-46-7 0.090 6.0
    Hexachlorobenzene 118-74-1 0.055 10
    Total PCBs
    (sum of all PCB isomers, or all
    Aroclors)
    1336-36-3 0.10 10
    Pentachlorobenzene 608-93-5 0.055 10
    1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14
    1,2,4-Trichlorobenzene 120-82-1 0.055 19
     
    K086
    Solvent wastes and sludges, caustic washes and sludges, or water washes and sludges from
    cleaning tubs and equipment used in the formulation of ink from pigments, driers, soaps, and
    stabilizers containing chromium and lead.
    Acetone 67-64-1 0.28 160
    Acetophenone 96-86-2 0.010 9.7
    bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28
    n-Butyl alcohol 71-36-3 5.6 2.6
    Butylbenzyl phthalate 85-68-7 0.017 28
    Cyclohexanone 108-94-1 0.36 NA
    o-Dichlorobenzene 95-50-1 0.088 6.0
    Diethyl phthalate 84-66-2 0.20 28
    Dimethyl phthalate 131-11-3 0.047 28
    Di-n-butyl phthalate 84-74-2 0.057 28
    Di-n-octyl phthalate 117-84-0 0.017 28
    Ethyl acetate 141-78-6 0.34 33
    Ethylbenzene 100-41-4 0.057 10
    Methanol 67-56-1 5.6 NA

     
    892
    Methyl ethyl ketone 78-93-3 0.28 36
    Methyl isobutyl ketone 108-10-1 0.14 33
    Methylene chloride 75-09-2 0.089 30
    Naphthalene 91-20-3 0.059 5.6
    Nitrobenzene 98-95-3 0.068 14
    Toluene 108-88-3 0.080 10
    1,1,1-Trichloroethane 71-55-6 0.054 6.0
    Trichloroethylene 79-01-6 0.054 6.0
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    K087
    Decanter tank tar sludge from coking operations.
    Acenaphthylene 208-96-8 0.059 3.4
    Benzene 71-43-2 0.14 10
    Chrysene 218-01-9 0.059 3.4
    Fluoranthene 206-44-0 0.068 3.4
    Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 85-01-8 0.059 5.6
    Toluene 108-88-3 0.080 10
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    K088
    Spent potliners from primary aluminum reduction.
    Acenaphthene 83-32-9 0.059 3.4
    Anthracene 120-12-7 0.059 3.4
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Benzo(b)fluoranthene 205-99-2 0.11 6.8
    Benzo(k)fluoranthene 207-08-9 0.11 6.8
    Benzo(g,h,i)perylene 191-24-2 0.0055 1.8
    Chrysene 218-01-9 0.059 3.4
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
    Fluoranthene 206-44-0 0.068 3.4
    Indeno(1,2,3-c,d)pyrene 193-39-5 0.0055 3.4

     
    893
    Phenanthrene 85-01-8 0.059 5.6
    Pyrene 129-00-0 0.067 8.2
    Antimony 7440-36-0 1.9 1.15 mg/lmg/
     
    TCLP
    Arsenic 7440-38-2 1.4 26.1 mg/lmg/
     
    Barium 7440-39-3 1.2 21 mg/lmg/
    TCLP
    Beryllium 7440-41-7 0.82 1.22 mg/lmg/
     
    TCLP
    Cadmium 7440-43-9 0.69 0.11 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Mercury 7439-97-6 0.15 0.025 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
    Selenium 7782-49-2 0.82 5.7 mg/lmg/
     
    TCLP
    Silver 7440-22-4 0.43 0.14 mg/lmg/
     
    TCLP
    Cyanide (Total)
    7
    57-12-5 1.2 590
    Cyanide (Amenable)
    7
    57-12-5 0.86 30
    Fluoride 16984-48-8 35 NA
     
    K093
    Distillation light ends from the production of phthalic anhydride from ortho-xylene.
    Phthalic anhydride (measured as
    Phthalic acid or Terephthalic
    acid)
    100-21-0 0.055 28
    Phthalic anhydride (measured as
    Phthalic acid or Terephthalic
    acid)
    85-44-9 0.055 28
     
    K094
    Distillation bottoms from the production of phthalic anhydride from ortho-xylene.
    Phthalic anhydride (measured as
    Phthalic acid or Terephthalic
    acid)
    100-21-0 0.055 28
    Phthalic anhydride (measured as
    Phthalic acid or Terephthalic
    acid)
    85-44-9 0.055 28
     
    K095
    Distillation bottoms from the production of 1,1,1-trichloroethane.
    Hexachloroethane 67-72-1 0.055 30

     
    894
    Pentachloroethane 76-01-7 0.055 6.0
    1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0
    1,1,2,2-Tetrachloroethane 79-34-6 0.057 6.0
    Tetrachloroethylene 127-18-4 0.056 6.0
    1,1,2-Trichloroethane 79-00-5 0.054 6.0
    Trichloroethylene 79-01-6 0.054 6.0
     
    K096
    Heavy ends from the heavy ends column from the production of 1,1,1-trichloroethane.
    m-Dichlorobenzene 541-73-1 0.036 6.0
    Pentachloroethane 76-01-7 0.055 6.0
    1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0
    1,1,2,2-Tetrachloroethane 79-34-6 0.057 6.0
    Tetrachloroethylene 127-18-4 0.056 6.0
    1,2,4-Trichlorobenzene 120-82-1 0.055 19
    1,1,2-Trichloroethane 79-00-5 0.054 6.0
    Trichloroethylene 79-01-6 0.054 6.0
     
    K097
    Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.
    Chlordane (
    α
    and
    χ
    isomers)
    57-74-9 0.0033 0.26
    Heptachlor 76-44-8 0.0012 0.066
    Heptachlor epoxide 1024-57-3 0.016 0.066
    Hexachlorocyclopentadiene 77-47-4 0.057 2.4
     
    K098
    Untreated process wastewater from the production of toxaphene.
    Toxaphene 8001-35-2 0.0095 2.6
     
    K099
    Untreated wastewater from the production of 2,4-D.
    2,4-Dichlorophenoxyacetic acid 94-75-7 0.72 10
    HxCDDs (All Hexachloro-
    dibenzo-p-dioxins)
    NA 0.000063 0.001
    HxCDFs (All Hexachloro-
    dibenzofurans)
    55684-94-1 0.000063 0.001
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    36088-22-9 0.000063 0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    30402-15-4 0.000035 0.001
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    41903-57-5 0.000063 0.001
    TCDFs (All Tetrachloro-
    dibenzofurans)
    55722-27-5 0.000063 0.001
     

     
    895
    K100
    Waste leaching solution from acid leaching of emission control dust or sludge from secondary
    lead smelting.
    Cadmium 7440-43-9 0.69 0.11 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    K101
    Distillation tar residues from the distillation of aniline-based compounds in the production of
    veterinary pharmaceuticals from arsenic or organo-arsenic compounds.
    o-Nitroaniline 88-74-4 0.27 14
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
    Cadmium 7440-43-9 0.69 NA
    Lead 7439-92-1 0.69 NA
    Mercury 7439-97-6 0.15 NA
     
    K102
    Residue from the use of activated carbon for decolorization in the production of veterinary
    pharmaceuticals from arsenic or organo-arsenic compounds.
    o-Nitrophenol 88-75-5 0.028 13
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
    Cadmium 7440-43-9 0.69 NA
    Lead 7439-92-1 0.69 NA
    Mercury 7439-97-6 0.15 NA
     
    K103
    Process residues from aniline extraction from the production of aniline.
    Aniline 62-53-3 0.81 14
    Benzene 71-43-2 0.14 10
    2,4-Dinitrophenol 51-28-5 0.12 160
    Nitrobenzene 98-95-3 0.068 14
    Phenol 108-95-2 0.039 6.2
     
    K104
    Combined wastewater streams generated from nitrobenzene or aniline production.
    Aniline 62-53-3 0.81 14
    Benzene 71-43-2 0.14 10
    2,4-Dinitrophenol 51-28-5 0.12 160
    Nitrobenzene 98-95-3 0.068 14
    Phenol 108-95-2 0.039 6.2
    Cyanides (Total)
    7
    57-12-5 1.2 590

     
    896
     
    K105
    Separated aqueous stream from the reactor product washing step in the production of chloro-
    benzenes.
    Benzene 71-43-2 0.14 10
    Chlorobenzene 108-90-7 0.057 6.0
    2-Chlorophenol 95-57-8 0.044 5.7
    o-Dichlorobenzene 95-50-1 0.088 6.0
    p-Dichlorobenzene 106-46-7 0.090 6.0
    Phenol 108-95-2 0.039 6.2
    2,4,5-Trichlorophenol 95-95-4 0.18 7.4
    2,4,6-Trichlorophenol 88-06-2 0.035 7.4
     
    K106
    K106 (wastewater treatment sludge from the mercury cell process in chlorine production)
    nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.
    Mercury 7439-97-6 NA RMERC
     
    K106
    K106 (wastewater treatment sludge from the mercury cell process in chlorine production)
    nonwastewaters that contain less than 260 mg/kg total mercury that are residues from RMERC.
    Mercury 7439-97-6 NA 0.20 mg/lmg/
     
    TCLP
     
    K106
    Other K106 nonwastewaters that contain less than 260 mg/kg total mercury and are not residues
    from RMERC.
    Mercury 7439-97-6 NA 0.025 mg/lmg/
     
    TCLP
     
    K106
    All K106 wastewaters.
    Mercury 7439-97-6 0.15 NA
     
    K107
    Column bottoms from product separation from the production of 1,1-dimethylhydrazine
    (UDMH) from carboxylic acid hydrazides.
    NA NA CMBST; or
    CHOXD fb
    CARBN; or
    BIODG fb
    CARBN
    CMBST
     

     
    897
    K108
    Condensed column overheads from product separation and condensed reactor vent gases from
    the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
    NA NA CMBST; or
    CHOXD fb
    CARBN; or
    BIODG fb
    CARBN
    CMBST
     
    K109
    Spent filter cartridges from product purification from the production of 1,1-dimethylhydrazine
    (UDMH) from carboxylic acid hydrazides.
    NA NA CMBST; or
    CHOXD fb
    CARBN; or
    BIODG fb
    CARBN
    CMBST
     
    K110
    Condensed column overheads from intermediate separation from the production of 1,1-dimethyl-
    hydrazine (UDMH) from carboxylic acid hydrazides.
    NA NA CMBST; or
    CHOXD fb
    CARBN; or
    BIODG fb
    CARBN
    CMBST
     
    K111
    Product washwaters from the production of dinitrotoluene via nitration of toluene.
    2,4-Dinitrotoluene 121-1-1 0.32 140
    2,6-Dinitrotoluene 606-20-2 0.55 28
     
    K112
    Reaction by-product water from the drying column in the production of toluenediamine via
    hydrogenation of dinitrotoluene.
    NA NA CMBST; or
    CHOXD fb
    CARBN; or
    BIODG fb
    CARBN
    CMBST
     
    K113
    Condensed liquid light ends from the purification of toluenediamine in the production of
    toluenediamine via hydrogenation of dinitrotoluene.
    NA NA CARBN; or
    CMBST
    CMBST

     
    898
     
    K114
    Vicinals from the purification of toluenediamine in the production of toluenediamine via hydro-
    genation of dinitrotoluene.
    NA NA CARBN; or
    CMBST
    CMBST
     
    K115
    Heavy ends from the purification of toluenediamine in the production of toluenediamine via
    hydrogenation of dinitrotoluene.
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
    NA NA CARBN; or
    CMBST
    CMBST
     
    K116
    Organic condensate from the solvent recovery column in the production of toluene diisocyanate
    via phosgenation of toluenediamine.
    NA NA CARBN; or
    CMBST
    CMBST
     
    K117
    Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via
    bromination of ethene.
    Methyl bromide (Bromo-
    methane)
    74-83-9 0.11 15
    Chloroform 67-66-3 0.046 6.0
    Ethylene dibromide (1,2-
    Dibromoethane)
    106-93-4 0.028 15
     
    K118
    Spent absorbent solids from purification of ethylene dibromide in the production of ethylene
    dibromide via bromination of ethene.
    Methyl bromide (Bromo-
    methane)
    74-83-9 0.11 15
    Chloroform 67-66-3 0.046 6.0
    Ethylene dibromide (1,2-
    Dibromoethane)
    106-93-4 0.028 15
     
    K123
    Process wastewater (including supernates, filtrates, and washwaters) from the production of
    ethylenebisdithiocarbamic acid and its salts.
    NA NA CMBST; or
    CHOXD fb
    (BIODG or
    CARBN)
    CMBST
     

     
    899
    K124
    Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.
    NA NA CMBST; or
    CHOXD fb
    (BIODG or
    CARBN)
    CMBST
     
    K125
    Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithio-
    carbamic acid and its salts.
    NA NA CMBST; or
    CHOXD fb
    (BIODG or
    CARBN)
    CMBST
     
    K126
    Baghouse dust and floor sweepings in milling and packaging operations from the production or
    formulation of ethylenebisdithiocarbamic acid and its salts.
    NA NA CMBST; or
    CHOXD fb
    (BIODG or
    CARBN)
    CMBST
     
    K131
    Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of
    methyl bromide.
    Methyl bromide (Bromo-
    methane)
    74-83-9 0.11 15
     
    K132
    Spent absorbent and wastewater separator solids from the production of methyl bromide.
    Methyl bromide (Bromo-
    methane)
    74-83-9 0.11 15
     
    K136
    Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide
    via bromination of ethene.
    Methyl bromide (Bromo-
    methane)
    74-83-9 0.11 15
    Chloroform 67-66-3 0.046 6.0
    Ethylene dibromide (1,2-
    Dibromoethane)
    106-93-4 0.028 15
     
    K141
    Process residues from the recovery of coal tar, including, but not limited to, collecting sump
    residues from the production of coke or the recovery of coke by-products produced from coal.

     
    900
    This listing does not include K087 (decanter tank tar sludge from coking operations).
    Benzene 71-43-2 0.14 10
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzo(a)pyrene 50-2-8 0.061 3.4
    Benzo(b)fluoranthene (difficult
    to distinguish from benzo(k)-
    fluoranthene)
    205-99-2 0.11 6.8
    Benzo(k)fluoranthene (difficult
    to distinguish from benzo(b)-
    fluoranthene)
    207-08-9 0.11 6.8
    Chrysene 218-01-9 0.059 3.4
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
    Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4
     
    K142
    Tar storage tank residues from the production of coke from coal or from the recovery of coke by-
    products produced from coal.
    Benzene 71-43-2 0.14 10
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Benzo(b)fluoranthene (difficult
    to distinguish from benzo(k)-
    fluoranthene)
    205-99-2 0.11 6.8
    Benzo(k)fluoranthene (difficult
    to distinguish from benzo(b)-
    fluoranthene)
    207-08-9 0.11 6.8
    Chrysene 218-01-9 0.059 3.4
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
    Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4
     
    K143
    Process residues from the recovery of light oil, including, but not limited to, those generated in
    stills, decanters, and wash oil recovery units from the recovery of coke by-products produced
    from coal.
    Benzene 71-43-2 0.14 10
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Benzo(b)fluoranthene (difficult
    to distinguish from benzo(k)-
    fluoranthene)
    205-99-2 0.11 6.8
    Benzo(k)fluoranthene (difficult
    to distinguish from benzo(b)-
    fluoranthene)
    207-08-9 0.11 6.8
    Chrysene 218-01-9 0.059 3.4
     

     
    901
    K144
    Wastewater sump residues from light oil refining, including, but not limited to, intercepting or
    contamination sump sludges from the recovery of coke by-products produced from coal.
    Benzene 71-43-2 0.14 10
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Benzo(b)fluoranthene (difficult
    to distinguish from benzo(k)-
    fluoranthene)
    205-99-2 0.11 6.8
    Benzo(k)fluoranthene (difficult
    to distinguish from benzo(b)-
    fluoranthene)
    207-08-9 0.11 6.8
    Chrysene 218-01-9 0.059 3.4
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
     
    K145
    Residues from naphthalene collection and recovery operations from the recovery of coke by-
    products produced from coal.
    Benzene 71-43-2 0.14 10
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Chrysene 218-01-9 0.059 3.4
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
    Naphthalene 91-20-3 0.059 5.6
     
    K147
    Tar storage tank residues from coal tar refining.
    Benzene 71-43-2 0.14 10
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Benzo(b)fluoranthene (difficult
    to distinguish from benzo(k)-
    fluoranthene)
    205-99-2 0.11 6.8
    Benzo(k)fluoranthene (difficult
    to distinguish from benzo(b)-
    fluoranthene)
    207-08-9 0.11 6.8
    Chrysene 218-01-9 0.059 3.4
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
    Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4
     
    K148
    Residues from coal tar distillation, including, but not limited to, still bottoms.
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzo(a)pyrene 50-32-8 0.061 3.4

     
    902
    Benzo(b)fluoranthene (difficult
    to distinguish from benzo(k)-
    fluoranthene)
    205-99-2 0.11 6.8
    Benzo(k)fluoranthene (difficult
    to distinguish from benzo(b)-
    fluoranthene)
    207-08-9 0.11 6.8
    Chrysene 218-01-9 0.059 3.4
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
    Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4
     
    K149
    Distillation bottoms from the production of
    α
    - (or methyl-) chlorinated toluenes, ring-chlorinated
    toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. (This
    waste does not include still bottoms from the distillations of benzyl chloride.)
    Chlorobenzene 108-90-7 0.057 6.0
    Chloroform 67-66-3 0.046 6.0
    Chloromethane 74-87-3 0.19 30
    p-Dichlorobenzene 106-46-7 0.090 6.0
    Hexachlorobenzene 118-74-1 0.055 10
    Pentachlorobenzene 608-93-5 0.055 10
    1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14
    Toluene 108-88-3 0.080 10
     
    K150
    Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydro-
    chloric acid recovery processes associated with the production of
    α
    - (or methyl-) chlorinated
    toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these
    functional groups.
    Carbon tetrachloride 56-23-5 0.057 6.0
    Chloroform 67-66-3 0.046 6.0
    Chloromethane 74-87-3 0.19 30
    p-Dichlorobenzene 106-46-7 0.090 6.0
    Hexachlorobenzene 118-74-1 0.055 10
    Pentachlorobenzene 608-93-5 0.055 10
    1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14
    1,1,2,2- Tetrachloroethane 79-34-5 0.057 6.0
    Tetrachloroethylene 127-18-4 0.056 6.0
    1,2,4-Trichlorobenzene 120-82-1 0.055 19
     
    K151
    Wastewater treatment sludges, excluding neutralization and biological sludges, generated during
    the treatment of wastewaters from the production of
    α
    - (or methyl-) chlorinated toluenes, ring-
    chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional
    groups.
    Benzene 71-43-2 0.14 10
    Carbon tetrachloride 56-23-5 0.057 6.0

     
    903
    Chloroform 67-66-3 0.046 6.0
    Hexachlorobenzene 118-74-1 0.055 10
    Pentachlorobenzene 608-93-5 0.055 10
    1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14
    Tetrachloroethylene 127-18-4 0.056 6.0
    Toluene 108-88-3 0.080 10
     
    K156
    Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and
    decantates) from the production of carbamates and carbamoyl oximes.
    10
     
    Acetonitrile 75-05-8 5.6 1.8
    Acetophenone 96-86-2 0.010 9.7
    Aniline 62-53-3 0.81 14
    Benomyl 17804-35-2 0.056 1.4
    Benzene 71-43-2 0.14 10
    Carbaryl 63-25-21 0.006 0.14
    Carbenzadim 10605-21-7 0.056 1.4
    Carbofuran 1563-66-2 0.006 0.14
    Carbosulfan 55285-14-8 0.028 1.4
    Chlorobenzene 108-90-7 0.057 6.0
    Chloroform 67-66-3 0.046 6.0
    o-Dichlorobenzene 95-50-1 0.088 6.0
    Methomyl 16752-77-5 0.028 0.14
    Methylene chloride 75-09-2 0.089 30
    Methyl ethyl ketone 78-93-3 0.28 36
    Naphthalene 91-20-3 0.059 5.6
    Phenol 108-95-2 0.039 6.2
    Pyridine 110-86-1 0.014 16
    Toluene 108-88-3 0.080 10
    Triethylamine 121-44-8 0.081 1.5
     
    K157
    Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters)
    from the production of carbamates and carbamoyl oximes.
    Carbon tetrachloride 56-23-5 0.057 6.0
    Chloroform 67-66-3 0.046 6.0
    Chloromethane 74-87-3 0.19 30
    Methomyl 16752-77-5 0.028 0.14
    Methylene chloride 75-09-2 0.089 30
    Methyl ethyl ketone 78-93-3 0.28 36
    Pyridine 110-86-1 0.014 16
    Triethylamine 121-44-8 0.081 1.5
     

     
    904
    K158
    Baghouse dusts and filter/separation solids from the production of carbamates and carbamoyl
    oximes.
    Benomyl 17804-35-2 0.056 1.4
    Benzene 71-43-2 0.14 10
    Carbenzadim 10605-21-7 0.056 1.4
    Carbofuran 1563-66-2 0.006 0.14
    Carbosulfan 55285-14-8 0.028 1.4
    Chloroform 67-66-3 0.046 6.0
    Methylene chloride 75-09-2 0.089 30
    Phenol 108-95-2 0.039 6.2
     
    K159
    Organics from the treatment of thiocarbamate wastes.
    10
     
    Benzene 71-43-2 0.14 10
    Butylate 2008-41-5 0.042 1.4
    EPTC (Eptam) 759-94-4 0.042 1.4
    Molinate 2212-67-1 0.042 1.4
    Pebulate 1114-71-2 0.042 1.4
    Vernolate 1929-77-7 0.042 1.4
     
    K161
    Purification solids (including filtration, evaporation, and centrifugation solids), baghouse dust
    and floor sweepings from the production of dithiocarbamate acids and their salts.
    Antimony 7440-36-0 1.9 1.15
    11
     
    Arsenic 7440-38-2 1.4 5.0
    11
     
    Carbon disulfide 75-15-0 3.8 4.8
    11
     
    Dithiocarbamates (total) 137-30-4 0.028 28
    Lead 7439-92-1 0.69 0.75
    11
     
    Nickel 7440-02-0 3.98 11
    11
     
    Selenium 7782-49-2 0.82 5.7
    11
     
     
    K169
    Crude oil tank sediment from petroleum refining operations.
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzene 71-43-2 0.14 10
    Benzo(g,h,i)perylene 191-24-2 0.0055 1.8
    Chrysene 218-01-9 0.059 3.4
    Ethyl benzene 100-41-4 0.057 10
    Fluorene 86-73-7 0.059 3.4
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 81-05-8 0.059 5.6
    Pyrene 129-00-0 0.067 8.2
    Toluene (Methyl Benzene) 108-88-3 0.080 10
    Xylenes (Total) 1330-20-7 0.32 30
     

     
    905
    K170
    Clarified slurry oil sediment from petroleum refining operations.
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzene 71-43-2 0.14 10
    Benzo(g,h,i)perylene 191-24-2 0.0055 1.8
    Chrysene 218-01-9 0.059 3.4
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
    Ethyl benzene 100-41-4 0.057 10
    Fluorene 86-73-7 0.059 3.4
    Indeno(1,2,3,-cd)pyrene 193-39-5 0.0055 3.4
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 81-05-8 0.059 5.6
    Pyrene 129-00-0 0.067 8.2
    Toluene (Methyl Benzene) 108-88-3 0.080 10
    Xylenes (Total 1330-20-7 0.32 30
     
    K171
    Spent hydrotreating catalyst from petroleum refining operations, including guard beds used to
    desulfurize feeds to other catalytic reactors. (This listing does not include inert support media.)
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzene 71-43-2 0.14 10
    Chrysene 218-01-9 0.059 3.4
    Ethyl benzene 100-41-4 0.057 10
    Naphthalene 91-20-3 0.059 5.6
    Phenanthrene 81-05-8 0.059 5.6
    Pyrene 129-00-0 0.067 8.2
    Toluene (Methyl Benzene) 108-88-3 0.080 10
    Xylenes (Total) 1330-20-7 0.32 30
    Arsenic 7740-38-2 1.4 5 mg/lmg/
    TCLP
    Nickel 7440-02-0 3.98 11.0 mg/lmg/
     
    TCLP
    Vanadium 7440-62-2 4.3 1.6 mg/lmg/
     
    TCLP
    Reactive sulfides NA DEACT DEACT
     
    K172
    Spent hydrorefining catalyst from petroleum refining operations, including guard beds used to
    desulfurize feeds to other catalytic reactors. (This listing does not include inert support media.)
    Benzene 71-43-2 0.14 10
    Ethyl benzene 100-41-4 0.057 10
    Toluene (Methyl Benzene) 108-88-3 0.080 10
    Xylenes (Total) 1330-20-7 0.32 30
    Antimony 7740-36-0 1.9 1.15 mg/lmg/
     
    TCLP
    Arsenic 7740-38-2 1.4 5 mg/lmg/
    TCLP

     
    906
    Nickel 7440-02-0 3.98 11.0 mg/lmg/
     
    TCLP
    Vanadium 7440-62-2 4.3 1.6 mg/lmg/
     
    TCLP
    Reactive Sulfides NA DEACT DEACT
     
    K174
    Wastewater treatment sludge from the production of ethylene dicholoride or vinyl choloride
    monomer.
    1,2,3,4,6,7,8-Heptachloro-
    dibenzo-p-dioxin (1,2,3,4,6,7,8-
    HpCDD)
    35822-46-9 0.000035 or
    CMBST
    11
    0.0025 or
    CMBST
    11
     
    1,2,3,4,6,7,8-Heptachloro-
    dibenzofuran (1,2,3,4,6,7,8-
    HpCDF)
    67562-39-4 0.000035 or
    CMBST
    11
     
    0.0025 or
    CMBST
    11
     
    1,2,3,4,7,8,9-Heptachloro-
    dibenzofuran (1,2,3,4,7,8,9-
    HpCDF)
    55673-89-7 0.000035 or
    CMBST
    11
     
    0.0025 or
    CMBST
    11
     
    All hexachlorodibenzo-p-dioxins
    (HxCDDs)
    34465-46-8 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    All hexachlorodibenzofurans
    (HxCDFs)
    55684-94-1 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    1,2,3,4,6,7,8,9-Octachloro-
    dibenzo-p-dioxin
    (1,2,3,4,6,7,8,9-OCDD)
    3268-87-9 0.000063 or
    CMBST
    11
     
    0.005 or CMBST
    11
     
    1,2,3,4,6,7,8,9-Octachloro-
    dibenzofuran (1,2,3,4,6,7,8,9-
    OCDF)
    39001-02-0 0.000063 or
    CMBST
    11
     
    0.005 or CMBST
    11
     
    All pentachlorodibenzo-p-
    dioxins (PeCDDs)
    36088-22-9 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    All pentachlorodibenzofurans
    (PeCDFs)
    30402-15-4 0.000035 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    All tetrachlorodibenzo-p-dioxins
    (TCDDs)
    41903-57-5 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    All tetrachlorodibenzofurans
    (TCDFs)
    55722-27-5 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    Arsenic 7440-36-0 1.4 5.0 mg/Lmg/
     
    TCLP
     
    K175
    Wastewater treatment sludge from the production of vinyl choloride monomer using mercuric
    chloride catalyst in an acetylene-based process.
    Mercury
    12
    7439-97-6 NA 0.025 mg/Lmg/
     
    TCLP
    PH
    12
    NA pH
    6.0
     

     
    907
    K175
    All K175 wastewaters.
    Mercury 7439-97-6 0.15 NA
     
    K176
    Baghouse filters from the production of antimony oxide, including filters from the production of
    intermediates e.g., antimony metal or crude antimony oxide).
    Antimony 7440-36-0 1.9 1.15 mg/Lmg/
     
    TCLP
    Arsenic 7440-38-2 1.4 5.0 mg/Lmg/
     
    TCLP
    Cadmium 7440-43-9 0.69 0.11 mg/Lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/Lmg/
     
    TCLP
    Mercury 7439-97-6 0.15 0.025 mg/Lmg/
     
    TCLP
     
    K177
    Slag from the production of antimony oxide that is speculatively accumulated or disposed,
    including slag from the production of intermediates (e.g., antimony metal or crude antimony
    oxide).
    Antimony 7440-36-0 1.9 1.15 mg/Lmg/
     
    TCLP
    Arsenic 7440-38-2 1.4 5.0 mg/Lmg/
     
    TCLP
    Lead 7439-92-1 0.69 0.75 mg/Lmg/
     
    TCLP
     
    K178
    Residues from manufacturing and manufacturing-site storage of ferric chloride from acids
    formed during the production of titanium dioxide using the chloride-ilmenite process.
    1,2,3,4,6,7,8-Heptachloro-
    dibenzo-p-dioxin (1,2,3,4,6,7,8-
    HpCDD)
    35822-46-9 0.000035 or
    CMBST
    11
     
    0.0025 or
    CMBST
    11
     
    1,2,3,4,6,7,8-Heptachloro-
    dibenzofuran (1,2,3,4,6,7,8-
    HpCDF)
    67562-39-4 0.000035 or
    CMBST
    11
     
    0.0025 or
    CMBST
    11
     
    1,2,3,4,7,8,9-Heptachloro-
    dibenzofuran (1,2,3,4,7,8,9-
    HpCDF)
    55673-89-7 0.000035 or
    CMBST
    11
     
    0.0025 or
    CMBST
    11
     
    HxCDDs (All Hexachloro-
    dibenzo-p-dioxins)
    34465-46-8 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    HxCDFs (All Hexachloro-
    dibenzofurans)
    55684-94-1 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     

     
    908
    1,2,3,4,6,7,8,9-Octachloro-
    dibenzo-p-dioxin
    (1,2,3,4,6,7,8,9-OCDD)
    3268-87-9 0.000063 or
    CMBST
    11
     
    0.005 or CMBST
    11
     
    1,2,3,4,6,7,8,9-Octachloro-
    dibenzofuran (OCDF)
    39001-02-0 0.000063 or
    CMBST
    11
     
    0.005 or CMBST
    11
     
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    36088-22-9 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    PeCDFs (All Pentachloro-
    dibenzofurans)
    30402-15-4 0.000035 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    41903-57-5 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    TCDFs (All Tetrachloro-
    dibenzofurans)
    55722-27-5 0.000063 or
    CMBST
    11
     
    0.001 or CMBST
    11
     
    Thallium 7440-28-0 1.4 0.20 mg/Lmg/
     
    TCLP
     
    K181
    Nonwastewaters from the production of dyes or pigments (including nonwastewaters
    commingled at the point of generation with nonwastewaters from other processes) that, at the
    point of generation, contain mass loadings of any of the constituents identified in Section
    721.132(c) which are equal to or greater than the corresponding Section 721.132(c) levels, as
    determined on a calendar-year basis.
    Aniline 62-53-3 0.81 14
    o-Anisidine (2-methoxyaniline) 90-04-0 0.010 0.66
    4-Chloroaniline 106-47-8 0.46 16
    p-Cresidine 120-71-8 0.010 0.66
    2,4-Dimethylaniline (2,4-
    xylidine)
    95-68-1 0.010 0.66
    1,2-Phenylenediamine 95-54-5 CMBST; or
    CHOXD fb
    (BIODG or
    CARBN); or
    BIODG fb
    CARBN
    CMBST; or
    CHOXD fb
    (BIODG or
    CARBN); or
    BIODG fb
    CARBN
    1,3-Phenylenediamine 108-45-2 0.010 0.66
     
    P001
    Warfarin, & salts, when present at concentrations greater than 0.3 percent.
    Warfarin 81-81-2 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     

     
    909
    P002
    1-Acetyl-2-thiourea.
    1-Acetyl-2-thiourea 591-08-2 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P003
    Acrolein.
    Acrolein 107-02-8 0.29 CMBST
     
    P004
    Aldrin.
    Aldrin 309-00-2 0.021 0.066
     
    P005
    Allyl alcohol.
    Allyl alcohol 107-18-6 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P006
    Aluminum phosphide.
    Aluminum phosphide 20859-73-8 CHOXD; CHRED;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    P007
    5-Aminomethyl-3-isoxazolol.
    5-Aminomethyl-3-isoxazolol 2763-96-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P008
    4-Aminopyridine.
    4-Aminopyridine 504-24-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P009
    Ammonium picrate.
    Ammonium picrate 131-74-8 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED;
    or CMBST

     
    910
     
    P010
    Arsenic acid.
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
     
    P011
    Arsenic pentoxide.
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
     
    P012
    Arsenic trioxide.
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
     
    P013
    Barium cyanide.
    Barium 7440-39-3 NA 21 mg/lmg/
    TCLP
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
     
    P014
    Thiophenol (Benzene thiol).
    Thiophenol (Benzene thiol) 108-98-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P015
    Beryllium dust.
    Beryllium 7440-41-7 RMETL;or
    RTHRM
    RMETL; or
    RTHRM
     
    P016
    Dichloromethyl ether (Bis(chloromethyl)ether).
    Dichloromethyl ether 542-88-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     

     
    911
    P017
    Bromoacetone.
    Bromoacetone 598-31-2 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P018
    Brucine.
    Brucine 357-57-3 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P020
    2-sec-Butyl-4,6-dinitrophenol (Dinoseb).
    2-sec-Butyl-4,6-dinitrophenol
    (Dinoseb)
    88-85-7 0.066 2.5
     
    P021
    Calcium cyanide.
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
     
    P022
    Carbon disulfide.
    Carbon disulfide 75-15-0 3.8 CMBST
    Carbon disulfide; alternate
    6
     
    standard for nonwastewaters
    only
    75-15-0 NA 4.8 mg/lmg/
     
    TCLP
     
    P023
    Chloroacetaldehyde.
    Chloroacetaldehyde 107-20-0 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P024
    p-Chloroaniline.
    p-Chloroaniline 106-47-8 0.46 16
     

     
    912
    P026
    1-(o-Chlorophenyl)thiourea.
    1-(o-Chlorophenyl)thiourea 5344-82-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P027
    3-Chloropropionitrile.
    3-Chloropropionitrile 542-76-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P028
    Benzyl chloride.
    Benzyl chloride 100-44-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P029
    Copper cyanide.
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
     
    P030
    Cyanides (soluble salts and complexes).
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
     
    P031
    Cyanogen.
    Cyanogen 460-19-5 CHOXD;
    WETOX; or
    CMBST
    CHOXD;
    WETOX; or
    CMBST
     
    P033
    Cyanogen chloride.
    Cyanogen chloride 506-77-4 CHOXD;
    WETOX; or
    CMBST
    CHOXD;
    WETOX; or
    CMBST
     

     
    913
    P034
    2-Cyclohexyl-4,6-dinitrophenol.
    2-Cyclohexyl-4,6-dinitrophenol 131-89-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P036
    Dichlorophenylarsine.
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
     
    P037
    Dieldrin.
    Dieldrin 60-57-1 0.017 0.13
     
    P038
    Diethylarsine.
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
     
    P039
    Disulfoton.
    Disulfoton 298-04-4 0.017 6.2
     
    P040
    O,O-Diethyl-O-pyrazinyl-phosphorothioate.
    O,O-Diethyl-O-pyrazinyl-
    phosphorothioate
    297-97-2 CARBN; or
    CMBST
    CMBST
     
    P041
    Diethyl-p-nitrophenyl phosphate.
    Diethyl-p-nitrophenyl phosphate 311-45-5 CARBN; or
    CMBST
    CMBST
     
    P042
    Epinephrine.
    Epinephrine 51-43-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P043
    Diisopropylfluorophosphate (DFP).
    Diisopropylfluorophosphate
    (DFP)
    55-91-4 CARBN; or
    CMBST
    CMBST

     
    914
     
    P044
    Dimethoate.
    Dimethoate 60-51-5 CARBN; or
    CMBST
    CMBST
     
    P045
    Thiofanox.
    Thiofanox 39196-18-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P046
    α
    ,
    α
    -Dimethylphenethylamine.
    α
    ,
    α
    -Dimethylphenethylamine
    122-09-8 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P047
    4,6-Dinitro-o-cresol.
    4,6-Dinitro-o-cresol 543-52-1 0.28 160
     
    P047
    4,6-Dinitro-o-cresol salts.
    NA NA (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P048
    2,4-Dinitrophenol.
    2,4-Dinitrophenol 51-28-5 0.12 160
     
    P049
    Dithiobiuret.
    Dithiobiuret 541-53-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P050
    Endosulfan.
    Endosulfan I 939-98-8 0.023 0.066
    Endosulfan II 33213-6-5 0.029 0.13

     
    915
    Endosulfan sulfate 1031-07-8 0.029 0.13
     
    P051
    Endrin.
    Endrin 72-20-8 0.0028 0.13
    Endrin aldehyde 7421-93-4 0.025 0.13
     
    P054
    Aziridine.
    Aziridine 151-56-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P056
    Fluorine.
    Fluoride (measured in
    wastewaters only)
    16964-48-8 35 ADGAS fb
    NEUTR
     
    P057
    Fluoroacetamide.
    Fluoroacetamide 640-19-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P058
    Fluoroacetic acid, sodium salt.
    Fluoroacetic acid, sodium salt 62-74-8 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P059
    Heptachlor.
    Heptachlor 76-44-8 0.0012 0.066
    Heptachlor epoxide 1024-57-3 0.016 0.066
     
    P060
    Isodrin.
    Isodrin 465-73-6 0.021 0.066
     
    P062
    Hexaethyl tetraphosphate.
    Hexaethyl tetraphosphate 757-58-4 CARBN; or
    CMBST
    CMBST

     
    916
     
    P063
    Hydrogen cyanide.
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
     
    P064
    Isocyanic acid, ethyl ester.
    Isocyanic acid, ethyl ester 624-83-9 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P065
    P065 (mercury fulminate) nonwastewaters, regardless of their total mercury content, that are not
    incinerator residues or are not residues from RMERC.
    Mercury 7439-97-6 NA IMERC
     
    P065
    P065 (mercury fulminate) nonwastewaters that are either incinerator residues or are residues
    from RMERC; and contain greater than or equal to 260 mg/kg total mercury.
    Mercury 7339-97-6 NA RMERC
     
    P065
    P065 (mercury fulminate) nonwastewaters that are residues from RMERC and contain less than
    260 mg/kg total mercury.
    Mercury 7439-97-6 NA 0.20 mg/lmg/
     
    TCLP
     
    P065
    P065 (mercury fulminate) nonwastewaters that are incinerator residues and contain less than 260
    mg/kg total mercury.
    Mercury 7439-97-6 NA 0.025 mg/lmg/
     
    TCLP
     
    P065
    All P065 (mercury fulminate) wastewaters.
    Mercury 7439-97-6 0.15 NA
     
    P066
    Methomyl.
    Methomyl 16752-77-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     

     
    917
    P067
    2-Methyl-aziridine.
    2-Methyl-aziridine 75-55-8 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P068
    Methyl hydrazine.
    Methyl hydrazine 60-34-4 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED,
    or CMBST
     
    P069
    2-Methyllactonitrile.
    2-Methyllactonitrile 75-86-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P070
    Aldicarb.
    Aldicarb 116-06-3 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P071
    Methyl parathion.
    Methyl parathion 298-00-0 0.014 4.6
     
    P072
    1-Naphthyl-2-thiourea.
    1-Naphthyl-2-thiourea 86-88-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P073
    Nickel carbonyl.
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
     
    P074
    Nickel cyanide.
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30

     
    918
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
     
    P075
    Nicotine and salts.
    Nicotine and salts 54-11-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P076
    Nitric oxide.
    Nitric oxide 10102-43-9 ADGAS ADGAS
     
    P077
    p-Nitroaniline.
    p-Nitroaniline 100-01-6 0.028 28
     
    P078
    Nitrogen dioxide.
    Nitrogen dioxide 10102-44-0 ADGAS ADGAS
     
    P081
    Nitroglycerin.
    Nitroglycerin 55-63-0 CHOXD; CHRED;
    CARBN; BIODG
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    P082
    N-Nitrosodimethylamine.
    N-Nitrosodimethylamine 62-75-9 0.40 2.3
     
    P084
    N-Nitrosomethylvinylamine.
    N-Nitrosomethylvinylamine 4549-40-0 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P085
    Octamethylpyrophosphoramide.
    Octamethylpyrophosphoramide 152-16-9 CARBN; or
    CMBST
    CMBST
     

     
    919
    P087
    Osmium tetroxide.
    Osmium tetroxide 20816-12-0 RMETL; or
    RTHRM
    RMETL; or
    RTHRM
     
    P088
    Endothall.
    Endothall 145-73-3 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P089
    Parathion.
    Parathion 56-38-2 0.014 4.6
     
    P092
    P092 (phenyl mercuric acetate) nonwastewaters, regardless of their total mercury content, that
    are not incinerator residues or are not residues from RMERC.
    Mercury 7439-97-6 NA IMERC; or
    RMERC
     
    P092
    P092 (phenyl mercuric acetate) nonwastewaters that are either incinerator residues or are
    residues from RMERC; and still contain greater than or equal to 260 mg/kg total mercury.
    Mercury 7439-97-6 NA RMERC
     
    P092
    P092 (phenyl mercuric acetate) nonwastewaters that are residues from RMERC and contain less
    than 260 mg/kg total mercury.
    Mercury 7439-97-6 NA 0.20 mg/lmg/
     
    TCLP
     
    P092
    P092 (phenyl mercuric acetate) nonwastewaters that are incinerator residues and contain less
    than 260 mg/kg total mercury.
    Mercury 7439-97-6 NA 0.025 mg/lmg/
     
    TCLP
     
    P092
    All P092 (phenyl mercuric acetate) wastewaters.
    Mercury 7439-97-6 0.15 NA
     

     
    920
    P093
    Phenylthiourea.
    Phenylthiourea 103-85-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P094
    Phorate.
    Phorate 298-02-2 0.021 4.6
     
    P095
    Phosgene.
    Phosgene 75-44-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P096
    Phosphine.
    Phosphine 7803-51-2 CHOXD; CHRED;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    P097
    Famphur.
    Famphur 52-85-7 0.017 15
     
    P098
    Potassium cyanide.
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
     
    P099
    Potassium silver cyanide.
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
    Silver 7440-22-4 0.43 0.14 mg/lmg/
     
    TCLP
     
    P101
    Ethyl cyanide (Propanenitrile).
    Ethyl cyanide (Propanenitrile) 107-12-0 0.24 360
     

     
    921
    P102
    Propargyl alcohol.
    Propargyl alcohol 107-19-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P103
    Selenourea.
    Selenium 7782-49-2 0.82 5.7 mg/lmg/
     
    TCLP
     
    P104
    Silver cyanide.
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
    Silver 7440-22-4 0.43 0.14 mg/lmg/
     
    TCLP
     
    P105
    Sodium azide.
    Sodium azide 26628-22-8 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    P106
    Sodium cyanide.
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
     
    P108
    Strychnine and salts.
    Strychnine and salts 57-24-9 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P109
    Tetraethyldithiopyrophosphate.
    Tetraethyldithiopyrophosphate 3689-24-5 CARBN; or
    CMBST
    CMBST
     
    P110
    Tetraethyl lead.
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP

     
    922
     
    P111
    Tetraethylpyrophosphate.
    Tetraethylpyrophosphate 107-49-3 CARBN; or
    CMBST
    CMBST
     
    P112
    Tetranitromethane.
    Tetranitromethane 509-14-8 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    P113
    Thallic oxide.
    Thallium (measured in
    wastewaters only)
    7440-28-0 1.4 RTHRM; or
    STABL
     
    P114
    Thallium selenite.
    Selenium 7782-49-2 0.82 5.7 mg/lmg/
     
    TCLP
     
    P115
    Thallium (I) sulfate.
    Thallium (measured in
    wastewaters only)
    7440-28-0 1.4 RTHRM; or
    STABL
     
    P116
    Thiosemicarbazide.
    Thiosemicarbazide 79-19-6 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P118
    Trichloromethanethiol.
    Trichloromethanethiol 75-70-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    P119
    Ammonium vanadate.
    Vanadium (measured in
    wastewaters only)
    7440-62-2 4.3 STABL
     

     
    923
    P120
    Vanadium pentoxide.
    Vanadium (measured in
    wastewaters only)
    7440-62-2 4.3 STABL
     
    P121
    Zinc cyanide.
    Cyanides (Total)
    7
    57-12-5 1.2 590
    Cyanides (Amenable)
    7
    57-12-5 0.86 30
     
    P122
    Zinc phosphide Zn3P2, when present at concentrations greater than 10 percent.
    Zinc Phosphide 1314-84-7 CHOXD; CHRED;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    P123
    Toxaphene.
    Toxaphene 8001-35-2 0.0095 2.6
     
    P127
    Carbofuran.
    Carbofuran 1563-66-2 0.006 0.14
     
    P128
    Mexacarbate.
    Mexacarbate 315-18-4 0.056 1.4
     
    P185
    Tirpate.
    10
     
    Tirpate 26419-73-8 0.056 0.28
     
    P188
    Physostigimine salicylate.
    Physostigmine salicylate 57-64-7 0.056 1.4
     
    P189
    Carbosulfan.
    Carbosulfan 55285-14-8 0.028 1.4
     
    P190
    Metolcarb.
    Metolcarb 1129-41-5 0.056 1.4
     
    P191
    Dimetilan.
    10
     
    Dimetilan 644-64-4 0.056 1.4

     
    924
     
    P192
    Isolan.
    10
     
    Isolan 119-38-0 0.056 1.4
     
    P194
    Oxamyl.
    Oxamyl 23135-22-0 0.056 0.28
     
    P196
    Manganese dimethyldithiocarbamates (total).
    Dithiocarbamates (total) NA 0.028 28
     
    P197
    Formparanate.
    10
     
    Formparanate 17702-57-7 0.056 1.4
     
    P198
    Formetanate hydrochloride.
    Formetanate hydrochloride 23422-53-9 0.056 1.4
     
    P199
    Methiocarb.
    Methiocarb 2032-65-7 0.056 1.4
     
    P201
    Promecarb.
    Promecarb 2631-37-0 0.056 1.4
     
    P202
    m-Cumenyl methylcarbamate.
    m-Cumenyl methylcarbamate 64-00-6 0.056 1.4
     
    P203
    Aldicarb sulfone.
    Aldicarb sulfone 1646-88-4 0.056 0.28
     
    P204
    Physostigmine.
    Physostigmine 57-47-6 0.056 1.4
     
    P205
    Ziram.
    Dithiocarbamates (total) NA 0.028 28
     

     
    925
    U001
    Acetaldehyde.
    Acetaldehyde 75-07-0 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U002
    Acetone.
    Acetone 67-64-1 0.28 160
     
    U003
    Acetonitrile.
    Acetonitrile 75-05-8 5.6 CMBST
    Acetonitrile; alternate
    6
    standard
    for nonwastewaters only
    75-05-8 NA 38
     
    U004
    Acetophenone.
    Acetophenone 98-86-2 0.010 9.7
     
    U005
    2-Acetylaminofluorene.
    2-Acetylaminofluorene 53-96-3 0.059 140
     
    U006
    Acetyl chloride.
    Acetyl chloride 75-36-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U007
    Acrylamide.
    Acrylamide 79-06-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U008
    Acrylic acid.
    Acrylic acid 79-10-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     

     
    926
    U009
    Acrylonitrile.
    Acrylonitrile 107-13-1 0.24 84
     
    U010
    Mitomycin C.
    Mitomycin C 50-07-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U011
    Amitrole.
    Amitrole 61-82-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U012
    Aniline.
    Aniline 62-53-3 0.81 14
     
    U014
    Auramine.
    Auramine 492-80-8 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U015
    Azaserine.
    Azaserine 115-02-6 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U016
    Benz(c)acridine.
    Benz(c)acridine 225-51-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     

     
    927
    U017
    Benzal chloride.
    Benzal chloride 98-87-3 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U018
    Benz(a)anthracene.
    Benz(a)anthracene 56-55-3 0.059 3.4
     
    U019
    Benzene.
    Benzene 71-43-2 0.14 10
     
    U020
    Benzenesulfonyl chloride.
    Benzenesulfonyl chloride 98-09-9 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U021
    Benzidine.
    Benzidine 92-87-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U022
    Benzo(a)pyrene.
    Benzo(a)pyrene 50-32-8 0.061 3.4
     
    U023
    Benzotrichloride.
    Benzotrichloride 98-07-7 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    U024
    bis(2-Chloroethoxy)methane.
    bis(2-Chloroethoxy)methane 111-91-1 0.036 7.2
     
    U025
    bis(2-Chloroethyl)ether.
    bis(2-Chloroethyl)ether 111-44-4 0.033 6.0

     
    928
     
    U026
    Chlornaphazine.
    Chlornaphazine 494-03-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U027
    bis(2-Chloroisopropyl)ether.
    bis(2-Chloroisopropyl)ether 39638-32-9 0.055 7.2
     
    U028
    bis(2-Ethylhexyl)phthalate.
    bis(2-Ethylhexyl)phthalate 117-81-7 0.28 28
     
    U029
    Methyl bromide (Bromomethane).
    Methyl bromide (Bromo-
    methane)
    74-83-9 0.11 15
     
    U030
    4-Bromophenyl phenyl ether.
    4-Bromophenyl phenyl ether 101-55-3 0.055 15
     
    U031
    n-Butyl alcohol.
    n-Butyl alcohol 71-36-3 5.6 2.6
     
    U032
    Calcium chromate.
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
     
    U033
    Carbon oxyfluoride.
    Carbon oxyfluoride 353-50-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     

     
    929
    U034
    Trichloroacetaldehyde (Chloral).
    Trichloroacetaldehyde (Chloral) 75-87-6 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U035
    Chlorambucil.
    Chlorambucil 305-03-3 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U036
    Chlordane.
    Chlordane (
    α
    and
    χ
    isomers)
    57-74-9 0.0033 0.26
     
    U037
    Chlorobenzene.
    Chlorobenzene 108-90-7 0.057 6.0
     
    U038
    Chlorobenzilate.
    Chlorobenzilate 510-15-6 0.10 CMBST
     
    U039
    p-Chloro-m-cresol.
    p-Chloro-m-cresol 59-50-7 0.018 14
     
    U041
    Epichlorohydrin (1-Chloro-2,3-epoxypropane).
    Epichlorohydrin (1-Chloro-2,3-
    epoxypropane)
    106-89-8 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U042
    2-Chloroethyl vinyl ether.
    2-Chloroethyl vinyl ether 110-75-8 0.062 CMBST
     
    U043
    Vinyl chloride.
    Vinyl chloride 75-01-4 0.27 6.0
     

     
    930
    U044
    Chloroform.
    Chloroform 67-66-3 0.046 6.0
     
    U045
    Chloromethane (Methyl chloride).
    Chloromethane (Methyl
    chloride)
    74-87-3 0.19 30
     
    U046
    Chloromethyl methyl ether.
    Chloromethyl methyl ether 107-30-2 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U047
    2-Chloronaphthalene.
    2-Chloronaphthalene 91-58-7 0.055 5.6
     
    U048
    2-Chlorophenol.
    2-Chlorophenol 95-57-8 0.044 5.7
     
    U049
    4-Chloro-o-toluidine hydrochloride.
    4-Chloro-o-toluidine hydro-
    chloride
    3165-93-3 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U050
    Chrysene.
    Chrysene 218-01-9 0.059 3.4
     
    U051
    Creosote.
    Naphthalene 91-20-3 0.059 5.6
    Pentachlorophenol 87-86-5 0.089 7.4
    Phenanthrene 85-01-8 0.059 5.6
    Pyrene 129-00-0 0.067 8.2
    Toluene 108-88-3 0.080 10
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30

     
    931
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    U052
    Cresols (Cresylic acid).
    o-Cresol 95-48-7 0.11 5.6
    m-Cresol (difficult to
    distinguish from p-cresol)
    108-39-4 0.77 5.6
    p-Cresol (difficult to distinguish
    from m-cresol)
    106-44-5 0.77 5.6
    Cresol-mixed isomers (Cresylic
    acid)
    (sum of o-, m-, and p-cresol
    concentrations)
    1319-77-3 0.88 11.2
     
    U053
    Crotonaldehyde.
    Crotonaldehyde 4170-30-3 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U055
    Cumene.
    Cumene 98-82-8 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U056
    Cyclohexane.
    Cyclohexane 110-82-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U057
    Cyclohexanone.
    Cyclohexanone 108-94-1 0.36 CMBST
    Cyclohexanone; alternate
    6
     
    standard for nonwastewaters
    only
    108-94-1 NA 0.75 mg/lmg/
     
    TCLP
     

     
    932
    U058
    Cyclophosphamide.
    Cyclophosphamide 50-18-0 CARBN; or
    CMBST
    CMBST
     
    U059
    Daunomycin.
    Daunomycin 20830-81-3 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U060
    DDD.
    o,p'-DDD 53-19-0 0.023 0.087
    p,p'-DDD 72-54-8 0.023 0.087
     
    U061
    DDT.
    o,p'-DDT 789-02-6 0.0039 0.087
    p,p'-DDT 50-29-3 0.0039 0.087
    o,p'-DDD 53-19-0 0.023 0.087
    p,p'-DDD 72-54-8 0.023 0.087
    o,p'-DDE 3424-82-6 0.031 0.087
    p,p'-DDE 72-55-9 0.031 0.087
     
    U062
    Diallate.
    Diallate 2303-16-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U063
    Dibenz(a,h)anthracene.
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
     
    U064
    Dibenz(a,i)pyrene.
    Dibenz(a,i)pyrene 189-55-9 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     

     
    933
    U066
    1,2-Dibromo-3-chloropropane.
    1,2-Dibromo-3-chloropropane 96-12-8 0.11 15
     
    U067
    Ethylene dibromide (1,2-Dibromoethane).
    Ethylene dibromide (1,2-
    Dibromoethane)
    106-93-4 0.028 15
     
    U068
    Dibromomethane.
    Dibromomethane 74-95-3 0.11 15
     
    U069
    Di-n-butyl phthalate.
    Di-n-butyl phthalate 84-74-2 0.057 28
     
    U070
    o-Dichlorobenzene.
    o-Dichlorobenzene 95-50-1 0.088 6.0
     
    U071
    m-Dichlorobenzene.
    m-Dichlorobenzene 541-73-1 0.036 6.0
     
    U072
    p-Dichlorobenzene.
    p-Dichlorobenzene 106-46-7 0.090 6.0
     
    U073
    3,3'-Dichlorobenzidine.
    3,3'-Dichlorobenzidine 91-94-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U074
    1,4-Dichloro-2-butene.
    cis-1,4-Dichloro-2-butene 1476-11-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
    trans-1,4-Dichloro-2-butene 764-41-0 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST

     
    934
     
    U075
    Dichlorodifluoromethane.
    Dichlorodifluoromethane 75-71-8 0.23 7.2
     
    U076
    1,1-Dichloroethane.
    1,1-Dichloroethane 75-34-3 0.059 6.0
     
    U077
    1,2-Dichloroethane.
    1,2-Dichloroethane 107-06-2 0.21 6.0
     
    U078
    1,1-Dichloroethylene.
    1,1-Dichloroethylene 75-35-4 0.025 6.0
     
    U079
    1,2-Dichloroethylene.
    trans-1,2-Dichloroethylene 156-60-5 0.054 30
     
    U080
    Methylene chloride.
    Methylene chloride 75-09-2 0.089 30
     
    U081
    2,4-Dichlorophenol.
    2,4-Dichlorophenol 120-83-2 0.044 14
     
    U082
    2,6-Dichlorophenol.
    2,6-Dichlorophenol 87-65-0 0.044 14
     
    U083
    1,2-Dichloropropane.
    1,2-Dichloropropane 78-87-5 0.85 18
     
    U084
    1,3-Dichloropropylene.
    cis-1,3-Dichloropropylene 10061-01-5 0.036 18
    trans-1,3-Dichloropropylene 10061-02-6 0.036 18
     

     
    935
    U085
    1,2:3,4-Diepoxybutane.
    1,2:3,4-Diepoxybutane 1464-53-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U086
    N,N'-Diethylhydrazine.
    N,N'-Diethylhydrazine 1615-80-1 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    U087
    O,O-Diethyl-S-methyldithiophosphate.
    O,O-Diethyl-S-methyldithio-
    phosphate
    3288-58-2 CARBN; or
    CMBST
    CMBST
     
    U088
    Diethyl phthalate.
    Diethyl phthalate 84-66-2 0.20 28
     
    U089
    Diethyl stilbestrol.
    Diethyl stilbestrol 56-53-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U090
    Dihydrosafrole.
    Dihydrosafrole 94-58-6 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U091
    3,3'-Dimethoxybenzidine.
    3,3'-Dimethoxybenzidine 119-90-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     

     
    936
    U092
    Dimethylamine.
    Dimethylamine 124-40-3 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U093
    p-Dimethylaminoazobenzene.
    p-Dimethylaminoazobenzene 60-11-7 0.13 CMBST
     
    U094
    7,12-Dimethylbenz(a)anthracene.
    7,12-Dimethylbenz(a)-
    anthracene
    57-97-6 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U095
    3,3'-Dimethylbenzidine.
    3,3'-Dimethylbenzidine 119-93-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U096
    α
    ,
    α
    -Dimethyl benzyl hydroperoxide.
    α
    ,
    α
    -Dimethyl benzyl hydro-
    peroxide
    80-15-9 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    U097
    Dimethylcarbamoyl chloride.
    Dimethylcarbamoyl chloride 79-44-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U098
    1,1-Dimethylhydrazine.
    1,1-Dimethylhydrazine 57-14-7 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     

     
    937
    U099
    1,2-Dimethylhydrazine.
    1,2-Dimethylhydrazine 540-73-8 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    U101
    2,4-Dimethylphenol.
    2,4-Dimethylphenol 105-67-9 0.036 14
     
    U102
    Dimethyl phthalate.
    Dimethyl phthalate 131-11-3 0.047 28
     
    U103
    Dimethyl sulfate.
    Dimethyl sulfate 77-78-1 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    U105
    2,4-Dinitrotoluene.
    2,4-Dinitrotoluene 121-14-2 0.32 140
     
    U106
    2,6-Dinitrotoluene.
    2,6-Dinitrotoluene 606-20-2 0.55 28
     
    U107
    Di-n-octyl phthalate.
    Di-n-octyl phthalate 117-84-0 0.017 28
     
    U108
    1,4-Dioxane.
    1,4-Dioxane 123-91-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
    1,4-Dioxane; alternate
    6
    standard
    for nonwastewaters only
    123-91-1 12.0 170
     
    U109
    1,2-Diphenylhydrazine.
    1,2-Diphenylhydrazine 122-66-7 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED;
    or CMBST

     
    938
    1,2-Diphenylhydrazine;
    alternate
    6
    standard for
    wastewaters only
    122-66-7 0.087 NA
     
    U110
    Dipropylamine.
    Dipropylamine 142-84-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U111
    Di-n-propylnitrosamine.
    Di-n-propylnitrosamine 621-64-7 0.40 14
     
    U112
    Ethyl acetate.
    Ethyl acetate 141-78-6 0.34 33
     
    U113
    Ethyl acrylate.
    Ethyl acrylate 140-88-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U114
    Ethylenebisdithiocarbamic acid salts and esters.
    Ethylenebisdithiocarbamic acid 111-54-6 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U115
    Ethylene oxide.
    Ethylene oxide 75-21-8 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CHOXD; or
    CMBST
    Ethylene oxide; alternate
    6
     
    standard for wastewaters only
    75-21-8 0.12 NA
     

     
    939
    U116
    Ethylene thiourea.
    Ethylene thiourea 96-45-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U117
    Ethyl ether.
    Ethyl ether 60-29-7 0.12 160
     
    U118
    Ethyl methacrylate.
    Ethyl methacrylate 97-63-2 0.14 160
     
    U119
    Ethyl methane sulfonate.
    Ethyl methane sulfonate 62-50-0 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U120
    Fluoranthene.
    Fluoranthene 206-44-0 0.068 3.4
     
    U121
    Trichloromonofluoromethane.
    Trichloromonofluoromethane 75-69-4 0.020 30
     
    U122
    Formaldehyde.
    Formaldehyde 50-00-0 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U123
    Formic acid.
    Formic acid 64-18-6 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     

     
    940
    U124
    Furan.
    Furan 110-00-9 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U125
    Furfural.
    Furfural 98-01-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U126
    Glycidylaldehyde.
    Glycidylaldehyde 765-34-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U127
    Hexachlorobenzene.
    Hexachlorobenzene 118-74-1 0.055 10
     
    U128
    Hexachlorobutadiene.
    Hexachlorobutadiene 87-68-3 0.055 5.6
     
    U129
    Lindane.
    α
    -BHC
    319-84-6 0.00014 0.066
    β
    -BHC
    319-85-7 0.00014 0.066
    δ
    -BHC
    319-86-8 0.023 0.066
    γ
    -BHC (Lindane)
    58-89-9 0.0017 0.066
     
    U130
    Hexachlorocyclopentadiene.
    Hexachlorocyclopentadiene 77-47-4 0.057 2.4
     
    U131
    Hexachloroethane.
    Hexachloroethane 67-72-1 0.055 30
     

     
    941
    U132
    Hexachlorophene.
    Hexachlorophene 70-30-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U133
    Hydrazine.
    Hydrazine 302-01-2 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    U134
    Hydrogen fluoride.
    Fluoride (measured in
    wastewaters only)
    16964-48-8 35 ADGAS fb
    NEUTR; or
    NEUTR
     
    U135
    Hydrogen sulfide.
    Hydrogen sulfide 7783-06-4 CHOXD; CHRED;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    U136
    Cacodylic acid.
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
     
    U137
    Indeno(1,2,3-c,d)pyrene.
    Indeno(1,2,3-c,d)pyrene 193-39-5 0.0055 3.4
     
    U138
    Iodomethane.
    Iodomethane 74-88-4 0.19 65
     
    U140
    Isobutyl alcohol.
    Isobutyl alcohol 78-83-1 5.6 170
     
    U141
    Isosafrole.
    Isosafrole 120-58-1 0.081 2.6
     

     
    942
    U142
    Kepone.
    Kepone 143-50-8 0.0011 0.13
     
    U143
    Lasiocarpine.
    Lasiocarpine 303-34-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U144
    Lead acetate.
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    U145
    Lead phosphate.
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    U146
    Lead subacetate.
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
     
    U147
    Maleic anhydride.
    Maleic anhydride 108-31-6 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U148
    Maleic hydrazide.
    Maleic hydrazide 123-33-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U149
    Malononitrile.
    Malononitrile 109-77-3 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST

     
    943
     
    U150
    Melphalan.
    Melphalan 148-82-3 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U151
    U151 (mercury) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.
    Mercury 7439-97-6 NA RMERC
     
    U151
    U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are
    residues from RMERC only.
    Mercury 7439-97-6 NA 0.20 mg/lmg/
     
    TCLP
     
    U151
    U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are not
    residues from RMERC only.
    Mercury 7439-97-6 NA 0.025 mg/lmg/
     
    TCLP
     
    U151
    All U151 (mercury) wastewater.
    Mercury 7439-97-6 0.15 NA
     
    U151
    Elemental Mercury Contaminated with Radioactive Materials.
    Mercury 7439-97-6 NA AMLGM
     
    U152
    Methacrylonitrile.
    Methacrylonitrile 126-98-7 0.24 84
     
    U153
    Methanethiol.
    Methanethiol 74-93-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     

     
    944
    U154
    Methanol.
    Methanol 67-56-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
    Methanol; alternate
    6
    set of
    standards for both wastewaters
    and nonwastewaters
    67-56-1 5.6 0.75 mg/lmg/
     
    TCLP
     
    U155
    Methapyrilene.
    Methapyrilene 91-80-5 0.081 1.5
     
    U156
    Methyl chlorocarbonate.
    Methyl chlorocarbonate 79-22-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U157
    3-Methylcholanthrene.
    3-Methylcholanthrene 56-49-5 0.0055 15
     
    U158
    4,4'-Methylene bis(2-chloroaniline).
    4,4'-Methylene bis(2-chloro-
    aniline)
    101-14-4 0.50 30
     
    U159
    Methyl ethyl ketone.
    Methyl ethyl ketone 78-93-3 0.28 36
     
    U160
    Methyl ethyl ketone peroxide.
    Methyl ethyl ketone peroxide 1338-23-4 CHOXD; CHRED;
    CARBN; BIODG;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    U161
    Methyl isobutyl ketone.
    Methyl isobutyl ketone 108-10-1 0.14 33
     

     
    945
    U162
    Methyl methacrylate.
    Methyl methacrylate 80-62-6 0.14 160
     
    U163
    N-Methyl-N'-nitro-N-nitrosoguanidine.
    N-Methyl-N'-nitro-N-nitroso-
    guanidine
    70-25-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U164
    Methylthiouracil.
    Methylthiouracil 56-04-2 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U165
    Naphthalene.
    Naphthalene 91-20-3 0.059 5.6
     
    U166
    1,4-Naphthoquinone.
    1,4-Naphthoquinone 130-15-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U167
    1-Naphthylamine.
    1-Naphthylamine 134-32-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U168
    2-Naphthylamine.
    2-Naphthylamine 91-59-8 0.52 CMBST
     
    U169
    Nitrobenzene.
    Nitrobenzene 98-95-3 0.068 14
     

     
    946
    U170
    p-Nitrophenol.
    p-Nitrophenol 100-02-7 0.12 29
     
    U171
    2-Nitropropane.
    2-Nitropropane 79-46-9 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U172
    N-Nitrosodi-n-butylamine.
    N-Nitrosodi-n-butylamine 924-16-3 0.40 17
     
    U173
    N-Nitrosodiethanolamine.
    N-Nitrosodiethanolamine 1116-54-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U174
    N-Nitrosodiethylamine.
    N-Nitrosodiethylamine 55-18-5 0.40 28
     
    U176
    N-Nitroso-N-ethylurea.
    N-Nitroso-N-ethylurea 759-73-9 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U177
    N-Nitroso-N-methylurea.
    N-Nitroso-N-methylurea 684-93-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U178
    N-Nitroso-N-methylurethane.
    N-Nitroso-N-methylurethane 615-53-2 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST

     
    947
     
    U179
    N-Nitrosopiperidine.
    N-Nitrosopiperidine 100-75-4 0.013 35
     
    U180
    N-Nitrosopyrrolidine.
    N-Nitrosopyrrolidine 930-55-2 0.013 35
     
    U181
    5-Nitro-o-toluidine.
    5-Nitro-o-toluidine 99-55-8 0.32 28
     
    U182
    Paraldehyde.
    Paraldehyde 123-63-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U183
    Pentachlorobenzene.
    Pentachlorobenzene 608-93-5 0.055 10
     
    U184
    Pentachloroethane.
    Pentachloroethane 76-01-7 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
    Pentachloroethane; alternate
    6
     
    standards for both wastewaters
    and nonwastewaters
    76-01-7 0.055 6.0
     
    U185
    Pentachloronitrobenzene.
    Pentachloronitrobenzene 82-68-8 0.055 4.8
     
    U186
    1,3-Pentadiene.
    1,3-Pentadiene 504-60-9 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     

     
    948
    U187
    Phenacetin.
    Phenacetin 62-44-2 0.081 16
     
    U188
    Phenol.
    Phenol 108-95-2 0.039 6.2
     
    U189
    Phosphorus sulfide.
    Phosphorus sulfide 1314-80-3 CHOXD; CHRED;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    U190
    Phthalic anhydride.
    Phthalic anhydride (measured as
    Phthalic acid or Terephthalic
    acid)
    100-21-0 0.055 28
    Phthalic anhydride (measured as
    Phthalic acid or Terephthalic
    acid)
    85-44-9 0.055 28
     
    U191
    2-Picoline.
    2-Picoline 109-06-8 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U192
    Pronamide.
    Pronamide 23950-58-5 0.093 1.5
     
    U193
    1,3-Propane sultone.
    1,3-Propane sultone 1120-71-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U194
    n-Propylamine.
    n-Propylamine 107-10-8 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST

     
    949
     
    U196
    Pyridine.
    Pyridine 110-86-1 0.014 16
     
    U197
    p-Benzoquinone.
    p-Benzoquinone 106-51-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U200
    Reserpine.
    Reserpine 50-55-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U201
    Resorcinol
    Resorcinol. 108-46-3 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U202
    Saccharin and salts.
    Saccharin 81-07-2 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U203
    Safrole.
    Safrole 94-59-7 0.081 22
     
    U204
    Selenium dioxide.
    Selenium 7782-49-2 0.82 5.7 mg/lmg/
     
    TCLP
     
    U205
    Selenium sulfide.
    Selenium 7782-49-2 0.82 5.7 mg/lmg/
     
    TCLP

     
    950
     
    U206
    Streptozotocin.
    Streptozotocin 18883-66-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U207
    1,2,4,5-Tetrachlorobenzene.
    1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14
     
    U208
    1,1,1,2-Tetrachloroethane.
    1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0
     
    U209
    1,1,2,2-Tetrachloroethane.
    1,1,2,2-Tetrachloroethane 79-34-5 0.057 6.0
     
    U210
    Tetrachloroethylene.
    Tetrachloroethylene 127-18-4 0.056 6.0
     
    U211
    Carbon tetrachloride.
    Carbon tetrachloride 56-23-5 0.057 6.0
     
    U213
    Tetrahydrofuran.
    Tetrahydrofuran 109-99-9 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U214
    Thallium (I) acetate.
    Thallium (measured in
    wastewaters only)
    7440-28-0 1.4 RTHRM; or
    STABL
     
    U215
    Thallium (I) carbonate.
    Thallium (measured in
    wastewaters only)
    7440-28-0 1.4 RTHRM; or
    STABL
     

     
    951
    U216
    Thallium (I) chloride.
    Thallium (measured in
    wastewaters only)
    7440-28-0 1.4 RTHRM; or
    STABL
     
    U217
    Thallium (I) nitrate.
    Thallium (measured in
    wastewaters only)
    7440-28-0 1.4 RTHRM; or
    STABL
     
    U218
    Thioacetamide.
    Thioacetamide 62-55-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U219
    Thiourea.
    Thiourea 62-56-6 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U220
    Toluene.
    Toluene 108-88-3 0.080 10
     
    U221
    Toluenediamine.
    Toluenediamine 25376-45-8 CARBN; or
    CMBST
    CMBST
     
    U222
    o-Toluidine hydrochloride.
    o-Toluidine hydrochloride 636-21-5 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U223
    Toluene diisocyanate.
    Toluene diisocyanate 26471-62-5 CARBN; or
    CMBST
    CMBST
     

     
    952
    U225
    Bromoform (Tribromomethane).
    Bromoform (Tribromomethane) 75-25-2 0.63 15
     
    U226
    1,1,1-Trichloroethane.
    1,1,1-Trichloroethane 71-55-6 0.054 6.0
     
    U227
    1,1,2-Trichloroethane.
    1,1,2-Trichloroethane 79-00-5 0.054 6.0
     
    U228
    Trichloroethylene.
    Trichloroethylene 79-01-6 0.054 6.0
     
    U234
    1,3,5-Trinitrobenzene.
    1,3,5-Trinitrobenzene 99-35-4 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U235
    tris-(2,3-Dibromopropyl)-phosphate.
    tris-(2,3-Dibromopropyl)-
    phosphate
    126-72-7 0.11 0.10
     
    U236
    Trypan Blue.
    Trypan Blue 72-57-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U237
    Uracil mustard.
    Uracil mustard 66-75-1 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     

     
    953
    U238
    Urethane (Ethyl carbamate).
    Urethane (Ethyl carbamate) 51-79-6 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U239
    Xylenes.
    Xylenes-mixed isomers
    (sum of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30
     
    U240
    2,4-D (2,4-Dichlorophenoxyacetic acid).
    2,4-D (2,4-Dichloro-
    phenoxyacetic acid)
    94-75-7 0.72 10
    2,4-D (2,4-Dichloro-
    phenoxyacetic acid) salts and
    esters
    NA (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U243
    Hexachloropropylene.
    Hexachloropropylene 1888-71-7 0.035 30
     
    U244
    Thiram.
    Thiram 137-26-8 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U246
    Cyanogen bromide.
    Cyanogen bromide 506-68-3 CHOXD;
    WETOX; or
    CMBST
    CHOXD;
    WETOX; or
    CMBST
     
    U247
    Methoxychlor.
    Methoxychlor 72-43-5 0.25 0.18
     

     
    954
    U248
    Warfarin, & salts, when present at concentrations of 0.3 percent or less.
    Warfarin 81-81-2 (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
     
    U249
    Zinc phosphide, Zn3P2, when present at concentrations of 10 percent or less.
    Zinc Phosphide 1314-84-7 CHOXD; CHRED;
    or CMBST
    CHOXD; CHRED;
    or CMBST
     
    U271
    Benomyl.
    Benomyl 17804-35-2 0.056 1.4
     
    U278
    Bendiocarb.
    Bendiocarb 22781-23-3 0.056 1.4
     
    U279
    Carbaryl.
    Carbaryl 63-25-2 0.006 0.14
     
    U280
    Barban.
    Barban 101-27-9 0.056 1.4
     
    U328
    o-Toluidine.
    o-Toluidine 95-53-4 CMBST; or
    CHOXD fb
    (BIODG or
    CARBN); or
    BIODG fb
    CARBN
    CMBST
     
    U353
    p-Toluidine.
    p-Toluidine 106-49-0 CMBST; or
    CHOXD fb
    (BIODG or
    CARBN); or
    BIODG fb
    CARBN
    CMBST
     

     
    955
    U359
    2-Ethoxyethanol.
    2-Ethoxyethanol 110-80-5 CMBST; or
    CHOXD fb
    (BIODG or
    CARBN); or
    BIODG fb
    CARBN
    CMBST
     
    U364
    Bendiocarb phenol.
    10
     
    Bendiocarb phenol 22961-82-6 0.056 1.4
     
    U367
    Carbofuran phenol.
    Carbofuran phenol 1563-38-8 0.056 1.4
     
    U372
    Carbendazim.
    Carbendazim 10605-21-7 0.056 1.4
     
    U373
    Propham.
    Propham 122-42-9 0.056 1.4
     
    U387
    Prosulfocarb.
    Prosulfocarb 52888-80-9 0.042 1.4
     
    U389
    Triallate.
    Triallate 2303-17-5 0.042 1.4
     
    U394
    A2213.
    10
     
    A2213 30558-43-1 0.042 1.4
     
    U395
    Diethylene glycol, dicarbamate.
    10
     
    Diethylene glycol, dicarbamate 5952-26-1 0.056 1.4
     
    U404
    Triethylamine.
    Triethylamine 101-44-8 0.081 1.5
     

     
    956
    U409
    Thiophanate-methyl.
    Thiophanate-methyl 23564-05-8 0.056 1.4
     
    U410
    Thiodicarb.
    Thiodicarb 59669-26-0 0.019 1.4
     
    U411
    Propoxur.
    Propoxur 114-26-1 0.056 1.4
     
    Notes:
     
    1 The waste descriptions provided in this table do not replace waste descriptions in 35 Ill.
    Adm. Code 721. Descriptions of Treatment or Regulatory Subcategories are provided, as
    needed, to distinguish between applicability of different standards.
     
    2 CAS means Chemical Abstract Services. When the waste code or regulated constituents
    are described as a combination of a chemical with its salts or esters, the CAS number is
    given for the parent compound only.
     
    3 Concentration standards for wastewaters are expressed in mg/lmg/
    and are based on
    analysis of composite samples.
     
    4 All treatment standards expressed as a Technology Code or combination of Technology
    Codes are explained in detail in Table C of this Part, “Technology Codes and
    Descriptions of Technology-Based Standards.” “fb” inserted between waste codes
    denotes “followed by,” so that the first-listed treatment is followed by the second-listed
    treatment. A semicolon (;) separates alternative treatment schemes.
     
    5 Except for Metals (EP or TCLP) and Cyanides (Total and Amenable), the nonwastewater
    treatment standards expressed as a concentration were established, in part, based on
    incineration in units operated in accordance with the technical requirements of Subpart O
    of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725 or based on combustion
    in fuel substitution units operating in accordance with applicable technical requirements.
    A facility may comply with these treatment standards according to provisions in Section
    728.140(d). All concentration standards for nonwastewaters are based on analysis of
    grab samples.
     
    6 Where an alternate treatment standard or set of alternate standards has been indicated, a
    facility may comply with this alternate standard, but only for the Treatment or Regulatory
    Subcategory or physical form (i.e., wastewater or nonwastewater) specified for that
    alternate standard.
     
    7 Both Cyanides (Total) and Cyanides (Amenable) for nonwastewaters are to be analyzed

     
    957
    using Method 9010 9010C or 9012 9012B, found in “Test Methods for Evaluating Solid
    Waste, Physical or Chemical Methods,” USEPA Publication publication number
    EPA530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(a),
    with a sample size of 10 grams and a distillation time of one hour and 15 minutes.
     
    8 These wastes, when rendered non-hazardous and then subsequently managed in CWA or
    CWA-equivalent systems, are not subject to treatment standards. (See Section
    728.101(c)(3) and (c)(4).)
     
    9 These wastes, when rendered non-hazardous and then subsequently injected in a Class I
    SDWA well, are not subject to treatment standards. (See 35 Ill. Adm. Code 738.101(d).)
     
    10 The treatment standard for this waste may be satisfied by either meeting the constituent
    concentrations in the table in this Section or by treating the waste by the specified
    technologies: combustion, as defined by the technology code CMBST at Table C, for
    nonwastewaters; and biodegradation, as defined by the technology code BIODG; carbon
    adsorption, as defined by the technology code CARBN; chemical oxidation, as defined by
    the technology code CHOXD; or combustion, as defined as technology code CMBST, at
    Table C, for wastewaters.
     
    11 For these wastes, the definition of CMBST is limited to any of the following that have
    obtained a determination of equivalent treatment under Section 728.142(b): (1)
    combustion units operating under 35 Ill. Adm. Code 726, (2) combustion units permitted
    under Subpart O of 35 Ill. Adm. Code 724, or (3) combustion units operating under
    Subpart O of 35 Ill. Adm. Code 725.
     
    12 Disposal of USEPA hazardous waste number K175 waste that has complied with all
    applicable Section 728.140 treatment standards must also be macroencapsulated in
    accordance with Table F of this Part, unless the waste is placed in either of the following
    types of facilities:
     
    a) A RCRA Subtitle C monofill containing only K175 wastes that meet all
    applicable 40 CFR 268.40 treatment standards; or
     
    b) A dedicated RCRA Subtitle C landfill cell in which all other wastes being co-
    disposed are at pH
    6.0.
     
    BOARD NOTE: Derived from table to 40 CFR 268.40 (2002) (2005).
     
    NA means not applicable.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    958
    Section 728.Table U Universal Treatment Standards (UTS)
     
    Regulated Constituent-
    Common Name CAS
    1
    No.
    Wastewater
    Standard
    Concentration (in
    mg/lmg/
    2
    )
    Nonwastewater
    Standard
    Concentration (in
    mg/kg
    3
    unless
    noted as
    “mg/lmg/
    TCLP”)
    Acenaphthylene 208-96-8 0.059 3.4
    Acenaphthene 83-32-9 0.059 3.4
    Acetone 67-64-1 0.28 160
    Acetonitrile 75-05-8 5.6 38
    Acetophenone 96-86-2 0.010 9.7
    2-Acetylaminofluorene 53-96-3 0.059 140
    Acrolein 107-02-8 0.29 NA
    Acrylamide 79-06-1 19 23
    Acrylonitrile 107-13-1 0.24 84
    Aldicarb sulfone
    6
    1646-88-4 0.056 0.28
    Aldrin 309-00-2 0.021 0.066
    4-Aminobiphenyl 92-67-1 0.13 NA
    Aniline 62-53-3 0.81 14
    o-Anisidine (2-methoxy-
    aniline)
    90–04–0 0.010 0.66
    Anthracene 120-12-7 0.059 3.4
    Aramite 140-57-8 0.36 NA
    α
    -BHC
    319-84-6 0.00014 0.066
    β
    -BHC
    319-85-7 0.00014 0.066
    δ
    -BHC
    319-86-8 0.023 0.066
    γ
    -BHC
    58-89-9 0.0017 0.066
    Barban
    6
    101-27-9 0.056 1.4
    Bendiocarb
    6
    22781-23-3 0.056 1.4
    Benomyl
    6
    17804-35-2 0.056 1.4
    Benz(a)anthracene 56-55-3 0.059 3.4
    Benzal chloride 98-87-3 0.055 6.0
    Benzene 71-43-2 0.14 10
    Benzo(b)fluoranthene
    (difficult to distinguish from
    benzo(k)fluoranthene)
    205-99-2 0.11 6.8
    Benzo(k)fluoranthene
    (difficult to distinguish from
    benzo(b)fluoranthene)
    207-08-9 0.11 6.8
    Benzo(g,h,i)perylene 191-24-2 0.0055 1.8
    Benzo(a)pyrene 50-32-8 0.061 3.4
    Bromodichloromethane 75-27-4 0.35 15
    Methyl bromide (Bromo-
    methane)
    74-83-9 0.11 15

     
    959
    4-Bromophenyl phenyl ether 101-55-3 0.055 15
    n-Butyl alcohol 71-36-3 5.6 2.6
    Butylate
    6
    2008-41-5 0.042 1.4
    Butyl benzyl phthalate 85-68-7 0.017 28
    2-sec-Butyl-4,6-dinitrophenol
    (Dinoseb)
    88-85-7 0.066 2.5
    Carbaryl
    6
    63-25-2 0.006 0.14
    Carbenzadim
    6
    10605-21-7 0.056 1.4
    Carbofuran
    6
    1563-66-2 0.006 0.14
    Carbofuran phenol
    6
    1563-38-8 0.056 1.4
    Carbon disulfide 75-15-0 3.8 4.8 mg/lmg/
     
    TCLP
    Carbon tetrachloride 56-23-5 0.057 6.0
    Carbosulfan
    6
    55285-14-8 0.028 1.4
    Chlordane (
    α
    and
    γ
    isomers)
    57-74-9 0.0033 0.26
    p-Chloroaniline 106-47-8 0.46 16
    Chlorobenzene 108-90-7 0.057 6.0
    Chlorobenzilate 510-15-6 0.10 NA
    2-Chloro-1,3-butadiene 126-99-8 0.057 0.28
    p-Chloro-m-cresol 59-50-7 0.018 14
    Chlorodibromomethane 124-48-1 0.057 15
    Chloroethane 75-00-3 0.27 6.0
    bis(2-Chloroethoxy)methane 111-91-1 0.036 7.2
    bis(2-Chloroethyl)ether 111-44-4 0.033 6.0
    2-Chloroethyl vinyl ether 110-75-8 0.062 NA
    Chloroform 67-66-3 0.046 6.0
    bis(2-Chloroisopropyl)ether 39638-32-9 0.055 7.2
    Chloromethane (Methyl
    chloride)
    74-87-3 0.19 30
    2-Chloronaphthalene 91-58-7 0.055 5.6
    2-Chlorophenol 95-57-8 0.044 5.7
    3-Chloropropylene 107-05-1 0.036 30
    Chrysene 218-01-9 0.059 3.4
    p-Cresidine 120–71–8 0.010 0.66
    o-Cresol 95-48-7 0.11 5.6
    m-Cresol (difficult to
    distinguish from p-cresol)
    108-39-4 0.77 5.6
    p-Cresol (difficult to
    distinguish from m-cresol)
    106-44-5 0.77 5.6
    m-Cumenyl methyl-
    carbamate
    6
     
    64-00-6 0.056 1.4
    Cyclohexanone 108-94-1 0.36 0.75 mg/lmg/
     
    TCLP
    o,p'-DDD 53-19-0 0.023 0.087
    p,p'-DDD 72-54-8 0.023 0.087
    o,p'-DDE 3424-82-6 0.031 0.087

     
    960
    p,p'-DDE 72-55-9 0.031 0.087
    o,p'-DDT 789-02-6 0.0039 0.087
    p,p'-DDT 50-29-3 0.0039 0.087
    Dibenz(a,h)anthracene 53-70-3 0.055 8.2
    Dibenz(a,e)pyrene 192-65-4 0.061 NA
    1,2-Dibromo-3-chloro-
    propane
    96-12-8 0.11 15
    1,2-Dibromoethane/Ethylene
    dibromide
    106-93-4 0.028 15
    Dibromomethane 74-95-3 0.11 15
    m-Dichlorobenzene 541-73-1 0.036 6.0
    o-Dichlorobenzene 95-50-1 0.088 6.0
    p-Dichlorobenzene 106-46-7 0.090 6.0
    Dichlorodifluoromethane 75-71-8 0.23 7.2
    1,1-Dichloroethane 75-34-3 0.059 6.0
    1,2-Dichloroethane 107-06-2 0.21 6.0
    1,1-Dichloroethylene 75-35-4 0.025 6.0
    trans-1,2-Dichloroethylene 156-60-5 0.054 30
    2,4-Dichlorophenol 120-83-2 0.044 14
    2,6-Dichlorophenol 87-65-0 0.044 14
    2,4-Dichlorophenoxyacetic
    acid/2,4-D
    94-75-7 0.72 10
    1,2-Dichloropropane 78-87-5 0.85 18
    cis-1,3-Dichloropropylene 10061-01-5 0.036 18
    trans-1,3-Dichloropropylene 10061-02-6 0.036 18
    Dieldrin 60-57-1 0.017 0.13
    Diethyl phthalate 84-66-2 0.20 28
    p-Dimethylaminoazobenzene 60-11-7 0.13 NA
    2,4-Dimethylaniline (2,4-
    xylidine)
    95–68–1 0.010 0.66
    2,4-Dimethyl phenol 105-67-9 0.036 14
    Dimethyl phthalate 131-11-3 0.047 28
    Di-n-butyl phthalate 84-74-2 0.057 28
    1,4-Dinitrobenzene 100-25-4 0.32 2.3
    4,6-Dinitro-o-cresol 534-52-1 0.28 160
    2,4-Dinitrophenol 51-28-5 0.12 160
    2,4-Dinitrotoluene 121-14-2 0.32 140
    2,6-Dinitrotoluene 606-20-2 0.55 28
    Di-n-octyl phthalate 117-84-0 0.017 28
    Di-n-propylnitrosamine 621-64-7 0.40 14
    1,4-Dioxane 123-91-1 12.0 170
    Diphenylamine (difficult to
    distinguish from
    diphenylnitrosamine)
    122-39-4 0.92 13

     
    961
    Diphenylnitrosamine
    (difficult to distinguish from
    diphenylamine)
    86-30-6 0.92 13
    1,2-Diphenylhydrazine 122-66-7 0.087 NA
    Disulfoton 298-04-4 0.017 6.2
    Dithiocarbamates (total)
    6
    137-30-4 0.028 28
    Endosulfan I 959-98-8 0.023 0.066
    Endosulfan II 33213-65-9 0.029 0.13
    Endosulfan sulfate 1031-07-8 0.029 0.13
    Endrin 72-20-8 0.0028 0.13
    Endrin aldehyde 7421-93-4 0.025 0.13
    EPTC
    6
    759-94-4 0.042 1.4
    Ethyl acetate 141-78-6 0.34 33
    Ethyl benzene 100-41-4 0.057 10
    Ethyl cyanide
    (Propanenitrile)
    107-12-0 0.24 360
    Ethylene oxide 75-21-8 0.12 NA
    Ethyl ether 60-29-7 0.12 160
    bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28
    Ethyl methacrylate 97-63-2 0.14 160
    Famphur 52-85-7 0.017 15
    Fluoranthene 206-44-0 0.068 3.4
    Fluorene 86-73-7 0.059 3.4
    Formetanate hydrochloride
    6
    23422-53-9 0.056 1.4
    Heptachlor 76-44-8 0.0012 0.066
    1,2,3,4,6,7,8-Heptachloro-
    dibenzo-p-dioxin
    (1,2,3,4,6,7,8-HpCDD)
    35822-46-9 0.000035 0.0025
    1,2,3,4,6,7,8-Heptachloro-
    dibenzofuran (1,2,3,4,6,7,8-
    HpCDF)
    67562-39-4 0.000035 0.0025
    1,2,3,4,7,8,9-Heptachloro-
    dibenzofuran (1,2,3,4,7,8,9-
    HpCDF)
    55673-89-7 0.000035 0.0025
    Heptachlor epoxide 1024-57-3 0.016 0.066
    Hexachlorobenzene 118-74-1 0.055 10
    Hexachlorobutadiene 87-68-3 0.055 5.6
    Hexachlorocyclopentadiene 77-47-4 0.057 2.4
    HxCDDs (All Hexachloro-
    dibenzo-p-dioxins)
    NA 0.000063 0.001
    HxCDFs (All Hexachloro-
    dibenzofurans)
    55684-94-1 0.000063 0.001
    Hexachloroethane 67-72-1 0.055 30
    Hexachloropropylene 1888-71-7 0.035 30
    Indeno (1,2,3-c,d) pyrene 193-39-5 0.0055 3.4
    Iodomethane 74-88-4 0.19 65

     
    962
    Isobutyl alcohol 78-83-1 5.6 170
    Isodrin 465-73-6 0.021 0.066
    Isosafrole 120-58-1 0.081 2.6
    Kepone 143-50-0 0.0011 0.13
    Methacrylonitrile 126-98-7 0.24 84
    Methanol 67-56-1 5.6 0.75 mg/lmg/
     
    TCLP
    Methapyrilene 91-80-5 0.081 1.5
    Methiocarb
    6
    2032-65-7 0.056 1.4
    Methomyl
    6
    16752-77-5 0.028 0.14
    Methoxychlor 72-43-5 0.25 0.18
    3-Methylcholanthrene 56-49-5 0.0055 15
    4,4-Methylene bis(2-chloro-
    aniline)
    101-14-4 0.50 30
    Methylene chloride 75-09-2 0.089 30
    Methyl ethyl ketone 78-93-3 0.28 36
    Methyl isobutyl ketone 108-10-1 0.14 33
    Methyl methacrylate 80-62-6 0.14 160
    Methyl methansulfonate 66-27-3 0.018 NA
    Methyl parathion 298-00-0 0.014 4.6
    Metolcarb
    6
    1129-41-5 0.056 1.4
    Mexacarbate
    6
    315-18-4 0.056 1.4
    Molinate
    6
    2212-67-1 0.042 1.4
    Naphthalene 91-20-3 0.059 5.6
    2-Naphthylamine 91-59-8 0.52 NA
    o-Nitroaniline 88-74-4 0.27 14
    p-Nitroaniline 100-01-6 0.028 28
    Nitrobenzene 98-95-3 0.068 14
    5-Nitro-o-toluidine 99-55-8 0.32 28
    o-Nitrophenol 88-75-5 0.028 13
    p-Nitrophenol 100-02-7 0.12 29
    N-Nitrosodiethylamine 55-18-5 0.40 28
    N-Nitrosodimethylamine 62-75-9 0.40 2.3
    N-Nitroso-di-n-butylamine 924-16-3 0.40 17
    N-Nitrosomethylethylamine 10595-95-6 0.40 2.3
    N-Nitrosomorpholine 59-89-2 0.40 2.3
    N-Nitrosopiperidine 100-75-4 0.013 35
    N-Nitrosopyrrolidine 930-55-2 0.013 35
    1,2,3,4,6,7,8,9-Octachloro-
    dibenzo-p-dioxin
    (1,2,3,4,6,7,8,9-OCDD)
    3268-87-9 0.000063 0.005
    1,2,3,4,6,7,8,9-Octachloro-
    dibenzofuran (1,2,3,4,6,7,8,9-
    OCDF)
    39001-02-0 0.000063 0.005
    Oxamyl
    6
    23135-22-0 0.056 0.28
    Parathion 56-38-2 0.014 4.6

     
    963
    Total PCBs (sum of all PCB
    isomers, or all Aroclors)
    8
    1336-36-3 0.10 10
    Pebulate
    6
    1114-71-2 0.042 1.4
    Pentachlorobenzene 608-93-5 0.055 10
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    36088-22-9 0.000063 0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    30402-15-4 0.000035 0.001
    Pentachloroethane 76-01-7 0.055 6.0
    Pentachloronitrobenzene 82-68-8 0.055 4.8
    Pentachlorophenol 87-86-5 0.089 7.4
    Phenacetin 62-44-2 0.081 16
    Phenanthrene 85-01-8 0.059 5.6
    Phenol 108-95-2 0.039 6.2
    1,3-Phenylenediamine 108–45–2 0.010 0.66
    Phorate 298-02-2 0.021 4.6
    Phthalic acid 100-21-0 0.055 28
    Phthalic anhydride 85-44-9 0.055 28
    Physostigmine
    6
    57-47-6 0.056 1.4
    Physostigmine salicylate
    6
    57-64-7 0.056 1.4
    Promecarb
    6
    2631-37-0 0.056 1.4
    Pronamide 23950-58-5 0.093 1.5
    Propham
    6
    122-42-9 0.056 1.4
    Propoxur
    6
    114-26-1 0.056 1.4
    Prosulfocarb
    6
    52888-80-9 0.042 1.4
    Pyrene 129-00-0 0.067 8.2
    Pyridine 110-86-1 0.014 16
    Safrole 94-59-7 0.081 22
    Silvex (2,4,5-TP) 93-72-1 0.72 7.9
    1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    41903-57-5 0.000063 0.001
    TCDFs (All Tetrachloro-
    dibenzofurans)
    55722-27-5 0.000063 0.001
    1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0
    1,1,2,2-Tetrachloroethane 79-34-5 0.057 6.0
    Tetrachloroethylene 127-18-4 0.056 6.0
    2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4
    Thiodicarb
    6
    59669-26-0 0.019 1.4
    Thiophanate-methyl
    6
    23564-05-8 0.056 1.4
    Toluene 108-88-3 0.080 10
    Toxaphene 8001-35-2 0.0095 2.6
    Triallate
    6
    2303-17-5 0.042 1.4
    Tribromomethane
    (Bromoform)
    75-25-2 0.63 15
    1,2,4-Trichlorobenzene 120-82-1 0.055 19

     
    964
    1,1,1-Trichloroethane 71-55-6 0.054 6.0
    1,1,2-Trichloroethane 79-00-5 0.054 6.0
    Trichloroethylene 79-01-6 0.054 6.0
    Trichloromonofluoromethane 75-69-4 0.020 30
    2,4,5-Trichlorophenol 95-95-4 0.18 7.4
    2,4,6-Trichlorophenol 88-06-2 0.035 7.4
    2,4,5-Trichlorophenoxyacetic
    acid/2,4,5-T
    93-76-5 0.72 7.9
    1,2,3-Trichloropropane 96-18-4 0.85 30
    1,1,2-Trichloro-1,2,2-
    trifluoroethane
    76-13-1 0.057 30
    Triethylamine
    6
    101-44-8 0.081 1.5
    tris-(2,3-Dibromopropyl)
    phosphate
    126-72-7 0.11 0.10
    Vernolate
    6
    1929-77-7 0.042 1.4
    Vinyl chloride 75-01-4 0.27 6.0
    Xylenes-mixed isomers (sum
    of o-, m-, and p-xylene
    concentrations)
    1330-20-7 0.32 30
    Antimony 7440-36-0 1.9 1.15 mg/lmg/
     
    TCLP
    Arsenic 7440-38-2 1.4 5.0 mg/lmg/
     
    TCLP
    Barium 7440-39-3 1.2 21 mg/lmg/
    TCLP
    Beryllium 7440-41-7 0.82 1.22 mg/lmg/
     
    TCLP
    Cadmium 7440-43-9 0.69 0.11 mg/lmg/
     
    TCLP
    Chromium (Total) 7440-47-3 2.77 0.60 mg/lmg/
     
    TCLP
    Cyanides (Total)
    4
    57-12-5 1.2 590
    Cyanides (Amenable)
    4
    57-12-5 0.86 30
    Fluoride
    5
    16984-48-8 35 NA
    Lead 7439-92-1 0.69 0.75 mg/lmg/
     
    TCLP
    Mercury-Nonwastewater
    from Retort
    7439-97-6 NA 0.20 mg/lmg/
     
    TCLP
    Mercury-All Others 7439-97-6 0.15 0.025 mg/lmg/
     
    TCLP
    Nickel 7440-02-0 3.98 11 mg/lmg/
    TCLP
    Selenium
    7
    7782-49-2 0.82 5.7 mg/lmg/
     
    TCLP
    Silver 7440-22-4 0.43 0.14 mg/lmg/
     
    TCLP
    Sulfide 18496-25-8 14 NA

     
    965
    Thallium 7440-28-0 1.4 0.20 mg/lmg/
     
    TCLP
    Vanadium
    5
    7440-62-2 4.3 1.6 mg/lmg/
     
    TCLP
    Zinc
    5
    7440-66-6 2.61 4.3 mg/lmg/
     
    TCLP
     
    1 CAS means Chemical Abstract Services. When the waste code or regulated constituents
    are described as a combination of a chemical with its salts or esters, the CAS number is
    given for the parent compound only.
     
    2 Concentration standards for wastewaters are expressed in mg/l mg/
    are based on
    analysis of composite samples.
     
    3 Except for metals (EP or TCLP) and cyanides (total and amenable), the nonwastewater
    treatment standards expressed as a concentration were established, in part, based on
    incineration in units operated in accordance with the technical requirements of Subpart O
    of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725 or on combustion in fuel
    substitution units operating in accordance with applicable technical requirements. A
    facility may comply with these treatment standards according to provisions in Section
    728.140(d). All concentration standards for nonwastewaters are based on analysis of
    grab samples.
     
    4 Both Cyanides (Total) and Cyanides (Amenable) for nonwastewaters are to be analyzed
    using Method 9010 9010C or 9012 9012B, found in “Test Methods for Evaluating Solid
    Waste, Physical/Chemical Methods,” USEPA Publication publication number EPA-
    530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111 720.111(a), with a
    sample size of 10 grams and a distillation time of one hour and 15 minutes.
     
    5 These constituents are not “underlying hazardous constituents” in characteristic wastes,
    according to the definition at Section 728.102(i).
     
    6 This footnote corresponds with footnote 6 to the table to 40 CFR 268.48(a), which has
    already expired by its own terms. This statement maintains structural consistency with
    the corresponding federal regulations.
     
    7 This constituent is not an underlying hazardous constituent, as defined at Section
    728.102(i), because its UTS level is greater than its TC level. Thus, a treated selenium
    waste would always be characteristically hazardous unless it is treated to below its
    characteristic level.
     
    8 This standard is temporarily deferred for soil exhibiting a hazardous characteristic due to
    USEPA hazardous waste numbers D004 through D011 only.
     
    Note: NA means not applicable.
     

     
    966
    BOARD NOTE: Derived from table to 40 CFR 268.48(a) (2002) (2005).
     
    (Source: Amended at 27 Ill. Reg. 13045, effective July 17, 2003)
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER d: UNDERGROUND INJECTION CONTROL AND
    UNDERGROUND STORAGE TANK PROGRAMS
     
    PART 738
    HAZARDOUS WASTE INJECTION RESTRICTIONS
     
    SUBPART A: GENERAL
    Section
    738.101 Purpose, Scope, and Applicability
    738.102 Definitions
    738.103 Dilution Prohibited as a Substitute for Treatment
    738.104 Case-by-Case Extensions of an Effective Date
    738.105 Waste Analysis
     
    SUBPART B: PROHIBITIONS ON INJECTION
    Section
    738.110 Waste Specific Waste-Specific Prohibitions: - Solvent Wastes
    738.111 Waste Specific
    Waste-Specific Prohibitions: - Dioxin-Containing Wastes
    738.112 Waste Specific
    Waste-Specific Prohibitions: - California List Wastes
    738.114 Waste Specific
    Waste-Specific Prohibitions: - First Third Wastes
    738.115 Waste Specific
    Waste-Specific Prohibitions: - Second Third Wastes
    738.116 Waste Specific
    Waste-Specific Prohibitions: - Third Third Wastes
    738.117 Waste Specific
    Waste-Specific Prohibitions: - Newly-Listed Wastes
    738.118 Waste
    Specific Waste-Specific Prohibitions: - Newly-Listed and Identified
    Wastes
     
    SUBPART C: PETITION STANDARDS AND PROCEDURES
    Section
    738.120 Petitions to Allow Injection of a Prohibited Waste
    738.121 Required Information to Support Petitions
    738.122 Submission, Review, and Approval or Denial of Petitions
    738.123 Review of Adjusted Standards
    738.124 Termination of Approved Petition
     
    AUTHORITY: Implementing Sections 7.2, 13, and 22.4 and authorized by Section 27 of the
    Environmental Protection Act [415 ILCS 5/7.2, 13, 22.4, and 27].
     
    SOURCE: Adopted in R89-2 at 14 Ill. Reg. 3059, effective February 20, 1990; amended in R89-
    11 at 14 Ill. Reg. 11948, effective July 9, 1990; amended in R90-14 at 15 Ill. Reg. 11425,

     
    967
    effective July 24, 1991; amended in R92-13 at 17 Ill. Reg. 6190, effective April 5, 1993;
    amended in R93-6 at 17 Ill. Reg. 15641, effective September 14, 1993; amended in R95-4 at 19
    Ill. Reg. 9501, effective June 27, 1995; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 238,
    effective December 16, 1997; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17486, effective
    September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1695, effective January 19,
    1999; amended in R00-11/R01-1 at 24 Ill. Reg. 18576, effective December 7, 2000; amended in
    R01-21/R01-23 at 25 Ill. Reg. 9161, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at
    26 Ill. Reg. 6835, effective April 22, 2002; amended in R06-5/R06-6/R06-7 at 30 Ill. Reg.
    ________, effective ______________________.
     
    SUBPART A: GENERAL
     
    Section 738.101 Purpose, Scope, and Applicability
     
    a) This Part identifies hazardous wastes that are restricted from disposal into Class I
    injection wells and defines those circumstances under which a waste, otherwise
    prohibited from injection, may be injected.
     
    b) The requirements of this Part apply to owners or operators of the following Class
    I injection wells:
     
    1) Hazardous waste injection wells that are used to inject hazardous waste;
    and
     
    2) Injection wells that are used to inject wastes which that once exhibited a
    prohibited characteristic of hazardous waste identified in Subpart C of 35
    Ill. Adm. Code 721.Subpart C, at the point of generation, and which no
    longer exhibit the characteristic at the point of injection.
     
    c) Wastes otherwise prohibited from injection may continue to be injected under any
    of the following circumstances:
     
    1) If USEPA has granted an extension from the effective date of a
    prohibition, has been granted pursuant to as described in Section 738.104;
    or
     
    2) If the Board has granted an adjusted standard has been granted in response
    to a petition filed under Section 738.120; or
     
    3) If the waste is generated by a conditionally exempt small quantity
    generator, as defined in 35 Ill. Adm. Code 721.105.
     
    d) A waste that is hazardous only because it exhibits a characteristic of hazardous
    waste and which is otherwise prohibited from injection under this Part or 35 Ill.
    Adm. Code 728 is not prohibited from injection if the following is true of the
    waste:

     
    968
     
    1) It is disposed into a non-hazardous or hazardous waste injection well, as
    defined under 35 Ill. Adm. Code 730.106(a); and
     
    2) It does not exhibit any prohibited characteristic of hazardous waste
    identified in Subpart C of 35 Ill. Adm. Code 721.Subpart C at the point of
    injection.
     
    BOARD NOTE: Derived from 40 CFR 148.1 (1996) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.102 Definitions
     
    “EPA USEPA Hazardous Waste Number” hazardous waste number” means the
    number assigned by EPA USEPA pursuant to each hazardous waste listed in
    Subpart D of 35 Ill. Adm. Code 721.Subpart D and to each characteristic
    identified in Subpart C of 35 Ill. Adm. Code 721.Subpart C.
     
    “Injection interval” means that part of the injection zone in which the well is
    screened, or in which the waste is otherwise directly emplaced.
     
    “Transmissive fault or fracture” is a fault or fracture that has sufficient
    permeability and vertical extent to allow fluids to move between formations.
     
    “USEPA hazardous waste number” means the number assigned by USEPA
    pursuant to each hazardous waste listed in Subpart D of 35 Ill. Adm. Code 721
    and to each characteristic identified in Subpart C of 35 Ill. Adm. Code 721.
     
    BOARD NOTE: Derived from 40 CFR 148.2 (1988), as added at 53 Fed. Reg. 28155, July 26,
    1988 (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.103 Dilution Prohibited as a Substitute for Treatment
     
    a) The provisions of 35 Ill. Adm. Code 728.103 shall apply to owners or operators of
    Class I injection wells used to inject a waste that is hazardous at the point of
    generation whether or not the waste is hazardous at the point of injection.
     
    b) Owners or operators The owner or operator of a Class I nonhazardous non-
    hazardous waste injection wells well that inject injects waste formerly exhibiting
    a hazardous characteristic which that has been removed by dilution may address
    underlying hazardous constituents by treating the hazardous waste, by obtaining
    an exemption pursuant to a petition filed under Section 738.120, or by complying
    with the provisions set forth in 35 Ill. Adm. Code 728.109.

     
    969
     
    BOARD NOTE: Derived from 40 CFR 148.3 (1996) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.104 Case-by-Case Extensions of an Effective Date
     
    The owner or operator of a Class I hazardous or nonhazardous non-hazardous waste injection
    well may submit an application to USEPA for an extension of the effective date of any
    applicable prohibition established under Subpart B of this Part pursuant to 40 CFR 268.5. (See
    35 Ill. Adm. Code 728.105.) Any extension that is granted by USEPA will be deemed an extension
    of the effective date of the derivative Board rule.
     
    BOARD NOTE: Derived from 40 CFR 148.4 (1996) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.105 Waste Analysis
     
    Generators The generator of hazardous wastes waste that are is disposed of into a Class I
    injection wells well must comply with the applicable requirements of 35 Ill. Adm. Code
    728.107(a) and (b). Owners or operators The owner or operator of a Class I hazardous waste
    injection wells well must comply with the applicable requirements of 35 Ill. Adm. Code
    728.107(c).
     
    BOARD NOTE: Derived from 40 CFR 148.5 (1988), as added at 53 Fed. Reg. 28155, July 26,
    1988 (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART B: PROHIBITIONS ON INJECTION
     
    Section 738.110 Waste Specific Waste-Specific Prohibitions: - Solvent Wastes
     
    a) The spent solvent wastes specified in 35 Ill. Adm. Code 721.131 by the following
    EPA Hazardous Waste USEPA hazardous waste numbers are prohibited from
    underground injection: F001, F002, F003, F004, and F005.
     
    F001
    F002
    F003
    F004
    F005
     
    b) The requirements of subsection (a) above of this Section do not apply under any
    of the following circumstances:

     
    970
     
    1) If the wastes meet waste meets or are is treated to meet the standards of
    Subpart D of 35 Ill. Adm. Code 728.Subpart D; or
     
    2) If the Board has granted an adjusted standard has been granted in response
    to a petition under Subpart C of this Part; or
     
    3) During the period of extension of the applicable effective date, if an
    extension has been granted under by USEPA as referenced in Section
    738.Subpart D 738.104.
     
    BOARD NOTE: Derived from 40 CFR 148.10 (1991), as amended at 57 Fed. Reg. 8088, March
    6, 1992 (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.111 Waste Specific Waste-Specific Prohibitions: - Dioxin-Containing Wastes
     
    a) The dioxin-containing wastes specified in 35 Ill. Adm. Code 721.131 by the
    following EPA Hazardous Waste USEPA hazardous waste numbers are
    prohibited from underground injection: F020, F021, F022, F023, F026, F027, and
    F028.
     
    F020
    F021
    F022
    F023
    F026
    F027
    F028
     
    b) The requirements of subsection (a) of this Section do not apply under any of the
    following circumstances:
     
    1) If the wastes meet waste meets or are is treated to meet the standards of
    Subpart D of 35 Ill. Adm. Code 728.Subpart D; or
     
    2) If the Board has granted an adjusted standard has been granted in response
    to a petition under Subpart C of this Part; or
     
    3) During the period of extension of the applicable effective date, if an
    extension has been granted under by USEPA as referenced in Section
    738.104.
     
    BOARD NOTE: Derived from 40 CFR 148.11 (1989) (2005).
     

     
    971
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.112 Waste Specific Waste-Specific Prohibitions: - California List Wastes
     
    a) The hazardous wastes listed in 35 Ill. Adm. Code 728.132 containing
    polychlorinated biphenyls at concentrations greater than or equal to 50 ppm or
    halogenated organic compounds at concentrations greater than or equal to 10,000
    mg/kg are prohibited from underground injection.
     
    b) The following hazardous wastes are prohibited from underground injection:
     
    1) Liquid hazardous wastes, including free liquids associated with any solid
    or sludge, containing free cyanides at concentrations greater than or equal
    to 1000 mg/l1,000 mg/
    ;
     
    2) Liquid hazardous wastes, including free liquids associated with any solid
    or sludge, containing the following metals (or elements) or compounds of
    these metals (or elements) at concentrations greater than or equal to those
    specified below:
     
    A) Arsenic or compounds (as As) 500 mg/lmg/
    ;
     
    B) Cadmium or compounds (as Cd) 100 mg/lmg/
    ;
     
    C) Chromium (VI) or compounds (as Cr VI) 500 mg/lmg/
    ;
     
    D) Lead or compounds (as Pb) 500 mg/lmg/
    ;
     
    E) Mercury or compounds (as Hg) 20 mg/lmg/
    ;
     
    F) Nickel or compounds (as Ni) 134 mg/lmg/
    ;
     
    G) Selenium or compounds (as Se) 100 mg/lmg/
    ; and
     
    H) Thallium or compounds (as Tl) 130 mg/lmg/
    ;
     
    3) Liquid hazardous waste having a pH less than or equal to two (2.0); and
     
    4) Hazardous wastes containing halogenated organic compounds in total
    concentration less than 10,000 mg/kg but greater than or equal to 1000
    1,000 mg/kg.
     
    c) The requirements of subsections (a) and (b) of this Section do not apply under any
    of the following circumstances:
     
    1) If the wastes meet waste meets or are is treated to meet the applicable

     
    972
    standards specified in Subpart D of 35 Ill. Adm. Code 728.Subpart D; or
     
    2) If the Board has granted an adjusted standard has been granted in response
    to a petition under Subpart C of this Part; or
     
    3) During the period of extension of the applicable effective date, if an
    extension is granted under by USEPA as referenced in Section 738.104.
     
    BOARD NOTE: Derived from 40 CFR 148.12 (1990) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.114 Waste Specific Waste-Specific Prohibitions: - First Third Wastes
     
    a) Prohibitions.
     
    1) The wastes specified in 35 Ill. Adm. Code 721.131 by the following EPA
    Hazardous Waste number USEPA hazardous waste numbers are
    prohibited from underground injection: F006 (wastewaters and
    nonwastewaters), F008, F009, F019.
     
    F006 (wastewaters and nonwastewaters)
    F008
    F009
    F019
     
    2) The wastes specified in 35 Ill. Adm. Code 721.132 by the following EPA
    Hazardous Waste USEPA hazardous waste numbers are prohibited from
    underground injection: K001, K004, K008, K015 (wastewaters and
    nonwastewaters), K016 (at concentrations greater than or equal to one
    percent), K017, K018, K019, K020, K021 (wastewaters, and
    nonwastewaters generated by the process described in the waste listing
    description, and not those generated in the course of treating wastewater
    forms of these wastes), K022 (wastewaters and nonwastewaters), K024,
    K030, K031, K035, K036 (wastewaters, and nonwastewaters generated by
    the process described in the waste listing description, and not those
    generated in the course of treating wastewater forms of these wastes),
    K037, K044, K045, K046 (wastewaters and nonwastewaters), K047,
    K048, K049, K050, K051, K052, K060 (wastewaters, and nonwastewaters
    generated by the process described in the waste listing description, and not
    those generated in the course of treating wastewater forms of these
    wastes), K061 (wastewaters and nonwastewaters), K062, K069 (calcium
    sulfate nonwastewaters; all wastewaters; and noncalcium sulfate
    nonwastewaters generated by the process described in the waste listing
    description, and not those generated in the course of treating wastewater
    forms of these wastes), K071, K073, K083, K084, K085, K086, K087,

     
    973
    K099, K101 (all wastewaters and nonwastewaters), K102 (all wastewaters
    and nonwastewaters), K103, K104, and K106.
     
    K001
    K004
    K008
    K015
    (wastewaters and nonwastewaters)
    K016
    (at concentrations greater than or equal to one percent)
    K017
    K018
    K019
    K020
    K021
    (wastewaters, and nonwastewaters generated by the process
    described in the waste listing description, and not those
    generated in the course of treating wastewater forms of
    these wastes)
    K022
    (wastewaters and nonwastewaters)
    K024
    K030
    K031
    K035
    K036
    (wastewaters, and nonwastewaters generated by the process
    described in the waste listing description, and not those
    generated in the course of treating wastewater forms of
    these wastes)
    K037
    K044
    K045
    K046
    (wastewaters and nonwastewaters)
    K047
    K048
    K049
    K050
    K051
    K052
    K060
    (wastewaters, and nonwastewaters generated by the process
    described in the waste listing description, and not those
    generated in the course of treating wastewater forms of
    these wastes)
    K061
    (wastewaters and nonwastewaters)
    K062
    K069
    (calcium sulfate nonwastewaters; all wastewaters; and
    noncalcium sulfate nonwastewaters generated by the
    process described in the waste listing description, and not
    those generated in the course of treating wastewater forms
    of these wastes)

     
    974
    K071
    K073
    K083
    K084
    K085
    K086
    K087
    K099
    K101
    (all wastewaters and nonwastewaters)
    K102
    (all wastewaters and nonwastewaters)
    K103
    K104
    K106
     
    3) The wastes specified in 35 Ill. Adm. Code 721.133 by the following EPA
    Hazardous Waste USEPA hazardous waste numbers are prohibited from
    underground injection: P001, P004, P005, P010, P011, P012, P015, P016,
    P018, P020, P030, P036, P037, P039, P041, P048, P050, P058, P059,
    P063, P068, P069, P070, P071, P081, P082, P084, P087, P089, P092,
    P094, P097, P102, P105, P108, P110, P115, P120, P122, P123, U007,
    U009, U010, U012, U016, U018, U019, U022, U029, U031, U036, U037,
    U041, U043, U044, U046, U050, U051, U053, U061, U063, U064, U066,
    U067, U074, U077, U078, U086, U089, U103, U105, U108, U115, U122,
    U124, U129, U130, U133, U134, U137, U151, U154, U155, U157, U158,
    U159, U171, U177, U180, U185, U188, U192, U200, U209, U210, U211,
    U219, U220, U221, U223, U226, U227, U228, U237, U238, U248, and
    U249.
     
    P001
    P004
    P005
    P010
    P011
    P012
    P015
    P016
    P018
    P020
    P030
    P036
    P037
    P039
    P041
    P048
    P050
    P058

     
    975
    P059
    P063
    P068
    P069
    P070
    P071
    P081
    P082
    P084
    P087
    P089
    P092
    P094
    P097
    P102
    P105
    P108
    P110
    P115
    P120
    P122
    P123
    U007
    U009
    U010
    U012
    U016
    U018
    U019
    U022
    U029
    U031
    U036
    U037
    U041
    U043
    U044
    U046
    U050
    U051
    U053
    U061
    U063
    U064
    U066
    U067

     
    976
    U074
    U077
    U078
    U086
    U089
    U103
    U105
    U108
    U115
    U122
    U124
    U129
    U130
    U133
    U134
    U137
    U151
    U154
    U155
    U157
    U158
    U159
    U171
    U177
    U180
    U185
    U188
    U192
    U200
    U209
    U210
    U211
    U219
    U220
    U221
    U223
    U226
    U227
    U228
    U237
    U238
    U248
    U249
     
    b) Effective June 7, 1991, the The wastes specified in 35 Ill. Adm. Code 721.132 by
    the following EPA Hazardous Waste USEPA hazardous waste number are

     
    977
    prohibited from underground injection: K016 (at concentrations less than one
    percent).
     
    K016
    (at concentrations less than one percent)
     
    c) Prohibitions.
     
    1) Effective June 8, 1991, the The wastes specified in 35 Ill. Adm. Code
    721.131 by the following EPA Hazardous Waste USEPA hazardous waste
    number are prohibited from underground injection: F007.
     
    F007
     
    2) Effective June 8, 1991, the The wastes specified in 35 Ill. Adm. Code
    721.132 by the following EPA Hazardous Waste USEPA hazardous waste
    numbers are prohibited from underground injection: K011
    (nonwastewaters) and K013 (nonwastewaters).
     
    K011
    (nonwastewaters)
    K013
    (nonwastewaters)
     
    d) Effective May 8, 1992, the The wastes specified in 35 Ill. Adm. Code 721.132 by
    the following EPA Hazardous Waste USEPA hazardous waste numbers are
    prohibited from underground injection: K011 (wastewaters), K013
    (wastewaters), and K014.
     
    K011
    (wastewaters)
    K013
    (wastewaters)
    K014
     
    e) The requirements of subsections (a) through (d) of this Section do not apply under
    any of the following circumstances:
     
    1) If the wastes meet waste meets or are is treated to meet the applicable
    standards specified in Subpart D of 35 Ill. Adm. Code 728.Subpart D; or
     
    2) If the Board has granted an adjusted standard has been granted in response
    to a petition under by USEPA as referenced in Subpart C of this Part; or
     
    3) During the period of extension of the applicable effective date, if an
    extension is granted under by USEPA as referenced in Section 738.104.
     
    BOARD NOTE: Derived from 40 CFR 148.14 (1990) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    978
    Section 738.115 Waste Specific Waste-Specific Prohibitions: - Second Third Wastes
     
    a) Prohibitions.
     
    1) The wastes specified in 35 Ill. Adm. Code 721.131 by the following EPA
    Hazardous Waste USEPA hazardous waste numbers are prohibited from
    underground injection: F010 and F024.
     
    F010
    F024
     
    2) The wastes specified in 35 Ill. Adm. Code 721.132 by the following EPA
    Hazardous Waste USEPA hazardous waste numbers are prohibited from
    underground injection: K009 (nonwastewaters), K010, K025
    (wastewaters, and nonwastewaters generated by the process described in
    the waste listing description, and not those generated in the course of
    treating wastewater forms of these wastes), K027, K028, K029
    (wastewaters and nonwastewaters), K038, K039, K040, K041, K042,
    K043, K095 (wastewaters and nonwastewaters), K096 (wastewaters and
    nonwastewaters), K097, K098, K105, K113, K114, K115, K116.
     
    K009
    (nonwastewaters)
    K010
    K025
    (wastewaters, and nonwastewaters generated by the process
    described in the waste listing description, and not those
    generated in the course of treating wastewater forms of
    these wastes)
    K027
    K028
    K029
    (wastewaters and nonwastewaters)
    K038
    K039
    K040
    K041
    K042
    K043
    K095
    (wastewaters and nonwastewaters)
    K096
    (wastewaters and nonwastewaters)
    K097
    K098
    K105
    K113
    K114
    K115
    K116
     

     
    979
    3) The wastes specified in 35 Ill. Adm. Code 721.133 by the following EPA
    Hazardous Waste USEPA hazardous waste numbers are prohibited from
    underground injection: P002, P003, P007, P008, P014, P026, P027, P029,
    P040, P043, P044, P049, P054, P057, P060, P062, P066, P067, P072,
    P074, P085, P098, P104, P106, P107, P111, P112, P113, P114, U002,
    U003, U005, U008, U011, U014, U015, U020, U021, U023, U025, U026,
    U028, U032, U035, U047, U049, U057, U058, U059, U060, U062, U070,
    U073, U080, U083, U092, U093, U094, U095, U097, U098, U099, U101,
    U106, U107, U109, U110, U111, U114, U116, U119, U127, U128, U131,
    U135, U138, U140, U142, U143, U144, U146, U147, U149, U150, U161,
    U162, U163, U164, U165, U168, U169, U170, U172, U173, U174, U176,
    U178, U179, U189, U193, U196, U203, U205, U206, U208, U213, U214,
    U215, U216, U217, U218, U235, U239, and U244.
     
    P002
    P003
    P007
    P008
    P014
    P026
    P027
    P029
    P040
    P043
    P044
    P049
    P054
    P057
    P060
    P062
    P066
    P067
    P072
    P074
    P085
    P098
    P104
    P106
    P107
    P111
    P112
    P113
    P114
    U002
    U003
    U005

     
    980
    U008
    U011
    U014
    U015
    U020
    U021
    U023
    U025
    U026
    U028
    U032
    U035
    U047
    U049
    U057
    U058
    U059
    U060
    U062
    U070
    U073
    U080
    U083
    U092
    U093
    U094
    U095
    U097
    U098
    U099
    U101
    U106
    U107
    U109
    U110
    U111
    U114
    U116
    U119
    U127
    U128
    U131
    U135
    U138
    U140
    U142

     
    981
    U143
    U144
    U146
    U147
    U149
    U150
    U161
    U162
    U163
    U164
    U165
    U168
    U169
    U170
    U172
    U173
    U174
    U176
    U178
    U179
    U189
    U193
    U196
    U203
    U205
    U206
    U208
    U213
    U214
    U215
    U216
    U217
    U218
    U235
    U239
    U244
     
    b) The wastes specified in 35 Ill. Adm. Code 721.131 by the following EPA
    Hazardous Waste USEPA hazardous waste numbers are prohibited from
    underground injection pursuant to the treatment standards specified in 35 Ill.
    Adm. Code 728.141 and 728.143 applicable to F011 and F012 wastewaters and
    nonwastewaters: F011 (nonwastewaters) and F012 (nonwastewaters).
     
    F011
    (nonwastewaters)
    F012
    (nonwastewaters)
     

     
    982
    c) Effective June 8, 1991, the The wastes specified in 35 Ill. Adm. Code 721.132 by
    the following EPA Hazardous Waste USEPA hazardous waste number are
    prohibited from underground injection: K009 (wastewaters).
     
    K009
    (wastewaters)
     
    d) The requirements of subsections (a) through (c) of this Section do not apply under
    any of the following circumstances:
     
    1) If the wastes meet waste meets or are is treated to meet the applicable
    standards specified in Subpart D of 35 Ill. Adm. Code 728.Subpart D; or
     
    2) If the Board has granted an adjusted standard has been granted in response
    to a petition under Subpart C of this Part; or
     
    3) During the period of extension of the applicable effective date, if an
    extension is granted under by USEPA as referenced in Section 738.104.
     
    BOARD NOTE: Derived from 40 CFR 148.15 (1990) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.116 Waste Specific Waste-Specific Prohibitions: - Third Third Wastes
     
    a) Prohibitions.
     
    1) The wastes specified in 35 Ill. Adm. Code 721.131 by the following EPA
    Hazardous Waste USEPA hazardous waste numbers are prohibited from
    underground injection: F025 and F039 (nonwastewaters).
     
    F025
    F039
    (nonwastewaters)
     
    2) The wastes specified in 35 Ill. Adm. Code 721.132 by the following EPA
    Hazardous Waste USEPA hazardous waste numbers are prohibited from
    underground injection: K002, K003, K005 (wastewaters and
    nonwastewaters), K006, K007 (wastewaters and nonwastewaters), K023,
    K026, K032, K033, K034, K093, K094, and K100.
     
    K002
    K003
    K005
    (wastewaters and nonwastewaters)
    K006
    K007
    (wastewaters and nonwastewaters)
    K023
    K026

     
    983
    K032
    K033
    K034
    K093
    K094
    K100
     
    3) The wastes specified in 35 Ill. Adm. Code 721.133 by the following EPA
    Hazardous Waste USEPA hazardous waste numbers are prohibited from
    underground injection: P006, P009, P013, P017, P021, P022, P023, P024,
    P028, P031, P033, P034, P038, P042, P045, P046, P047, P051, P056,
    P064, P065, P073, P075, P076, P077, P078, P088, P093, P095, P096,
    P099, P101, P103, P109, P116, P118, P119, P121, U001, U004, U006,
    U017, U024, U027, U030, U033, U034, U038, U039, U042, U045, U048,
    U052, U055, U056, U068, U069, U071, U072, U075, U076, U079, U081,
    U082, U084, U085, U087, U088, U090, U091, U096, U102, U112, U113,
    U117, U118, U120, U121, U123, U125, U126, U132, U136, U141, U145,
    U148, U152, U153, U156, U160, U166, U167, U181, U182, U183, U184,
    U186, U187, U190, U191, U194, U197, U201, U202, U204, U207, U222,
    U225, U234, U236, U240, U243, U246, and U247.
     
    P006
    P009
    P013
    P017
    P021
    P022
    P023
    P024
    P028
    P031
    P033
    P034
    P038
    P042
    P045
    P046
    P047
    P051
    P056
    P064
    P065
    P073
    P075
    P076
    P077

     
    984
    P078
    P088
    P093
    P095
    P096
    P099
    P101
    P103
    P109
    P116
    P118
    P119
    P121
    U001
    U004
    U006
    U017
    U024
    U027
    U030
    U033
    U034
    U038
    U039
    U042
    U045
    U048
    U052
    U055
    U056
    U068
    U069
    U071
    U072
    U075
    U076
    U079
    U081
    U082
    U084
    U085
    U087
    U088
    U090
    U091
    U096

     
    985
    U102
    U112
    U113
    U117
    U118
    U120
    U121
    U123
    U125
    U126
    U132
    U136
    U141
    U145
    U148
    U152
    U153
    U156
    U160
    U166
    U167
    U181
    U182
    U183
    U184
    U186
    U187
    U190
    U191
    U194
    U197
    U201
    U202
    U204
    U207
    U222
    U225
    U234
    U236
    U240
    U243
    U246
    U247
     
    4) The wastes specified in 35 Ill. Adm. Code 721.121 or 721.124 by
    characteristic alone and designated by the following EPA Hazardous

     
    986
    Waste USEPA hazardous waste numbers are prohibited from underground
    injection: D001, D004, D005, D006, D008, D009 (wastewaters), D010,
    D011, D012, D013, D014, D015, D016, and D017.
     
    D001
    D004
    D005
    D006
    D008
    D009
    (wastewaters)
    D010
    D011
    D012
    D013
    D014
    D015
    D016
    D017
     
    b) Mixed radioactive/hazardous
    radioactive and hazardous wastes in 35 Ill. Adm.
    Code 728.110, 728.111, and 728.112, which are mixed radioactive and hazardous
    wastes, are prohibited from underground injection.
     
    c) Prohibitions.
     
    1) Effective May 8, 1992, the The wastes specified in 35 Ill. Adm. Code
    721.131 by the following EPA Hazardous Waste USEPA hazardous waste
    number are prohibited from underground injection: F039
    (nonwastewaters).
     
    F039 (nonwastewaters)
     
    2) Effective May 8, 1992, the The wastes specified in 35 Ill. Adm. Code
    721.122, 721.123 or 721.124 as hazardous based on a characteristic alone
    and designated by the following EPA Hazardous Waste USEPA hazardous
    waste numbers are prohibited from underground injection: D002
    (wastewaters and nonwastewaters), D003 (wastewaters and
    nonwastewaters), D007 (wastewaters and nonwastewaters), and D009
    (nonwastewaters).
     
    D002
    (wastewaters and nonwastewaters)
    D003
    (wastewaters and nonwastewaters)
    D007
    (wastewaters and nonwastewaters)
    D009
    (nonwastewaters)
     
    3)
    The effective date of subsections (c)(1) and (c)(2) do not apply to the

     
    987
    wastes listed in Section 148.112(b) which are prohibited from
    underground injection effective August 8, 1990.
     
    d) The requirements of subsections (a) through (c) of this Section do not apply under
    any of the following circumstances:
     
    1) If the wastes meet waste meets or are is treated to meet the applicable
    standards specified in Subpart D of 35 Ill. Adm. Code 728.Subpart D; or
     
    2) If the Board has granted an adjusted standard has been granted in response
    to a petition under Subpart C of this Part; or
     
    3) During the period of extension of the applicable effective date, if an
    extension is granted under by USEPA as referenced in Section 738.104.
     
    BOARD NOTE: Derived from 40 CFR 148.16 (1990) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.117 Waste-Specific Prohibitions: - Newly-Listed Wastes
     
    a) The wastes specified in Subpart D of 35 Ill. Adm. Code 721.Subpart D by the
    following USEPA hazardous waste numbers are prohibited from underground
    injection: F037, F038, K107, K108, K109, K110, K111, K112, K117, K118,
    K123, K124, K125, K126, K131, K136, U328, U353, and U359.
     
    F037
    F038
    K107
    K108
    K109
    K110
    K111
    K112
    K117
    K118
    K123
    K124
    K125
    K126
    K131
    K136
    U328
    U353
    U359
     

     
    988
    b) The wastes specified in Subpart D of 35 Ill. Adm. Code 721.Subpart D by the
    following USEPA hazardous waste numbers are prohibited from underground
    injection: K141, K142, K143, K144, K145, K147, K148, K149, K150, and K151.
     
    K141
    K142
    K143
    K144
    K145
    K147
    K148
    K149
    K150
    K151
     
    c) This subsection (c) corresponds with 40 CFR 148.17(c), removed and marked
    “reserved” by USEPA at 61 Fed. Reg. 15662 (April 8, 1996). This statement
    maintains structural consistency with USEPA rules.
     
    d) Effective June 30, 1995, the The wastes specified in Subpart D of 35 Ill. Adm.
    Code 721.Subpart D by the following USEPA hazardous waste numbers are
    prohibited from underground injection: K117, K118, K131, and K132.
     
    K117
    K118
    K131
    K132
     
    e) The requirements of subsections (a) and (b) through (d) of this Section do not
    apply under any of the following circumstances:
     
    1) If the wastes meet waste meets or are is treated to meet the applicable
    standards specified in Subpart D of 35 Ill. Adm. Code 728.Subpart D; or
     
    2) If the Board has granted an adjusted standard has been granted in response
    to a petition under Subpart C of this Part; or
     
    3) During the period of extension of the applicable effective date, if an
    extension is granted under by USEPA as referenced in Section 738.104.
     
    BOARD NOTE: Derived from 40 CFR 148.17 (1996) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    989
    Section 738.118 Waste-Specific Prohibitions: - Newly-Listed and Identified Wastes
     
    a) All newly identified D004 through D011 wastes and characteristic mineral
    processing wastes, except those identified in subsection (b) of this Section, are
    prohibited from underground injection.
     
    b) Characteristic hazardous wastes from titanium dioxide mineral processing, and
    radioactive wastes mixed with newly identified D004 through D011 or mixed
    with newly identified characteristic mineral processing wastes, are prohibited
    from underground injection.
     
    c) The wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous waste
    numbers F032, F034, F035 are prohibited from underground injection.
     
    d) The wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous waste
    numbers F032, F034, F035 that are mixed with radioactive wastes are prohibited
    from underground injection.
     
    e) The wastes specified in 35 Ill. Adm. Code 721.132 as having the following
    USEPA hazardous waste numbers are prohibited from underground injection:
    K156, K157, K158, K159, K160, K161, P127, P128, P185, P188, P189, P190,
    P191, P192, P194, P196, P197, P198, P199, P201, P202, P203, P204, P205,
    U271, U277, U278, U279, U280, U364, U365, U366, U367, U372, U373, U375,
    U376, U377, U378, U379, U381, U382, U383, U384, U385, U386, U387, U389,
    U390, U391, U392, U393, U394, U395, U396, U400, U401, U402, U403, U404,
    U407, U409, U410, and U411.
     
    f) The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste
    number K088 is are prohibited from underground injection.
     
    g) The wastes specified in 35 Ill. Adm. Code 721 as having the following USEPA
    hazardous waste numbers and Mixed TC/Radioactive wastes are prohibited from
    underground injection: D018, D019, D020, D021, D022, D023, D024, D025,
    D026, D027, D028, D029, D030, D031, D032, D033, D034, D035, D036, D037,
    D038, D039, D040, D041, D042, and D043.
     
    h) This subsection (h) corresponds with 40 CFR 148.18(h), which USEPA has
    removed and marked “reserved.” This statement maintains structural consistency
    with the federal regulations.
     
    i) The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste
    numbers K169 through K172 are prohibited from underground injection.
     
    j) The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste
    numbers K174 and K175 are prohibited from underground injection.
     

     
    990
    k) Effective May 20, 2002, the The wastes specified in 35 Ill. Adm. Code 721.132 as
    USEPA hazardous waste numbers K176, K177, and K178 are prohibited from
    underground injection.
     
    l) The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste
    number K181 are prohibited from underground injection.
     
    lm) The requirements of subsections (a) through (k) (l) of this Section do not apply
    under any of the following circumstances:
     
    1) If the wastes meet waste meets or are is treated to meet the applicable
    standards specified in Subpart D of 35 Ill. Adm. Code 728; or
     
    2) If the Board has granted an exemption from a prohibition has been granted
    adjusted standard in response to a petition under Subpart C of this Part; or
     
    3) During the period of extension of the applicable effective date, if an
    extension has been granted under by USEPA as referenced in Section
    738.104.
     
    BOARD NOTE: Derived from 40 CFR 148.18 (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART C: PETITION STANDARDS AND PROCEDURES
     
    Section 738.120 Petitions to Allow Injection of a Prohibited Waste
     
    a) Any person seeking an exemption from a prohibition under Subpart B of this Part
    for the injection of a restricted hazardous waste, including a hazardous waste that
    exhibits a characteristic of hazardous waste and which contains underlying
    hazardous constituents at the point of generation, but which no longer exhibits a
    characteristic of hazardous waste when injected into a Class I injection well or
    wells, shall must submit a petition for an adjusted standard to the Board, pursuant
    to Subpart D of 35 Ill. Adm. Code 106.Subpart G 104, demonstrating that, to a
    reasonable degree of certainty, there will be no migration of hazardous
    constituents from the injection zone for as long as the waste remains hazardous.
    This demonstration requires a showing that the following:
     
    1) The hydrogeological and geochemical conditions at the site(s) site and the
    physiochemical nature of the waste stream(s) stream are such that reliable
    predictions can be made that with regard to each of the following:
     
    A) Fluid movement conditions are such that the injected fluids will
    not migrate within 10,000 years in either of the following ways:
     

     
    991
    i) Vertically upward out of the injection zone; or
     
    ii) Laterally within the injection zone to a point of discharge
    or interface with an Underground Source underground
    source of Drinking Water drinking water (USDW), as
    defined in 35 Ill. Adm. Code 730; or
     
    B) Before the injected fluids migrate out of the injection zone or to a
    point of discharge or interface with a USDW, the fluid will no
    longer be hazardous because of attenuation, transformation, or
    immobilization of hazardous constituents within the injection zone
    by hydrolysis, chemical interactions, or other means; and
     
    2) For each well, the petition has fulfilled the following requirements:
     
    A) Demonstrated
    It has demonstrated that the injection well’s area of
    review complies with the substantive requirements of 35 Ill. Adm.
    Code 730.163;
     
    B) Located,
    It has located, identified, and ascertained the condition of
    all wells within the injection well’s area of review (as specified in
    35 Ill. Adm. Code 730.163) that penetrate the injection zone or the
    confining zone by use of a protocol acceptable to the Board that
    meets the substantive requirements of 35 Ill. Adm. Code 730.164;
     
    C) Submitted
    It has provided a corrective action plan that meets the
    substantive requirements of 35 Ill. Adm. Code 730.164, the
    implementation of which shall will become a condition of any
    adjusted standard granted; and
     
    D) Submitted
    It has provided the results of pressure and radioactive
    tracer tests performed within one year prior to submission of the
    petition demonstrating the mechanical integrity of the well’s long
    string casing, injection tube, annular seal, and bottom hole cement.
    In cases where the petition has not been approved or denied within
    one year after the initial demonstration of mechanical integrity, the
    Board may require the owner or operator to perform the tests again
    and submit the results of the new tests.
     
    BOARD NOTE: The requirements of subsection (a)(2) of this Section
    need not be incorporated in a permit at the time the Board grants an
    adjusted standard.
     
    b) A demonstration under subsection (a)(1)(A) of this Section must identify the
    strata within the injection zone which will confine fluid movement above the
    injection interval, and it must include a showing that this strata is free of known

     
    992
    transmissive faults of fractures and that there is a confining zone above the
    injection zone.
     
    c) A demonstration under subsection (a)(1)(B) of this Section must identify the
    strata within the injection zone where waste transformation will be accomplished,
    and it must include a showing that this strata is free of known transmissive faults
    or fractures and that there is a confining zone above the injection zone.
     
    d) A demonstration may include a showing that either of the following features,
    which will become a condition of the adjusted standard:
     
    1) Treatment methods that the owner or operator will use to reduce the
    toxicity or mobility of the wastes, the implementation of which will
    become a condition of any adjusted standard, must be utilized; or
     
    2) A monitoring plan, the implementation of which will become a condition
    of any adjusted standard, must be utilized that the owner or operator will
    use to enhance confidence in one or more aspects of the demonstration.
     
    e) Any person that has been granted an adjusted standard pursuant to this Section
    may submit a petition for reissuance of the adjusted standard to include an
    additional restricted waste or wastes or to modify any conditions placed imposed
    on that adjusted standard by the Board. The Board will reissue the adjusted
    standard if the petitioner complies with subsections (a), (b), and (c) of this
    Section.
     
    f) Any person that has been granted an adjusted standard pursuant to this Section
    may submit a petition to modify that adjusted standard to include an additional
    (hazardous) waste or wastes. The Board may will grant the modification if it
    determines, to a reasonable degree of certainty, that the additional waste or wastes
    will behave hydraulically and chemically in a manner similar to previously
    included wastes and that it the additional waste or wastes will not interfere with
    the containment capability of the injection zone.
     
    BOARD NOTE: Derived from 40 CFR 148.20 (1996) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.121 Required Information to Support Petitions
     
    a) Information submitted in support of a Section 738.120 petition must meet the
    following criteria requirements:
     
    1) All data from waste analyses and any new testing performed by the
    petitioner must be approved by the Board and must provide data that are
    accurate, reproducible, and performed in accordance with quality

     
    993
    assurance standards;
     
    2) Estimation
    The following must be true with regard to estimation and
    monitoring techniques and the identification of applicable existing EPA-
    certified USEPA-certified test protocols:
     
    A) All estimation and monitoring techniques must be approved by the
    Board; and
     
    B) The petition must identify all applicable USEPA-certified test
    protocols in existence at the time the estimation and monitoring
    was performed;
     
    3) Predictive models must have been verified and validated, must be
    appropriate for the specific site, wastestreams waste streams, and injection
    conditions of the operation, and they must be calibrated for existing sites
    where sufficient data are available;
     
    4) A quality assurance and quality control plan addressing all aspects of the
    demonstration must be provided to and approved by the Board;
     
    5) Reasonably conservative values must be used whenever values taken from
    the literature or estimated on the basis of known information are used
    instead of site-specific measurements; and
     
    6) An analysis must be performed to identify and assess aspects of the
    demonstration that contribute significantly to uncertainty. The petitioner
    shall must conduct a sensitivity analysis to determine the effect that
    significant uncertainty may contribute to the demonstration. The
    demonstration must then be based on conservative assumptions identified
    in the analysis.
     
    b) Any petitioner under Section 738.120(a)(1)(A) shall must provide sufficient site-
    specific information to support the demonstration, such as the following:
     
    1) Thickness,
    The thickness, porosity, permeability and extent of the various
    strata in the injection zone;
     
    2) Thickness,
    The thickness, porosity, permeability, extent and continuity of
    the confining zone;
     
    3) Hydraulic
    The hydraulic gradient in the injection zone;
     
    4) Hydrostatic
    The hydrostatic pressure in the injection zone; and
     
    5) Geochemical The geochemical conditions of the site.

     
    994
     
    c) In addition to the information in subsection 738.121(b) (b) of this Section, any
    petitioner under Section 738.120(a)(1)(B) of this Part shall must provide
    sufficient waste-specific information to ensure reasonably reliable predictions
    about the waste transformation. The petitioner shall must provide the information
    necessary to support the demonstration, such as the following:
     
    1) Description
    A description of the chemical processes or other means that
    will lead to waste transformation; and
     
    2) Results of laboratory experiments verifying the waste transformation.
     
    BOARD NOTE: Derived from 40 CFR 148.21 (1988), as added at 53 Fed. Reg. 28156, July 26,
    1988 (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.122 Submission, Review, and Approval or Denial of Petitions
     
    a) Any petition submitted to the Board, pursuant to Section 738.120(a) of this Part,
    must include the following:
     
    1) An identification of the specific waste or wastes and the specific injection
    well or wells for which the demonstration will be made;
     
    2) A waste analysis fully describing the chemical and physical characteristics
    of the subject wastes;
     
    3) Such additional information as the Board requires to support the petition
    under Section 738.120 and Section 738.121 of this Part; and
     
    4) This
    The following statement signed by the petitioner or an authorized
    representative:
     
    I certify under penalty of law that I have personally examined and
    am familiar with the information submitted in this petition and all
    attached documents, and that, based on my inquiry of those
    individuals immediately responsible for obtaining the information,
    I believe that submitted information is true, accurate and complete.
    I am aware that there are significant penalties for submitting false
    information, including the possibility of fine and imprisonment.
     
    b) The Board will provide public notice and an opportunity for public comment in
    accordance with the procedures in Subpart D of 35 Ill. Adm. Code 106.Subpart G
    104.
     

     
    995
    c) An adjusted standard will apply only to the underground injection of the specific
    restricted waste or wastes identified in the petition into a Class I hazardous waste
    injection well or wells specifically identified in the petition (unless the adjusted
    standard is modified or reissued pursuant to Section 738.120(e) or (f)).
     
    d) Upon request by any petitioner who obtains an adjusted standard for a well under
    this Subpart C, the Agency shall must initiate and reasonably expedite the
    necessary procedures to issue or reissue a permit or permits for the hazardous
    waste well or wells covered by the adjusted standard for a term not to exceed ten
    years.
     
    e) Each adjusted standard granted under this Part is subject to the following
    condition, whether or not this condition appears as part of the adjusted standard,
    and the Board will include this condition as part of each adjusted standard
    granted: “This adjusted standard does not affect the enforceability of any
    provisions of the Environmental Protection Act, Board rules, or other laws, except
    to the extent that its provisions expressly state otherwise.”
     
    BOARD NOTE: Derived from 40 CFR 148.22 (1988), as added at 53 Fed. Reg. 28156, July 26,
    1988 (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.123 Review of Adjusted Standards
     
    a) Agency review.
     
    1) When considering whether to reissue a permit for the operation of a Class
    I hazardous waste injection well, the Agency shall must review any
    adjusted standard(s) standard granted by the Board pursuant to this
    Subpart C.
     
    2) If the Agency determines that new information shows that the basis for
    granting the adjusted standard may no longer be valid, the Agency shall
    must request in writing that the permittee submit a petition to the Board to
    modify the adjusted standard.
     
    3) All petitions requested by the Agency pursuant to subsection (a)(2) of this
    Section must be filed pursuant to section 738.120(f). Such a petition may
    seek reaffirmation of the adjusted standard without modification.
     
    4) Permittee's failure to file a petition, Agency petitions for reconsideration,
    and Board reconsideration of adjusted standards:.
     
    A) If the permittee fails to file a petition requested by the Agency
    under subsection (a)(2) of this Section, the Agency may petition

     
    996
    the Board for reconsideration of any adjusted standard granted
    under this Part at any time during the effectiveness of that adjusted
    standard, the limitation periods of 35 Ill. Adm. Code 101.300
    101.520 and 101.301 101.904 notwithstanding.
     
    B) Board review.
     
    i) The Board may conduct a plenary review of the substance
    of any adjusted standard on reconsideration to the same
    extent that it would review a new petition for an adjusted
    standard.
     
    ii) The Board may treat a motion for reconsideration of an
    adjusted standard as a new petition under Section 738.120
    and require that the full requirements of that section
    Section and of Subpart D of 35 Ill. Adm. Code 106.Subpart
    G 104 apply to the proceeding, with the Agency acting as
    the petitioner.
     
    b) Whenever the Board determines that the basis for approval of a petition may no
    longer be valid, the Board will require a new demonstration in accordance with
    Section 738.120.
     
    BOARD NOTE: Derived from 40 CFR 148.23 (1988), as added at 53 Fed. Reg. 28157, July 26,
    1988 (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 738.124 Termination of Approved Petition
     
    a) Termination through an enforcement action.
     
    1) Enforcement actions An enforcement action against an owners or
    operators owner or operator having an adjusted standards standard and
    limitations limitation on Agency petitions for reconsideration of an
    adjusted standards standard:
     
    A) Any person may file an enforcement action against an owner or
    operator of an underground injection well pursuant to Section 33
    of the Environmental Protection Act, Ill. Rev. Stat. ch. 111 1/2,
    par. 1033, [415 ILCS 5/33] for any violation of the Act or Board
    rules, notwithstanding the existence of any adjusted standard.
     
    B) The Agency may petition the Board for reconsideration of any
    adjusted standard at any time during the effectiveness of that
    adjusted standard, the limitation periods of 35 Ill. Adm. Code

     
    997
    101.300 101.520 and 101.301 101.904 notwithstanding.
     
    2) In any action under subsection (a)(1) of this Section, if the Board finds a
    violation of the Act or Board regulations, the Board may terminate any
    adjusted standard granted under Section 738.120 for any of the following
    causes:
     
    A) Noncompliance by the owner or operator with any condition of the
    adjusted standard;
     
    B) The owner or operator's failure in the petition or during the review
    and approval to disclose fully all relevant facts, or the petitioner's
    misrepresentation of any relevant facts at any time; or
     
    C) A determination that new information shows that the basis for
    approval of the petition is no longer valid.
     
    b) In any action under subsection (a)(1) of this Section, the Board will terminate an
    adjusted standard granted under Section 738.120 for the following cases causes:
     
    1) The petitioner's willful withholding during the review and approval of the
    petition of facts directly and materially relevant to the Board’s decision on
    the petition;
     
    2) A determination that there has been migration from the injection zone or
    the well that is not in accordance with the terms of the adjusted standard,
    except that the Board, may at its discretion decide not to terminate where
    both of the following conditions are fulfilled:
     
    A) The migration resulted from a mechanical failure of the well that
    can be promptly corrected promptly through a repair to the
    injection well itself or from an undetected well or conduit that can
    be plugged promptly; and
     
    B) The requirements of 35 Ill. Adm. Code 730.167 are satisfied.
     
    BOARD NOTE: Derived from 40 CFR 148.24 (1988), as added at 53 Fed. Reg. 28157, July 26,
    1988 (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
     

     
    998
    PART 739
    STANDARDS FOR THE MANAGEMENT OF USED OIL
     
    SUBPART A: DEFINITIONS
    Section
    739.100 Definitions
     
    SUBPART B: APPLICABILITY
    Section
    739.110 Applicability
    739.111 Used Oil Specifications
    739.112 Prohibitions
     
    SUBPART C: STANDARDS FOR USED OIL GENERATORS
    Section
    739.120 Applicability
    739.121 Hazardous Waste Mixing
    739.122 Used Oil Storage
    739.123 On-Site Burning in Space Heaters
    739.124 Off-Site Shipments
     
    SUBPART D: STANDARDS FOR USED OIL COLLECTION CENTERS AND
    AGGREGATION POINTS
    Section
    739.130 Do-It-Yourselfer Used Oil Collection Centers
    739.131 Used Oil Collection Centers
    739.132 Used Oil Aggregate Points Owned by the Generator
     
    SUBPART E: STANDARDS FOR USED OIL TRANSPORTER AND
    TRANSFER FACILITIES
    Section
    739.140 Applicability
    739.141 Restrictions on Transporters that Are Not Also Processors
    739.142 Notification
    739.143 Used Oil Transportation
    739.144 Rebuttable Presumption for Used Oil
    739.145 Used Oil Storage at Transfer Facilities
    739.146 Tracking
    739.147 Management of Residues
     
    SUBPART F: STANDARDS FOR USED OIL PROCESSORS
    Section
    739.150 Applicability
    739.151 Notification
    739.152 General Facility Standards
    739.153 Rebuttable Presumption for Used Oil

     
    999
    739.154 Used Oil Management
    739.155 Analysis Plan
    739.156 Tracking
    739.157 Operating Record and Reporting
    739.158 Off-Site Shipments of Used Oil
    739.159 Management of Residues
     
    SUBPART G: STANDARDS FOR USED OIL BURNERS THAT BURN OFF-
    SPECIFICATION USED OIL FOR ENERGY RECOVERY
    Section
    739.160 Applicability
    739.161 Restriction on Burning
    739.162 Notification
    739.163 Rebuttable Presumption for Used Oil
    739.164 Used Oil Storage
    739.165 Tracking
    739.166 Notices
    739.167 Management of Residues
     
    SUBPART H: STANDARDS FOR USED OIL FUEL MARKETERS
    Section
    739.170 Applicability
    739.171 Prohibitions
    739.172 On-Specification Used Oil Fuel
    739.173 Notification
    739.174 Tracking
    739.175 Notices
     
    SUBPART I: STANDARDS FOR USE AS A DUST SUPPRESSANT
    DISPOSAL OF USED OIL
    Section
    739.180 Applicability
    739.181 Disposal
    739.182 Use As a Dust Suppressant
     
    AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the
    Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].
     
    SOURCE: Adopted in R93-4 at 17 Ill. Reg. 20954, effective November 22, 1993; amended in
    R93-16 at 18 Ill. Reg. 6931, effective April 26, 1994; amended in R94-17 at 18 Ill. Reg. 17616,
    effective November 23, 1994; amended in R95-6 at 19 Ill. Reg. 10036, effective June 27, 1995;
    amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 767, effective December 16, 1997; amended in
    R98-21/R99-2/R99-7 at 23 Ill. Reg. 2274, effective January 19, 1999; amended in R04-16 at 28
    Ill. Reg. 10706, effective July 19, 2004; amended in R06-5/R06-6/R06-7 at 30 Ill. Reg.
    ________, effective ______________________.
     

     
    1000
    SUBPART B: APPLICABILITY
     
    Section 739.110 Applicability
     
    This Section identifies those materials that are subject to regulation as used oil under this Part.
    This Section also identifies some materials that are not subject to regulation as used oil under
    this Part, and indicates whether these materials may be subject to regulation as hazardous waste
    under 35 Ill. Adm. Code 702, 703, 720 through 726, and 728.
     
    a) Used oil. Used oil is presumed to be recycled, unless a used oil handler disposes
    of used oil or sends used oil for disposal. Except as provided in Section 739.111,
    the regulations of this Part apply to used oil and to materials identified in this
    Section as being subject to regulation as used oil, whether or not the used oil or
    material exhibits any characteristics of hazardous waste identified in Subpart C of
    35 Ill. Adm. Code 721.
     
    b) Mixtures of used oil and hazardous waste.
     
    1) Listed hazardous waste.
     
    A) A mixture of used oil and hazardous waste that is listed in Subpart
    D of 35 Ill. Adm. Code 721 is subject to regulation as hazardous
    waste under 35 Ill. Adm. Code 703, 720 through 726, and 728,
    rather than as used oil under this Part.
     
    B) Rebuttable presumption for used oil. Used oil containing more
    than 1,000 ppm total halogens is presumed to be a hazardous waste
    because it has been mixed with halogenated hazardous waste listed
    in Subpart D of 35 Ill. Adm. Code 721. Persons An owner or
    operator may rebut this presumption by demonstrating that the
    used oil does not contain hazardous waste (for example, by using
    an analytical method from SW-846, incorporated by reference in
    35 Ill. Adm. Code 720.111, to show showing that the used oil does
    not contain significant concentrations of halogenated hazardous
    constituents listed in Appendix H of 35 Ill. Adm. Code 721).
     
    i) This rebuttable presumption does not apply to
    metalworking oils or fluids containing chlorinated
    paraffins, if they are processed, through a tolling
    arrangement as described in Section 739.124(c), to reclaim
    metalworking oils or fluids. This presumption does apply
    to metalworking oils or fluids if such oils or fluids are
    recycled in any other manner, or disposed.
     
    ii) This rebuttable presumption does not apply to used oils
    contaminated with chlorofluorocarbons (CFCs) removed

     
    1001
    from refrigeration units where the CFCs are destined for
    reclamation. This rebuttable presumption does apply to
    used oils contaminated with CFCs that have been mixed
    with used oil from sources other than refrigeration units.
     
    2) Characteristic hazardous waste. A mixture of used oil and hazardous
    waste that exhibits a hazardous waste characteristic identified in Subpart C
    of 35 Ill. Adm. Code 721 and a mixture of used oil and hazardous waste
    that is listed in Subpart D of this Part solely because it exhibits one or
    more of the characteristics of hazardous waste identified in Subpart C of
    35 Ill. Adm. Code 721 is subject to the following:
     
    A) Except as provided in subsection (b)(2)(C) of this Section,
    regulation as hazardous waste under 35 Ill. Adm. Code 703, 720
    through 726, and 728 rather than as used oil under this Part, if the
    resultant mixture exhibits any characteristics of hazardous waste
    identified in Subpart C of 35 Ill. Adm. Code 721; or
     
    B) Except as provided in subsection (b)(2)(C) of this Section,
    regulation as used oil under this Part, if the resultant mixture does
    not exhibit any characteristics of hazardous waste identified under
    Subpart C of 35 Ill. Adm. Code 721.
     
    C) Regulation as used oil under this Part, if the mixture is of used oil
    and a waste that is hazardous solely because it exhibits the
    characteristic of ignitability (e.g., ignitable-only mineral spirits),
    provided that the resultant mixture does not exhibit the
    characteristic of ignitability under 35 Ill. Adm. Code 721.121.
     
    3) Conditionally exempt small quantity generator hazardous waste. A
    mixture of used oil and conditionally exempt small quantity generator
    hazardous waste regulated under 35 Ill. Adm. Code 721.105 is subject to
    regulation as used oil under this Part.
     
    c) Materials containing or otherwise contaminated with used oil.
     
    1) Except as provided in subsection (c)(2) of this Section, the following is
    true of a material containing or otherwise contaminated with used oil from
    which the used oil has been properly drained or removed to the extent
    possible so that no visible signs of free-flowing oil remain in or on the
    material:
     
    A) The material is not used oil, so it is not subject to this Part, and
     
    B) If applicable, the material is subject to the hazardous waste
    regulations of 35 Ill. Adm. Code 703, 705, 720 through 726, and

     
    1002
    728.
     
    2) A material containing or otherwise contaminated with used oil that is
    burned for energy recovery is subject to regulation as used oil under this
    Part.
     
    3) Used oil drained or removed from materials containing or otherwise
    contaminated with used oil is subject to regulation as used oil under this
    Part.
     
    d) Mixtures of used oil with products.
     
    1) Except as provided in subsection (d)(2) of this Section, mixtures of used
    oil and fuels or other fuel products are subject to regulation as used oil
    under this Part.
     
    2) Mixtures of used oil and diesel fuel mixed on-site by the generator of the
    used oil for use in the generator’s own vehicles are not subject to this Part
    once the used oil and diesel fuel have been mixed. Prior to mixing, the
    used oil is subject to the requirements of Subpart C of this Part.
     
    e) Materials derived from used oil.
     
    1) The following is true of materials that are reclaimed from used oil, which
    are used beneficially, and which are not burned for energy recovery or
    used in a manner constituting disposal (e.g., re-refined lubricants):
     
    A) The materials are not used oil and thus are not subject to this Part,
    and
     
    B) The materials are not solid wastes and are thus not subject to the
    hazardous waste regulations of 35 Ill. Adm. Code 703, 720 through
    726, and 728, as provided in 35 Ill. Adm. Code 721.103(e)(1).
     
    2) Materials produced from used oil that are burned for energy recovery
    (e.g., used oil fuels) are subject to regulation as used oil under this Part.
     
    3) Except as provided in subsection (e)(4) of this Section, the following is
    true of materials derived from used oil that are disposed of or used in a
    manner constituting disposal:
     
    A) The materials are not used oil and thus are not subject to this Part,
    and
     
    B) The materials are solid wastes and thus are subject to the
    hazardous waste regulations of 35 Ill. Adm. Code 703, 720 through

     
    1003
    726, and 728 if the materials are listed or identified as hazardous
    waste.
     
    4) Used oil re-refining distillation bottoms that are used as feedstock to
    manufacture asphalt products are not subject to this Part.
     
    f) Wastewater. Wastewater, the discharge of which is subject to regulation under
    either Section 402 or Section 307(b) of the federal Clean Water Act (including
    wastewaters at facilities that have eliminated the discharge of wastewater),
    contaminated with de minimis quantities of used oil are not subject to the
    requirements of this Part. For purposes of this subsection, “de minimis”
    quantities of used oils are defined as small spills, leaks, or drippings from pumps,
    machinery, pipes, and other similar equipment during normal operations or small
    amounts of oil lost to the wastewater treatment system during washing or draining
    operations. This exception will not apply if the used oil is discarded as a result of
    abnormal manufacturing operations resulting in substantial leaks, spills, or other
    releases, or to used oil recovered from wastewaters.
     
    g) Used oil introduced into crude oil pipelines or a petroleum refining facility.
     
    1) Used oil mixed with crude oil or natural gas liquids (e.g., in a production
    separator or crude oil stock tank) for insertion into a crude oil pipeline is
    exempt from the requirements of this Part. The used oil is subject to the
    requirements of this Part prior to the mixing of used oil with crude oil or
    natural gas liquids.
     
    2) Mixtures of used oil and crude oil or natural gas liquids containing less
    than one percent used oil that are being stored or transported to a crude oil
    pipeline or petroleum refining facility for insertion into the refining
    process at a point prior to crude distillation or catalytic cracking are
    exempt from the requirements of this Part.
     
    3) Used oil that is inserted into the petroleum refining process before crude
    distillation or catalytic cracking without prior mixing with crude oil is
    exempt from the requirements of this Part, provided that the used oil
    contains less than one percent of the crude oil feed to any petroleum
    refining facility process unit at any given time. Prior to insertion into the
    petroleum refining process, the used oil is subject to the requirements of
    this Part.
     
    4) Except as provided in subsection (g)(5) of this Section, used oil that is
    introduced into a petroleum refining facility process after crude distillation
    or catalytic cracking is exempt from the requirements of this Part only if
    the used oil meets the specification of Section 739.111. Prior to insertion
    into the petroleum refining facility process, the used oil is subject to the
    requirements of this Part.

     
    1004
     
    5) Used oil that is incidentally captured by a hydrocarbon recovery system or
    wastewater treatment system as part of routine process operations at a
    petroleum refining facility and inserted into the petroleum refining facility
    process is exempt from the requirements of this Part. This exemption does
    not extend to used oil that is intentionally introduced into a hydrocarbon
    recovery system (e.g., by pouring collected used oil into the wastewater
    treatment system).
     
    6) Tank bottoms from stock tanks containing exempt mixtures of used oil
    and crude oil or natural gas liquids are exempt from the requirements of
    this Part.
     
    h) Used oil on vessels. Used oil produced on vessels from normal shipboard
    operations is not subject to this Part until it is transported ashore.
     
    i) Used oil containing PCBs. Used oil containing PCBs, as defined at 40 CFR 761.3
    (Definitions), incorporated by reference at 35 Ill. Adm. Code 720.111(b), at any
    concentration less than 50 ppm is subject to the requirements of this Part unless,
    because of dilution, it is regulated under federal 40 CFR 761 as a used oil
    containing PCBs at 50 ppm or greater. PCB-containing used oil subject to the
    requirements of this Part may also be subject to the prohibitions and requirements
    of 40 CFR 761, including 40 CFR 761.20(d) and (e). Used oil containing PCBs at
    concentrations of 50 ppm or greater is not subject to the requirements of this Part,
    but is subject to regulation under federal 40 CFR 761. No person may avoid these
    provisions by diluting used oil containing PCBs, unless otherwise specifically
    provided for in this Part or federal 40 CFR 761.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART C: STANDARDS FOR USED OIL GENERATORS
     
    Section 739.120 Applicability
     
    a) General. This Subpart C applies to all generators of used oil, except the following:
     
    1) Household “do-it-yourselfer” used oil generators. Household “do-it-
    yourselfer” used oil generators are not subject to regulation under this Part.
     
    2) Vessels. Vessels at sea or at port are not subject to this Subpart C. For
    purposes of this Subpart C, used oil produced on vessels from normal
    shipboard operations is considered to be generated at the time it is
    transported ashore. The owner or operator of the vessel and the persons
    removing or accepting used oil from the vessel are co-generators of the used
    oil and are both responsible for managing the waste in compliance with this
    Subpart C once the used oil is transported ashore. The co-generators may

     
    1005
    decide among themselves which party will fulfill the requirements of this
    Subpart C.
     
    3) Diesel fuel. Mixtures of used oil and diesel fuel mixed by the generator of
    the used oil for use in the generator’s own vehicles are not subject to this Part
    once the used oil and diesel fuel have been mixed. Prior to mixing, the used
    oil fuel is subject to the requirements of this Subpart C.
     
    4) Farmers. Farmers who generate an average of 25 gallons per month or less
    of used oil from vehicles or machinery used on the farm in a calendar year
    are not subject to the requirements of this Part.
     
    b) Other applicable provisions. A used oil generator that conducts any of the following
    activities is subject to the requirements of other applicable provisions of this Part, as
    indicated in subsections (b)(1) through (b)(5):
     
    1) A generator that transports used oil, except under the self-transport
    provisions of Section 739.124(a) and (b), must also comply with Subpart E
    of this Part.
     
    2) A generator that processes or re-refines used oil.
     
    A) Except as provided in subsection (b)(2)(B) of this Section, a
    generator that processes or re-refines used oil must also comply with
    Subpart F of this Part.
     
    B) A generator that performs the following activities is not a used oil
    processor, provided that the used oil is generated on-site and is not
    being sent off-site to a burner of on- or off-specification used oil fuel:
     
    i) Filtering, cleaning, or otherwise reconditioning used oil
    before returning it for reuse by the generator;
     
    ii) Separating used oil from wastewater generated on-site to
    make the wastewater acceptable for discharge or reuse
    pursuant to Section 402 or 307(b) for the federal Clean Water
    Act (33 USC 1317 or 1342), 40 CFR 403 through 499, or 35
    Ill. Adm. Code 310 or 309, governing the discharge of
    wastewaters;
     
    iii) Using oil mist collectors to remove small droplets of used oil
    from in-plant air to make plant air suitable for continued
    recirculation;
     
    iv) Draining or otherwise removing used oil from materials
    containing or otherwise contaminated with used oil in order

     
    1006
    to remove excessive oil to the extent possible pursuant to
    Section 739.110(c); or
     
    v) Filtering, separating, or otherwise reconditioning used oil
    before burning it in a space heater pursuant to Section
    739.123.
     
    3) A generator that burns off-specification used oil for energy recovery, except
    under the on-site space heater provisions of Section 739.123, must also
    comply with Subpart G of this Part.
     
    4) A generator that directs shipments of off-specification used oil from their
    facility to a used oil burner or first claims that used oil that is to be burned for
    energy recovery meets the used oil fuel specifications set forth in Section
    739.111 must also comply with Subpart H of this Part.
     
    5) A generator that disposes of used oil, including the use of used oil as a dust
    suppressant, must also comply with Subpart I of this Part.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 739.122 Used Oil Storage
     
    A used oil generator is subject to all applicable federal Spill Prevention, Control and
    Countermeasures (40 CFR 112) in addition to the requirements of this Subpart C. A used oil
    generator is also subject to the Underground Storage Tank (35 Ill. Adm. Code 731) standards for
    used oil stored in underground tanks whether or not the used oil exhibits any characteristics of
    hazardous waste, in addition to the requirements of this Subpart C.
     
    a) Storage units. A used oil generator may not store used oil in units other than tanks,
    containers, or units subject to regulation under 35 Ill. Adm. Code 724 or 725.
     
    b) Condition of units. The following must be true of containers and aboveground tanks
    used to store used oil at a generator facility:
     
    1) The containers must be in good condition (no severe rusting, apparent
    structural defects or deterioration); and
     
    2) The containers may not be leaking (no visible leaks).
     
    c) Labels.
     
    1) Containers and aboveground tanks used to store used oil at generator
    facilities must be labeled or marked clearly with the words “Used Oil.”
     
    2) Fill pipes used to transfer used oil into underground storage tanks at

     
    1007
    generator facilities must be labeled or marked clearly with the words “Used
    Oil.”
     
    d) Response to releases. Upon detection of a release of used oil to the environment that
    is not subject to the federal requirements of Subpart F of 40 CFR 280, Subpart F
    and which has occurred after October 4, 1996, a generator must perform the
    following cleanup steps:
     
    BOARD NOTE: Corresponding 40 CFR 279.22(d) applies to releases that
    “occurred after the effective date of the authorized used oil program for the State
    in which the release is located.” The Board adopted the used oil standards in
    docket R93-4 at 17 Ill. Reg. 20954, effective November 22, 1993. USEPA
    approved the Illinois standards at 61 Fed. Reg. 40521 (Aug. 5, 1996), effective
    October 4, 1996. The Board has interpreted “the effective date of the authorized
    used oil program” to mean the October 4, 1996 date of federal authorization of the
    Illinois program, and we substituted that date for the federal effective date
    language. Had USEPA written something like “the effective date of the used oil
    program in the authorized State in which the release is located,” the Board would
    have used the November 22, 1993 effective date of the Illinois used oil standards.
     
    1) Stop the release;
     
    2) Contain the released used oil;
     
    3) Properly clean up and manage the released used oil and other materials; and
     
    4) If necessary, repair or replace any leaking used oil storage containers or tanks
    prior to returning them to service.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART E: STANDARDS FOR USED OIL TRANSPORTER AND
    TRANSFER FACILITIES
     
    Section 739.140 Applicability
     
    a) General. Except as provided in subsections (a)(1) through (a)(4) of this Section, this
    Subpart E applies to all used oil transporters. A used oil transporter is a person that
    transports used oil, a person that collects used oil from more than one generator and
    transport the collected oil, and an owner or operator of a used oil transfer facility.
     
    1) This Subpart E does not apply to on-site transportation.
     
    2) This Subpart E does not apply to a generator that transports shipments of
    used oil totaling 55 gallons or less from the generator to a used oil collection
    center as specified in Section 739.124(a).

     
    1008
     
    3) This Subpart E does not apply to a generator that transports shipments of
    used oil totaling 55 gallons or less from the generator to a used oil
    aggregation point owned or operated by the same generator as specified in
    Section 739.124(b).
     
    4) This Subpart E does not apply to transportation of used oil from household
    do-it-yourselfers to a regulated used oil generator, collection center,
    aggregation point, processor, or burner subject to the requirements of this
    Part. Except as provided in subsections (a)(1) through (a)(3) of this Section,
    this Subpart E does, however, apply to transportation of collected household
    do-it-yourselfer used oil from regulated used oil generators, collection
    centers, aggregation points, or other facilities where household do-it-
    yourselfer used oil is collected.
     
    BOARD NOTE: A generator that qualifies for an exemption under Section
    739.124 may still be subject to the State’s special waste hauling permit
    requirements under Part 809.
     
    b) Imports and exports. A transporter that imports used oil from abroad or export used
    oil outside of the United States are subject to the requirements of this Subpart E from
    the time the used oil enters and until the time it exits the United States.
     
    c) Trucks used to transport hazardous waste. Unless trucks previously used to transport
    hazardous waste are emptied as described in 35 Ill. Adm. Code 721.107 prior to
    transporting used oil, the used oil is considered to have been mixed with the
    hazardous waste and must be managed as hazardous waste unless, under the
    provisions of Section 739.110(b), the hazardous waste and used oil mixture is
    determined not to be hazardous waste.
     
    d) Other applicable provisions. A used oil transporter that conducts the following
    activities are also subject to other applicable provisions of this Part as indicated in
    subsections (d)(1) through (d)(5) of this Section:
     
    1) A transporter that generates used oil must also comply with Subpart C of this
    Part;
     
    2) A transporter that processes or re-refines used oil, except as provided in
    Section 739.141, must also comply with Subpart F of this Part;
     
    3) A transporter that burns off-specification used oil for energy recovery must
    also comply with Subpart G of this Part;
     
    4) A transporter that directs shipments of off-specification used oil from its
    facility to a used oil burner or first claims that used oil that is to be burned for
    energy recovery meets the used oil fuel specifications set forth in Section

     
    1009
    739.111 must also comply with Subpart H of this Part; and
     
    5) A transporter that disposes of used oil, including the use of used oil as a
    dust suppressant, must also comply with Subpart I of this Part.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 739.143 Used Oil Transportation
     
    a) Deliveries. A used oil transporter must deliver all used oil received to one of the
    following:
     
    1) Another used oil transporter, provided that the transporter has obtained a
    USEPA identification number and an Illinois special waste identification
    number;
     
    2) A used oil processing facility that has obtained a USEPA identification
    number and an Illinois special waste identification number;
     
    3) An off-specification used oil burner facility that has obtained a USEPA
    identification number and an Illinois special waste identification number; or
     
    4) An on-specification used oil burner facility.
     
    b) U.S. DOT
    USDOT requirements. A used oil transporter must comply with all
    applicable USDOT requirements under the U.S. Department of Transportation in
    49 CFR 171 through 180. A person transporting used oil that meets the definition of
    a hazardous material in 49 CFR 171.8 (Definitions and Abbreviations),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b), must comply with all
    applicable U.S. Department of Transportation USDOT Hazardous Materials
    Regulations in 49 CFR 171 through (General Information, Regulations, and
    Definitions), 172 (Hazardous Materials Table, Special Provisions, Hazardous
    Materials Communications, Emergency Response Information, and Training
    Requirements), 173 (Shippers--General Requirements for Shipments and
    Packages), 174 (Carriage by Rail), 175 (Carriage by Aircraft), 176 (Carriage by
    Vessel), 177 (Carriage by Public Highway), 178 (Specifications for Packagings),
    179 (Specifications for Tank Cars), and 180 (Continuing Qualification and
    Maintenance of Packagings), incorporated by reference in 35 Ill. Adm. Code
    720.111(b).
     
    c) Used oil discharges.
     
    1) In the event of a discharge of used oil during transportation, the transporter
    must take appropriate immediate action to protect human health and the
    environment (e.g., notify local authorities, dike the discharge area).
     

     
    1010
    2) If a discharge of used oil occurs during transportation and an official (State or
    local government or a Federal Agency federal agency) acting within the
    scope of official responsibilities determines that immediate removal of the
    used oil is necessary to protect human health or the environment, that official
    may authorize the removal of the used oil by a transporter that does not have
    a USEPA identification number and an Illinois special waste identification
    number.
     
    3) An air, rail, highway, or water transporter that has discharged used oil must
    do the following:
     
    A) Give notice, if required by federal 49 CFR 171.15 (Immediate
    Notice of Certain Hazardous Materials Incidents), incorporated by
    reference in 35 Ill. Adm. Code 720.111(b), to the National
    Response Center (800-424-8802 or 202-426-2675); and
     
    B) Report in writing as required by federal 49 CFR 171.16 (Detailed
    Hazardous Materials Incident Reports), incorporated by reference
    in 35 Ill. Adm. Code 720.111(b), to the Director, Office of
    Hazardous Materials Regulations, Materials Transportation Bureau,
    Department of Transportation, Washington, DC 20590.
     
    4) A water transporter that has discharged used oil must give notice as required
    by federal 33 CFR 153.203, (Procedure for the Notice of Discharge),
    incorporated by reference in 35 Ill. Adm. Code 720.111(b).
     
    5) A transporter must clean up any used oil discharged that occurs during
    transportation or take such action as may be required or approved by federal,
    state, or local officials so that the used oil discharge no longer presents a
    hazard to human health or the environment.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 739.144 Rebuttable Presumption for Used Oil
     
    a) To ensure that used oil is not a hazardous waste under the rebuttable presumption of
    Section 739.110(b)(1)(ii), the used oil transporter must determine whether the total
    halogen content of used oil being transporter or stored at a transfer facility is above
    or below 1,000 ppm.
     
    b) The transporter must make this determination by the following means:
     
    1) Testing the used oil; or
     
    2) Applying knowledge of the halogen content of the used oil in light of the
    materials or processes used.

     
    1011
     
    c) If the used oil contains greater than or equal to 1,000 ppm total halogens, it is
    presumed to be a hazardous waste because it has been mixed with halogenated
    hazardous waste listed in Subpart D of 35 Ill. Adm. Code 721. The owner or
    operator may rebut the presumption by demonstrating that the used oil does not
    contain hazardous waste (for example, by using an analytical method from SW-846,
    incorporated by reference in 35 Ill. Adm. Code 720.111, to show showing that the
    used oil does not contain significant concentrations of halogenated hazardous
    constituents listed in Appendix H of 35 Ill. Adm. Code 721).
     
    1) The rebuttable presumption does not apply to metalworking oils and fluids
    containing chlorinated paraffins, if they are processed, through a tolling
    arrangement as described in Section 739.124(c), to reclaim metalworking oils
    and fluids. The presumption does apply to metalworking oils and fluids if
    such oils and fluids are recycled in any other manner, or disposed.
     
    2) The rebuttable presumption does not apply to used oils contaminated with
    chlorofluorocarbons (CFCs) removed from refrigeration units if the CFC are
    destined for reclamation. The rebuttable presumption does apply to used oils
    contaminated with CFCs that have been mixed with used oil from sources
    other than refrigeration units.
     
    d) Record retention. Records of analyses conducted or information used to comply
    with subsections (a), (b), and (c) of this Section must be maintained by the
    transporter for at least three years.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 739.145 Used Oil Storage at Transfer Facilities
     
    A used oil transporter is subject to all applicable Spill Prevention, Control and Countermeasures (40
    CFR 112) in addition to the requirements of this Subpart E. A used oil transporter is also subject to
    the Underground Storage Tank (35 Ill. Adm. Code 731) standards for used oil stored in underground
    tanks whether or not the used oil exhibits any characteristics of hazardous waste, in addition to the
    requirements of this Subpart.
     
    a) Applicability. This Section applies to used oil transfer facilities. Used oil transfer
    facilities are transportation-related facilities including loading docks, parking areas,
    storage areas, and other areas where shipments of used oil are held for more than 24
    hours during the normal course of transportation and not longer than 35 days. A
    transfer facility that store used oil for more than 35 days are subject to regulation
    under Subpart F.
     
    b) Storage units. An owner or operator of a used oil transfer facility may not store used
    oil in units other than tanks, containers, or units subject to regulation under 35 Ill.
    Adm. Code 724 or 725.

     
    1012
     
    c) Condition of units. The following must be true of containers and aboveground tanks
    used to store used oil at a transfer facility:
     
    1) The containers must be in good condition (no severe rusting, apparent
    structural defects or deterioration); and
     
    2) The containers may not be leaking (no visible leaks).
     
    d) Secondary containment for containers. Containers used to store used oil at a transfer
    facility must be equipped with a secondary containment system.
     
    1) The secondary containment system must consist of the following, at a
    minimum:
     
    A) Both of the following:
     
    i) Dikes, berms, or retaining walls; and
     
    ii) A floor. The floor must cover the entire area within the dikes,
    berms, or retaining walls; or
     
    B) An equivalent secondary containment system.
     
    2) The entire containment system, including walls and floors, must be
    sufficiently impervious to used oil to prevent any used oil released into the
    containment system from migrating out of the system to the soil,
    groundwater, or surface water.
     
    e) Secondary containment for existing aboveground tanks. Existing aboveground tanks
    used to store used oil at a transfer facility must be equipped with a secondary
    containment system.
     
    1) The secondary containment system must consist of the following, at a
    minimum:
     
    A) Both of the following:
     
    i) Dikes, berms, or retaining walls; and
     
    ii) A floor. The floor must cover the entire area within the dike,
    berm, or retaining wall except areas where existing portions
    of the tank meet the ground; or
     
    B) An equivalent secondary containment system.
     

     
    1013
    2) The entire containment system, including walls and floors, must be
    sufficiently impervious to used oil to prevent any used oil released into the
    containment system from migrating out of the system to the soil,
    groundwater, or surface water.
     
    f) Secondary containment for new aboveground tanks. New aboveground tanks used to
    store used oil at a transfer facility must be equipped with a secondary containment
    system.
     
    1) The secondary containment system must consist of the following, at a
    minimum:
     
    A) Both of the following:
     
    i) Dikes, berms, or retaining walls; and
     
    ii) A floor. The floor must cover the entire area within the dike,
    berm, or retaining wall; or
     
    B) An equivalent secondary containment system.
     
    2) The entire containment system, including walls and floors, must be
    sufficiently impervious to used oil to prevent any used oil released into the
    containment system from migrating out of the system to the soil,
    groundwater, or surface water.
     
    g) Labels.
     
    1) Containers and aboveground tanks used to store used oil at transfer facilities
    must be labeled or marked clearly with the words “Used Oil.”
     
    2) Fill pipes used to transfer used oil into underground storage tanks at transfer
    facilities must be labeled or marked clearly with the words “Used Oil.”
     
    h) Response to releases. Upon detection of a release of used oil to the environment that
    is not subject to the federal requirements of Subpart F of 40 CFR 280, Subpart F and
    which has occurred after October 4, 1996, an owner or operator of a transfer facility
    must perform the following cleanup steps:
     
    BOARD NOTE: Corresponding 40 CFR 279.45(h) applies to releases that
    “occurred after the effective date of the authorized used oil program for the State in
    which the release is located.” The Board adopted the used oil standards in docket
    R93-4 at 17 Ill. Reg. 20954, effective November 22, 1993. USEPA approved the
    Illinois standards at 61 Fed. Reg. 40521 (Aug. 5, 1996), effective October 4,
    1996. The Board has interpreted “the effective date of the authorized used oil
    program” to mean the October 4, 1996 date of federal authorization of the Illinois

     
    1014
    program, and we substituted that date for the federal effective date language. Had
    USEPA written something like “the effective date of the used oil program in the
    authorized State in which the release is located,” the Board would have used the
    November 22, 1993 effective date of the Illinois used oil standards.
     
    1) Stop the release;
     
    2) Contain the released used oil;
     
    3) Properly clean up and manage the released used oil and other materials; and
     
    4) If necessary, repair or replace any leaking used oil storage containers or tanks
    prior to returning them to service.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART F: STANDARDS FOR USED OIL PROCESSORS
     
    Section 739.150 Applicability
     
    a) The requirements of this Subpart F apply to owners and operators of facilities that
    process used oil. Processing means chemical or physical operations designed to
    produce from used oil, or to make used oil more amenable for production of, fuel
    oils, lubricants, or other used oil-derived products. Processing includes, but is not
    limited to the following: blending used oil with virgin petroleum products, blending
    used oils to meet the fuel specification, filtration, simple distillation, chemical or
    physical separation, and re-refining. The requirements of this Subpart F do not apply
    to the following:
     
    1) A transporter that conducts incidental processing operations that occur during
    the normal course of transportation, as provided in Section 739.141; or
     
    2) A burner that conducts incidental processing operations that occur during the
    normal course of used oil management prior to burning, as provided in
    Section 739.161(b).
     
    b) Other applicable provisions. A used oil processor that conducts the following
    activities are also subject to the requirements of other applicable provisions of this
    Part, as indicated in subsections (b)(1) through (b)(5) of this Section.
     
    1) A processor that generates used oil must also comply with Subpart C of this
    Part;
     
    2) A processor that transports used oil must also comply with Subpart E of this
    Part;
     

     
    1015
    3) Except as provided in subsections (b)(3)(A) and (b)(3)(B) of this Section, a
    processor that burns off-specification used oil for energy recovery must also
    comply with Subpart G of this Part. Processors burning used oil for energy
    recovery under the following conditions are not subject to Subpart G of this
    Part:
     
    A) The used oil is burned in an on-site space heater that meets the
    requirements of Section 739.123; or
     
    B) The used oil is burned for purposes of processing used oil, which is
    considered burning incidentally to used oil processing;
     
    4) A processor that directs shipments of off-specification used oil from their
    facility to a used oil burner or first claim that used oil that is to be burned for
    energy recovery meets the used oil fuel specifications set forth in Section
    739.111 must also comply with Subpart H of this Part; and
     
    5) A processors that disposes of used oil, including the use of used oil as a
    dust suppressant, also must comply with Subpart I of this Part.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 739.153 Rebuttable Presumption for Used Oil
     
    a) To ensure that used oil is not a hazardous waste under the rebuttable presumption of
    Section 739.110(b)(1)(ii), the owner or operator of a used oil processing facility must
    determine whether the total halogen content of used oil managed at the facility is
    above or below 1,000 ppm.
     
    b) The owner or operator must make this determination by the following means:
     
    1) Testing the used oil; or
     
    2) Applying knowledge of the halogen content of the used oil in light of the
    materials or processes used.
     
    c) If the used oil contains greater than or equal to 1,000 ppm total halogens, it is
    presumed to be a hazardous waste because it has been mixed with halogenated
    hazardous waste listed in Subpart D of 35 Ill. Adm. Code 721. The owner or
    operator may rebut the presumption by demonstrating that the used oil does not
    contain hazardous waste (for example, by using an analytical method from SW-846,
    incorporated by reference in 35 Ill. Adm. Code 720.111, to show showing that the
    used oil does not contain significant concentrations of halogenated hazardous
    constituents listed in Appendix H of 35 Ill. Adm. Code 721).
     
    1) The rebuttable presumption does not apply to metalworking oils and fluids

     
    1016
    containing chlorinated paraffins, if they are processed, through a tolling
    arrangement as described in Section 739.124(c), to reclaim metalworking oils
    and fluids. The presumption does apply to metalworking oils and fluids if
    such oils and fluids are recycled in any other manner, or disposed.
     
    2) The rebuttable presumption does not apply to used oils contaminated with
    chlorofluorocarbons (CFCs) removed from refrigeration units if the CFC are
    destined for reclamation. The rebuttable presumption does apply to used oils
    contaminated with CFCs that have been mixed with used oil from sources
    other than refrigeration units.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 739.154 Used Oil Management
     
    A used oil processor is subject to all applicable Spill Prevention, Control and Countermeasures (40
    CFR 112) in addition to the requirements of this Subpart F. A used oil processor or re-refiner is also
    subject to the Underground Storage Tank (35 Ill. Adm. Code 731) standards for used oil stored in
    underground tanks whether or not the used oil exhibits any characteristics of hazardous waste, in
    addition to the requirements of this Subpart F.
     
    a) Management units. A used oil processor may not store used oil in units other than
    tanks, containers, or units subject to regulation under 35 Ill. Adm. Code 724 or 725.
     
    b) Condition of units. The following must be true of containers and aboveground tanks
    used to store or process used oil at a processing facility:
     
    1) The containers must be in good condition (no severe rusting, apparent
    structural defects or deterioration); and
     
    2) The containers may not be leaking (no visible leaks).
     
    c) Secondary containment for containers. Containers used to store or process used oil
    at processing and re-refining facilities must be equipped with a secondary
    containment system.
     
    1) The secondary containment system must consist of the following, at a
    minimum:
     
    A) Both of the following:
     
    i) Dikes, berms, or retaining walls; and
     
    ii) A floor. The floor must cover the entire area within the dike,
    berm, or retaining wall; or
     

     
    1017
    B) An equivalent secondary containment system.
     
    2) The entire containment system, including walls and floor, must be
    sufficiently impervious to used oil to prevent any used oil released into the
    containment system from migrating out of the system to the soil,
    groundwater, or surface water.
     
    d) Secondary containment for existing aboveground tanks. Existing aboveground tanks
    used to store or process used oil at processing and re-refining facilities must be
    equipped with a secondary containment system.
     
    1) The secondary containment system must consist of the following, at a
    minimum:
     
    A) Both of the following:
     
    i) Dikes, berms, or retaining walls; and
     
    ii) A floor. The floor must cover the entire area within the dike,
    berm, or retaining wall except areas where existing portions
    of the tank meet the ground; or
     
    B) An equivalent secondary containment system.
     
    2) The entire containment system, including walls and floor, must be
    sufficiently impervious to used oil to prevent any used oil released into the
    containment system from migrating out of the system to the soil,
    groundwater, or surface water.
     
    e) Secondary containment for new aboveground tanks. New aboveground tanks used to
    store or process used oil at processing and re-refining facilities must be equipped
    with a secondary containment system.
     
    1) The secondary containment system must consist of the following, at a
    minimum:
     
    A) Both of the following:
     
    i) Dikes, berms, or retaining walls; and
     
    ii) A floor. The floor must cover the entire area within the dike,
    berm, or retaining wall; or
     
    B) An equivalent secondary containment system.
     
    2) The entire containment system, including walls and floor, must be

     
    1018
    sufficiently impervious to used oil to prevent any used oil released into the
    containment system from migrating out of the system to the soil,
    groundwater, or surface water.
     
    f) Labels.
     
    1) Containers and aboveground tanks used to store used oil at processing
    facilities must be labeled or marked clearly with the words “Used Oil.”
     
    2) Fill pipes used to transfer used oil into underground storage tanks at
    processing facilities must be labeled or marked clearly with the words “Used
    Oil.”
     
    g) Response to releases. Upon detection of a release of used oil to the environment that
    is not subject to the federal requirements of Subpart F of 40 CFR 280, Subpart F and
    which has occurred after October 4, 1996, a processor must perform the following
    cleanup steps:
     
    BOARD NOTE: Corresponding 40 CFR 279.54(g) applies to releases that
    “occurred after the effective date of the authorized used oil program for the State in
    which the release is located.” The Board adopted the used oil standards in docket
    R93-4 at 17 Ill. Reg. 20954, effective November 22, 1993. USEPA approved the
    Illinois standards at 61 Fed. Reg. 40521 (Aug. 5, 1996), effective October 4,
    1996. The Board has interpreted “the effective date of the authorized used oil
    program” to mean the October 4, 1996 date of federal authorization of the Illinois
    program, and we substituted that date for the federal effective date language. Had
    USEPA written something like “the effective date of the used oil program in the
    authorized State in which the release is located,” the Board would have used the
    November 22, 1993 effective date of the Illinois used oil standards.
     
    1) Stop the release;
     
    2) Contain the released used oil;
     
    3) Properly clean up and manage the released used oil and other materials; and
     
    4) If necessary, repair or replace any leaking used oil storage containers or tanks
    prior to returning them to service.
     
    h) Closure.
     
    1) Aboveground tanks. An owner or operator that stores or processes used oil
    in aboveground tanks must comply with the following requirements:
     
    A) At closure of a tank system, the owner or operator must remove or
    decontaminate used oil residues in tanks, contaminated containment

     
    1019
    system components, contaminated soils, and structures and
    equipment contaminated with used oil, and manage them as
    hazardous waste, unless the materials are not hazardous waste under
    this chapter.
     
    B) If the owner or operator demonstrates that not all contaminated soils
    can be practicably removed or decontaminated as required in
    subsection (h)(1)(A) of this Section, then the owner or operator must
    close the tank system and perform post-closure care in accordance
    with the closure and post-closure care requirements that apply to
    hazardous waste landfills (35 Ill. Adm. Code 725.410).
     
    2) Containers. An owner or operator that stores used oil in containers must
    comply with the following requirements:
     
    A) At closure, containers holding used oils or residues of used oil must
    be removed from the site;
     
    B) The owner or operator must remove or decontaminate used oil
    residues, contaminated containment system components,
    contaminated soils, and structures and equipment contaminated with
    used oil, and manage them as hazardous waste, unless the materials
    are not hazardous waste 35 Ill. Adm. Code 721.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART G: STANDARDS FOR USED OIL BURNERS THAT BURN OFF-
    SPECIFICATION USED OIL FOR ENERGY RECOVERY
     
    Section 739.160 Applicability
     
    a) General. The requirements of this Subpart G apply to used oil burners except as
    specified in subsections (a)(1) and (a)(2) of this Section. A used oil burner is a
    facility where used oil not meeting the specification requirements in Section 739.111
    is burned for energy recovery in devices identified in Section 739.161(a). Facilities
    burning used oil for energy recovery under the following conditions are not subject
    to this Subpart G:
     
    1) The used oil is burned by the generator in an on-site space heater under the
    provisions of Section 739.123; or
     
    2) The used oil is burned by a processor for purposes of processing used oil,
    which is considered burning incidentally to used oil processing.
     
    b) Other applicable provisions. A used oil burner that conducts the following activities
    is also subject to the requirements of other applicable provisions of this Part as

     
    1020
    indicated below.
     
    1) A burner that generates used oil must also comply with Subpart C of this
    Part;
     
    2) A burner that transports used oil must also comply with Subpart E of this
    Part;
     
    3) Except as provided in Section 739.161(b), a burner that processes or re-
    refines used oil must also comply with Subpart F of this Part;
     
    4) A burner that directs shipments of off-specification used oil from their
    facility to a used oil burner or first claim that used oil that is to be burned for
    energy recovery meets the used oil fuel specifications set forth in Section
    739.111 must also comply with Subpart H of this Part; and
     
    5) A burner that disposes of used oil, including the use of used oil as a dust
    suppressant, must comply with Subpart I of this Part.
     
    c) Specification fuel. This Subpart G does not apply to a person burning used oil that
    meets the used oil fuel specification of Section 739.111, provided that the burner
    complies with the requirements of Subpart H of this Part.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 739.163 Rebuttable Presumption for Used Oil
     
    a) To ensure that used oil managed at a used oil burner facility is not hazardous waste
    under the rebuttable presumption of Section 739.110(b)(1)(ii), a used oil burner must
    determine whether the total halogen content of used oil managed at the facility is
    above or below 1,000 ppm.
     
    b) The used oil burner must determine if the used oil contains above or below 1,000
    ppm total halogens by the following means:
     
    1) Testing the used oil;
     
    2) Applying knowledge of the halogen content of the used oil in light of the
    materials or processes used; or
     
    3) If the used oil has been received from a processor subject to regulation under
    Subpart F of this Part, using information provided by the processor.
     
    c) If the used oil contains greater than or equal to 1,000 ppm total halogens, it is
    presumed to be a hazardous waste because it has been mixed with halogenated
    hazardous waste listed in Subpart D of 35 Ill. Adm. Code 721. The owner or

     
    1021
    operator may rebut the presumption by demonstrating that the used oil does not
    contain hazardous waste (for example, by using an analytical method from SW-846,
    incorporated by reference in 35 Ill. Adm. Code 720.111, to show showing that the
    used oil does not contain significant concentrations of halogenated hazardous
    constituents listed in Appendix H of 35 Ill. Adm. Code 721).
     
    1) The rebuttable presumption does not apply to metalworking oils or fluids
    containing chlorinated paraffins, if they are processed, through a tolling
    arrangement as described in Section 739.124(c), to reclaim metalworking oils
    or fluids. The presumption does apply to metalworking oils or fluids if such
    oils and fluids are recycled in any other manner, or disposed.
     
    2) The rebuttable presumption does not apply to used oils contaminated with
    chlorofluorocarbons (CFCs) removed from refrigeration units where the
    CFCs are destined for reclamation. The rebuttable presumption does apply to
    used oils contaminated with CFCs that have been mixed with used oil from
    sources other than refrigeration units.
     
    d) Record retention. Records of analyses conducted or information used to comply
    with subsections (a), (b), and (c) of this Section must be maintained by the burner
    for at least three years.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 739.164 Used Oil Storage
     
    A used oil burner is subject to all applicable Spill Prevention, Control and Countermeasures (federal
    40 CFR 112) in addition to the requirements of this Subpart G. A used oil burner is also subject to
    the Underground Storage Tank (35 Ill. Adm. Code 731) standards for used oil stored in underground
    tanks whether or not the used oil exhibits any characteristics of hazardous waste, in addition to the
    requirements of this Subpart G.
     
    a) Storage units. A used oil burner may not store used oil in units other than tanks,
    containers, or units subject to regulation under 35 Ill. Adm. Code 724 or 725.
     
    b) Condition of units. The following must be true of containers and aboveground tanks
    used to store used oil at a burner facility:
     
    1) The containers must be in good condition (no severe rusting, apparent
    structural defects or deterioration); and
     
    2) The containers may not be leaking (no visible leaks).
     
    c) Secondary containment for containers. Containers used to store used oil at a burner
    facility must be equipped with a secondary containment system.
     

     
    1022
    1) The secondary containment system must consist of the following, at a
    minimum:
     
    A) Dikes, berms, or retaining walls; and
     
    B) A floor. The floor must cover the entire area within the dike, berm,
    or retaining wall.
     
    2) The entire containment system, including walls and floor, must be
    sufficiently impervious to used oil to prevent any used oil released into the
    containment system from migrating out of the system to the soil,
    groundwater, or surface water.
     
    d) Secondary containment for existing aboveground tanks. Existing aboveground tanks
    used to store used oil at burner facilities must be equipped with a secondary
    containment system.
     
    1) The secondary containment system must consist of the following, at a
    minimum:
     
    A) Both of the following:
     
    i) Dikes, berms, or retaining walls; and
     
    ii) A floor. The floor must cover the entire area within the dike,
    berm, or retaining wall except areas where existing portions
    of the tank meet the ground; or
     
    B) An equivalent secondary containment system.
     
    2) The entire containment system, including walls and floor, must be
    sufficiently impervious to used oil to prevent any used oil released into the
    containment system from migrating out of the system to the soil,
    groundwater, or surface water.
     
    e) Secondary containment for existing aboveground tanks. A new aboveground tank
    used to store used oil at burner facilities must be equipped with a secondary
    containment system.
     
    1) The secondary containment system must consist of the following, at a
    minimum:
     
    A) Both of the following:
     
    i) Dikes, berms, or retaining walls; and
     

     
    1023
    ii) A floor. The floor must cover the entire area within the dike,
    berm, or retaining wall; or
     
    B) An equivalent secondary containment system.
     
    2) The entire containment system, including walls and floor, must be
    sufficiently impervious to used oil to prevent any used oil released into the
    containment system from migrating out of the system to the soil,
    groundwater, or surface water.
     
    f) Labels.
     
    1) A container or aboveground tank used to store used oil at a burner facility
    must be labeled or marked clearly with the words “Used Oil.”
     
    2) Fill pipes used to transfer used oil into underground storage tanks at burner
    facilities must be labeled or marked clearly with the words “Used Oil.”
     
    g) Response to releases. Upon detection of a release of used oil to the environment that
    is not subject to the federal requirements of Subpart F of 40 CFR 280, Subpart F and
    which has occurred after October 4, 1996, a burner must perform the following
    cleanup steps:
     
    BOARD NOTE: Corresponding 40 CFR 279.64(g) applies to releases that
    “occurred after the effective date of the authorized used oil program for the State in
    which the release is located.” The Board adopted the used oil standards in docket
    R93-4 at 17 Ill. Reg. 20954, effective November 22, 1993. USEPA approved the
    Illinois standards at 61 Fed. Reg. 40521 (Aug. 5, 1996), effective October 4,
    1996. The Board has interpreted “the effective date of the authorized used oil
    program” to mean the October 4, 1996 date of federal authorization of the Illinois
    program, and we substituted that date for the federal effective date language. Had
    USEPA written something like “the effective date of the used oil program in the
    authorized State in which the release is located,” the Board would have used the
    November 22, 1993 effective date of the Illinois used oil standards.
     
    1) Stop the release;
     
    2) Contain the released used oil;
     
    3) Properly clean up and manage the released used oil and other materials; and
     
    4) If necessary, repair or replace any leaking used oil storage containers or tanks
    prior to returning them to service.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    1024
    SUBPART H: STANDARDS FOR USED OIL FUEL MARKETERS
     
    Section 739.175 Notices
     
    a) Certification. Before a used oil generator, transporter, or processor directs the first
    shipment of off-specification used oil fuel to a burner, it must obtain a one-time
    written and signed notice from the burner certifying the following:
     
    1) That the burner has notified USEPA stating the location and general
    description of used oil management activities; and
     
    2) That the burner will burn the off-specification used oil only in an industrial
    furnace or boiler identified in Section 739.161(a).
     
    b) Certification retention. The certification described in subsection (a) of this Section
    must be maintained for three years from the date the last shipment of off-
    specification used oil is shipped to the burner.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART I: STANDARDS FOR USE AS A DUST SUPPRESSANT
    DISPOSAL OF USED OIL
     
    Section 739.180 Applicability
     
    The requirements of this Subpart I apply to all used oils that cannot be recycled and are therefore
    being disposed of.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 739.181 Disposal
     
    a) Disposal of hazardous used oils. A used oil that is identified as a hazardous waste
    and which cannot be recycled in accordance with this Part must be managed in
    accordance with the hazardous waste management requirements of 35 Ill. Adm.
    Code 703, 720 through 726, and 728.
     
    b) Disposal of nonhazardous used oils. A used oil that is not a hazardous waste and
    cannot be recycled under this Part must be disposed of in accordance with the
    requirements of 35 Ill. Adm. Code 807 through 815 and 40 CFR 257 and 258.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     

     
    1025
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER i: SOLID WASTE AND SPECIAL WASTE HAULING
     
    PART 810
    SOLID WASTE DISPOSAL: GENERAL PROVISIONS
    Section
    810.101 Scope and Applicability
    810.102 Severability
    810.103 Definitions
    810.104 Incorporations by Reference
     
    AUTHORITY: Implementing Sections 5, 21, 21.1, 22, 22.17, and 28.1 and authorized by
    Section 27 of the Environmental Protection Act [415 ILCS 5/5, 21, 21.1, 22, 22.17, 28.1 and 27].
     
    SOURCE: Adopted in R88-7 at 14 Ill. Reg. 15838, effective September 18, 1990; amended in
    R93-10 at 18 Ill. Reg. 1268, effective January 13, 1994; amended in R90-26 at 18 Ill. Reg.
    12457, effective August 1, 1994; amended in R95-9 at 19 Ill. Reg. 14427, effective September
    29, 1995; amended in R96-1 at 20 Ill. Reg. 11985, effective August 15, 1996; amended in R97-
    20 at 21 Ill. Reg. 15825, effective November 25, 1997; amended in R04-5/R04-15 at 28 Ill. Reg.
    9090, effective June 18, 2004; amended in R05-1 at 29 Ill. Reg. 5028, effective March 22, 2005;
    amended in R06-5/R06-6/R06-7 at 30 Ill. Reg. ________, effective ______________________.
     
    Section 810.104 Incorporations by Reference
     
    a) The Board incorporates the following material by reference:
     
    1) Code of Federal Regulations:
     
    40 CFR 141.40 (1997) (2005).
     
    40 CFR 258.Appendix II (1997) (2005), as corrected at 70 Fed.
    Reg. 44150 (August 1, 2005).
     
    2) American Institute of Certified Public Accountants, 1211 Avenue of the
    Americas, New York NY 10036:
     
    Auditing Standards--Current Text, August 1, 1990 Edition.
     
    3) ASTM. American Society for Testing and Materials, 1976 Race Street,
    Philadelphia PA 19103 215-299-5585:
     
    Method D2234-76, Test Method for Collection of Gross Samples
    of Coal.
     

     
    1026
    Method D3987-85, Standard Test Method for Shake Extraction of
    Solid Waste with Water.
     
    4) GASB. Government Accounting Standards Board, 401 Merritt 7, P.O.
    Box 5116, Norwalk CT 06856-5116:
     
    Statement 18.
     
    5) U.S. Army Corps of Engineers, Publication Department, 2803 52nd Ave.,
    Hyattville, Maryland 20781, 301-394-0081:
     
    Engineering Manual 1110-2-1906 Appendix VII, Falling-Head
    Permeability Cylinder (1986).
     
    6) U.S. Government Printing Office, Washington, D.C. 20402, Ph: 202-783-
    3238:
     
    “Test Methods for Evaluating Solid Waste, Physical/Chemical
    methods, Methods,” EPA Publication USEPA publication number
    EPA-530/SW-846 (Third Edition, 1986; Revision 6, January
    2005), as amended by Update I (November, 1990): (July 1992), II
    (September 1994), IIA (August 1993), IIB (January 1995), III
    (December 1996), IIIA (April 1998), and IIIB (November 2004)
    (document number 955-001-00000-1).
     
    b) This incorporation includes no later amendments or editions.
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER i: SOLID WASTE AND SPECIAL WASTE HAULING
     
    PART 811
    STANDARDS FOR NEW SOLID WASTE LANDFILLS
     
    SUBPART A: GENERAL STANDARDS FOR ALL LANDFILLS
    Section
    811.101 Scope and Applicability
    811.102 Location Standards
    811.103 Surface Water Drainage
    811.104 Survey Controls
    811.105 Compaction
    811.106 Daily Cover
    811.107 Operating Standards

     
    1027
    811.108 Salvaging
    811.109 Boundary Control
    811.110 Closure and Written Closure Plan
    811.111 Postclosure Maintenance
    811.112 Recordkeeping Requirements for MSWLF Units
     
    SUBPART B: INERT WASTE LANDFILLS
    Section
    811.201 Scope and Applicability
    811.202 Determination of Contaminated Leachate
    811.203 Design Period
    811.204 Final Cover
    811.205 Final Slope and Stabilization
    811.206 Leachate Sampling
    811.207 Load Checking
     
    SUBPART C: PUTRESCIBLE AND CHEMICAL WASTE LANDFILLS
    Section
    811.301 Scope and Applicability
    811.302 Facility Location
    811.303 Design Period
    811.304 Foundation and Mass Stability Analysis
    811.305 Foundation Construction
    811.306 Liner Systems
    811.307 Leachate Drainage System
    811.308 Leachate Collection System
    811.309 Leachate Treatment and Disposal System
    811.310 Landfill Gas Monitoring
    811.311 Landfill Gas Management System
    811.312 Landfill Gas Processing and Disposal System
    811.313 Intermediate Cover
    811.314 Final Cover System
    811.315 Hydrogeological Site Investigations
    811.316 Plugging and Sealing of Drill Holes
    811.317 Groundwater Impact Assessment
    811.318 Design, Construction, and Operation of Groundwater Monitoring Systems
    811.319 Groundwater Monitoring Programs
    811.320 Groundwater Quality Standards
    811.321 Waste Placement
    811.322 Final Slope and Stabilization
    811.323 Load Checking Program
    811.324 Corrective Action Measures for MSWLF Units
    811.325 Selection of remedy for MSWLF Units
    811.326 Implementation of the corrective action program at MSWLF Units
     

     
    1028
    SUBPART D: MANAGEMENT OF SPECIAL WASTES AT LANDFILLS
    Section
    811.401 Scope and Applicability
    811.402 Notice to Generators and Transporters
    811.403 Special Waste Manifests
    811.404 Identification Record
    811.405 Recordkeeping Requirements
    811.406 Procedures for Excluding Regulated Hazardous Wastes
     
    SUBPART E: CONSTRUCTION QUALITY ASSURANCE PROGRAMS
    Section
    811.501 Scope and Applicability
    811.502 Duties and Qualifications of Key Personnel
    811.503 Inspection Activities
    811.504 Sampling Requirements
    811.505 Documentation
    811.506 Foundations and Subbases
    811.507 Compacted Earth Liners
    811.508 Geomembranes
    811.509 Leachate Collection Systems
     
    SUBPART G: FINANCIAL ASSURANCE
    Section
    811.700 Scope, Applicability and Definitions
    811.701 Upgrading Financial Assurance
    811.702 Release of Financial Institution
    811.703 Application of Proceeds and Appeals
    811.704 Closure and Postclosure Care Cost Estimates
    811.705 Revision of Cost Estimate
    811.706 Mechanisms for Financial Assurance
    811.707 Use of Multiple Financial Mechanisms
    811.708 Use of a Financial Mechanism for Multiple Sites
    811.709 Trust Fund for Unrelated Sites
    811.710 Trust Fund
    811.711 Surety Bond Guaranteeing Payment
    811.712 Surety Bond Guaranteeing Performance
    811.713 Letter of Credit
    811.714 Closure Insurance
    811.715 Self-Insurance for Non-commercial Sites
    811.716 Local Government Financial Test
    811.717 Local Government Guarantee
    811.718 Discounting
    811.719 Corporate Financial Test
    811.720 Corporate Guarantee
     
    811.Appendix A Financial Assurance Forms

     
    1029
    Illustration A Trust Agreement
    Illustration B Certificate of Acknowledgment
    Illustration C Forfeiture Bond
    Illustration D Performance Bond
    Illustration E Irrevocable Standby Letter of Credit
    Illustration F Certificate of Insurance for Closure and/or Postclosure Care
    Illustration G Operator’s Bond Without Surety
    Illustration H Operator’s Bond With Parent Surety
    Illustration I Letter from Chief Financial Officer
     
    811.Appendix B Section-by-Section correlation between the Standards of the RCRA
    Subtitle D MSWLF regulations and the Board’s nonhazardous waste
    landfill regulations.
     
    AUTHORITY: Implementing Sections 5, 21, 21.1, 22, 22.17 and 28.1 and authorized by Section
    27 of the Environmental Protection Act [415 ILCS 5/5, 21, 21.1, 22, 22.17, 28.1, and 27].
     
    SOURCE: Adopted in R88-7 at 14 Ill. Reg. 15861, effective September 18, 1990; amended in
    R92-19 at 17 Ill. Reg. 12413, effective July 19, 1993; amended in R93-10 at 18 Ill. Reg. 1308,
    effective January 13, 1994; expedited correction at 18 Ill. Reg. 7504, effective July 19, 1993;
    amended in R90-26 at 18 Ill. Reg. 12481, effective August 1, 1994; amended in R95-13 at 19 Ill.
    Reg. 12257, effective August 15, 1995; amended in R96-1 at 20 Ill. Reg. 12000, effective
    August 15, 1996; amended in R97-20 at 21 Ill. Reg.15831, effective November 25, 1997;
    amended in R98-9 at 22 Ill. Reg.11491, effective June 23, 1998; amended in R99-1 at 23 Ill.
    Reg. 2794, effective February 17, 1999; amended in R98-29 at 23 Ill. Reg.6880, effective July 1,
    1999; amended in R04-5/R04-15 at 28 Ill. Reg. 9107, effective June 18, 2004; amended in R05-1
    at 29 Ill. Reg. 5044, effective March 22, 2005; amended in R06-5/R06-6/R06-7 at 30 Ill. Reg.
    ________, effective ______________________.
     
    SUBPART A:
     
    GENERAL STANDARDS FOR ALL LANDFILLS
     
    Section 811.107 Operating Standards
     
    a) Phasing of Operations.
     
    1) Waste must be placed in a manner and at such a rate that mass stability is
    provided during all phases of operation. Mass stability means that the
    mass of waste deposited will not undergo settling or slope failure that
    interrupts operations at the facility or causes damage to any of the various
    landfill operations or structures, such as the liner, leachate or drainage
    collection system, gas collection system, or monitoring system.
     
    2) The phasing of operations at the facility must be designed in such a way as
    to allow the sequential construction, filling, and closure of discrete units
    or parts of units.
     

     
    1030
    3) The operator must design and sequence the waste placement operation in
    each discrete unit or parts of units, in conjunction with the overall
    operations of the facility, so as to shorten the operational phase and allow
    wastes to be built up to the planned final grade.
     
    b) Size and Slope of Working Face.
     
    1) The working face of the unit must be no larger than is necessary, based on
    the terrain and equipment used in waste placement, to conduct operations
    in a safe and efficient manner.
     
    2) The slopes of the working face area must be no steeper than two to one
    (horizontal to vertical) unless the waste is stable at steeper slopes.
     
    c) Equipment.
     
    Equipment must be maintained and available for use at the facility during all
    hours of operation, so as to achieve and maintain compliance with the
    requirements of this Part.
     
    d) Utilities.
     
    All utilities, including but no limited to heat, lights, power and communications
    equipment, necessary for safe operation in compliance with the requirements of
    this Part must be available at the facility at all times.
     
    e) Maintenance.
     
    The operator must maintain and operate all systems and related appurtenances and
    structures in a manner that facilitates proper operations in compliance with this
    Part.
     
    f) Open Burning.
     
    Open burning is prohibited, except in accordance with 35 Ill. Adm. Code 200
    through 245.
     
    g) Dust Control.
     
    The operator must implement methods for controlling dust, so as to prevent wind
    dispersal of particulate matter.
     
    h) Noise Control.
     
    The facility must be designed, constructed, and maintained to minimize the level
    of equipment noise audible outside the facility. The facility must not cause or

     
    1031
    contribute to a violation of 35 Ill. Adm. Code 900 through 905 or of Section 24 of
    the Act [415 ILCS 5/24].
     
    i) Vector Control.
     
    The operator must implement measures to control the population of disease and
    nuisance vectors.
     
    j) Fire Protection.
     
    The operator must institute fire protection measures including, but not limited to,
    maintaining a supply of water onsite and radio or telephone access to the nearest
    fire department.
     
    k) Litter Control.
     
    1) The operator must patrol the facility daily to check for litter accumulation.
    All litter must be collected and placed in the fill or in a secure, covered
    container for later disposal.
     
    2) The facility must not accept solid waste from vehicles that do not utilize
    devices such as covers or tarpaulins to control litter, unless the nature of
    the solid waste load is such that it cannot cause any litter during its
    transportation to the facility.
     
    l) Mud Tracking. The facility must implement methods, such as use of wheel
    washing units, to prevent tracking of mud by hauling vehicles onto public
    roadways.
     
    m) Liquids Restrictions for MSWLF Units.
     
    1) Bulk or noncontainerized liquid waste may not be placed in MSWLF
    units, unless one of the following conditions is true:
     
    A) The waste is household waste other than septic waste;
     
    B) The waste is leachate or gas condensate derived from the MSWLF
    unit and the MSWLF unit, whether it is a new or existing MSWLF
    unit or lateral expansion, is designed with a composite liner and
    leachate collection system that complies with the requirements of
    Sections 811.306 through 811.309; or
     
    C) The Agency has issued an RD&D permit pursuant to 35 Ill. Adm.
    Code 813.112(a)(2) that allows the placement of noncontainerized
    liquids in the landfill, and that permit is in effect.
     

     
    1032
    2) Containers holding liquid waste may not be placed in an MSWLF unit,
    unless one of the following conditions is true:
     
    A) The container is a small container similar in size to that normally
    found in household waste;
     
    B) The container is designed to hold liquids for use other than
    storage; or
     
    C) The waste is household waste.
     
    3) For purposes of this Section, the following definitions apply:
     
    A) “Liquid waste” means any waste material that is determined to
    contain “free liquids,” as defined by Method 9095 9095B (Paint
    Filter Liquids Test) (Revision 2, November 2004), as described in
    “Test Methods for Evaluating Solid Wastes, Physical/Chemical
    Methods,” (USEPA Pub. No. USEPA publication number
    EPA530/SW-846), incorporated by reference in 35 Ill. Adm. Code
    810.104.
     
    B) “Gas condensate” means the liquid generated as a result of gas
    recovery processes at the MSWLF unit.
     
    BOARD NOTE: Subsections (m)(1) through (m)(3) are derived from 40 CFR
    258.28 (2004) (2005). Subsection (m)(1)(C) of this Section relating to RD&D
    permits is derived from 40 CFR 258.4(a)(2) (2004) (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    SUBPART G: FINANCIAL ASSURANCE
     
    Section 811.710 Trust Fund
     
    a) An owner or operator may satisfy the requirements of this Subpart G by
    establishing a trust fund which that conforms to the requirements of this Section
    and submitting an original signed duplicate of the trust agreement to the Agency.
     
    b) The trustee shall must be an entity which that has the authority to act as a trustee
    and of whom either of the following is true:
     
    1) Whose
    It is an entity whose trust operations are examined by the Illinois
    Commissioner of Banks and Trust Companies pursuant to the Illinois
    Banking Act (Ill. Rev. Stat. 1991, ch. 17, pars. 301 et seq. [205 ILCS 5/1
    et seq.]); or
     

     
    1033
    2) Who
    It is an entity that complies with the Corporate Fiduciary Act (Ill.
    Rev. Stat. 1991, ch. 17, pars. 1551-1 et seq. [205 ILCS 620/1-1 et seq.]).
     
    c) The trust agreement must be on the forms specified in Appendix A, Illustration A
    of this Part, and the trust agreement must be accompanied by a formal
    certification of acknowledgement, on the form specified in Appendix A,
    Illustration B of this Part.
     
    d) Payments into the trust:.
     
    1) For closure and post-closure care:.
     
    A) The owner or operator shall must make a payment into the trust
    fund each year during the pay-in period.
     
    B) The pay-in period is the number of years remaining until the
    assumed closure date.
     
    C) Annual payments are determined by the following formula:
     
    Annual payment = (CE-CV)/Y
     
    Annual payment =
    Y
    CV
    CE
      
     
    where the variables are defined as follows:
     
    CE = Current cost estimate,
     
    CV = Current value of the trust fund, and
     
    Y = Number of years remaining in the pay in
    period.
     
    D) The owner or operator shall must make the first annual payment
    prior to the initial receipt of waste for disposal. The owner or
    operator shall must also, prior to such initial receipt of waste,
    submit to the Agency a receipt from the trustee for the first annual
    payment.
     
    E) Subsequent annual payments must be made no later than 30 days
    after each anniversary of the first payment.
     
    F) The owner or operator may accelerate payments into the trust fund,
    or may deposit the full amount of the current cost estimate at the

     
    1034
    time the fund is established.
     
    G) An owner or operator required to provide additional financial
    assurance for an increase in the cost estimate because of an
    amendment to this Subchapter i may provide such additional
    financial assurance pursuant to this subsection (d)(1)(G). The
    owner or operator may provide the increase by contributing to a
    new or existing trust fund pursuant to this Section. Subsection
    (d)(2) of this Section notwithstanding, the pay-in period for such
    additional financial assurance shall must be not less than three
    years.
     
    2) For corrective action at MSWLF units:.
     
    A) The owner or operator shall must make payments into the trust
    fund annually over one-half of the estimated length of the
    corrective action program in the case of corrective action for
    known releases. This period is referred to as the pay-in period.
     
    B) The owner or operator shall must make the first payment into the
    trust fund equal to at least one-half of the current cost estimate for
    corrective action divided by the number of years in the corrective
    action pay-in period, as defined in subsection (d)(2)(A) of this
    section Section. The amount of subsequent payments must be
    determined by the following formula:
     
    Next payment = (RB-CV)/Y
     
    Next payment =
    Y
    CV
    RB
     
     
    where the variables are defined as follows:
     
    RB = Most recent estimate of the required trust fund
    balance for corrective action (i.e., the total costs
    that will be incurred during the second half of the
    corrective action period);,
     
    CV = Current value of the trust fund;, and
     
    Y = Number of years remaining in the pay-in
    period.
     
    C) The owner or operator shall must make the initial payment into the
    trust fund no later than 120 days after the remedy has been selected

     
    1035
    in accordance with the requirements of Section 811.325.
     
    Board Note. Changes to subsection BOARD NOTE. Subsection (d) of this
    Section are is partly derived from 40 CFR 258.74 (a)(2), (a)(4), and (a)(5) (1992)
    (2005).
     
    e) The trustee shall must evaluate the trust fund annually, as of the day the trust was
    created or on such earlier date as may be provided in the agreement. The trustee
    shall must notify the owner or operator and the Agency of the value within 30
    days after the evaluation date.
     
    f) If the owner or operator of a MSWLF unit establishes a trust fund after having
    used one or more alternative mechanisms specified in this Subpart G, the initial
    payment into the trust fund must be at least the amount that the fund would
    contain if the trust fund were established initially and annual payments made
    according to the specifications of this Section.
     
    Board Note. Subsection (f) of this Section is derived from 40 CFR 258.74 (a)(6)
    (1992) (2005).
     
    g) Release of excess funds:.
     
    1) If the value of the financial assurance is greater than the total amount of
    the current cost estimate, the owner or operator may submit a written
    request to the Agency for a release of the amount in excess of the current
    cost estimate.
     
    2) Within 60 days after receiving a request from the owner or operator for a
    release of funds, the Agency shall must instruct the trustee to the owner or
    operator to release such funds as the Agency specifies in writing to be in
    excess of the current cost estimate.
     
    h) Reimbursement for closure, postclosure care, and corrective action expenses:.
     
    1) After initiating closure or corrective action, an owner or operator, or any
    other person authorized to perform closure, or postclosure care, or
    corrective action, may request reimbursement for closure, or postclosure
    care, or corrective action expenditures, by submitting itemized bills to the
    Agency.
     
    2) Within 60 days after receiving the itemized bills for closure, or
    postclosure care, activities or correction action activities, the Agency shall
    must determine whether the expenditures are in accordance with the
    closure, or postclosure care, or corrective action plan. The Agency shall
    must instruct the trustee to make reimbursement in such amounts as the
    Agency specifies in writing as expenditures in accordance with the

     
    1036
    closure, or postclosure care, or corrective action plan.
     
    3) If the Agency determines, based on such information as is available to it,
    that the cost of closure and postclosure care or corrective action will be
    greater than the value of the trust fund, it shall must withhold
    reimbursement of such amounts as it determines are necessary to preserve
    the fund in order to accomplish closure and postclosure care or corrective
    action until it determines that the owner or operator is no longer required
    to maintain financial assurance for closure and postclosure care or
    corrective action. In the event the fund is inadequate to pay all claims, the
    Agency shall must pay claims according to the following priorities:
     
    A) Persons with whom the Agency has contracted to perform closure,
    or postclosure care, or corrective action activities (first priority);
     
    B) Persons who have completed closure, or postclosure care, or
    corrective action authorized by the Agency (second priority);
     
    C) Persons who have completed work which that furthered the
    closure, or postclosure care, or corrective action (third priority);
     
    D) The owner or operator and related business entities (last priority).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    Section 811.716 Local Government Financial Test
     
    A unit of local government owner or operator that satisfies the requirements of subsections (a)
    through (c) of this Section may demonstrate financial assurance up to the amount specified in
    subsection (d) of this Section.
     
    a) Financial component.
     
    1) The unit of local government owner or operator shall must satisfy
    subsection (a)(1)(A) or (a)(1)(B) of this Section, as applicable:
     
    A) If the owner or operator has outstanding, rated, general obligation
    bonds that are not secured by insurance, a letter of credit, or other
    collateral or guarantee, it must have a current rating of Aaa, Aa, A,
    or Baa, as issued by Moody's, or AAA, AA, A, or BBB, as issued
    by Standard and Poor's, on all such general obligation bonds; or
     
    B) The owner or operator shall must satisfy each of the following
    financial ratios based on the owner or operator's most recent
    audited annual financial statement:
     

     
    1037
    i) A ratio of cash plus marketable securities to total
    expenditures greater than or equal to 0.05; and
     
    ii) A ratio of annual debt service to total expenditures less
    than or equal to 0.20.
     
    2) The unit of local government owner or operator shall must prepare its
    financial statements in conformity with Generally Accepted Accounting
    Principles for governments and have its financial statements audited by an
    independent certified public accountant or the Comptroller of the State of
    Illinois pursuant to the Governmental Account Audit Act [50 ILCS 310].
     
    3) A unit of local government is not eligible to assure its obligations under
    this Section if any of the following is true:
     
    A) It is currently in default on any outstanding general obligation
    bonds;
     
    B) It has any outstanding general obligation bonds rated lower than
    Baa as issued by Moody's or BBB as issued by Standard and
    Poor's;
     
    C) It operated at a deficit equal to five percent or more of total annual
    revenue in each of the past two fiscal years; or
     
    D) It receives an adverse opinion, disclaimer of opinion, or other
    qualified opinion from the independent certified public accountant
    or the Comptroller of the State of Illinois pursuant to the
    Governmental Account Audit Act [50 ILCS 310] auditing its
    financial statement as required under subsection (a)(2) of this
    Section. However, the Agency shall must evaluate qualified
    opinions on a case-by-case basis and allow use of the financial test
    in cases where the Agency deems the qualification insufficient to
    warrant disallowance of use of the test.
     
    4) The following terms Terms used in this Section are defined as follows:
     
    “Cash plus marketable securities” is all the cash plus marketable
    securities held by the unit of local government on the last day of a
    fiscal year, excluding cash and marketable securities designated to
    satisfy past obligations such as pensions.
     
    “Debt service” is the amount of principal and interest due on a loan
    in a given time period, typically the current year.
     
    “Deficit” equals total annual revenues minus total annual

     
    1038
    expenditures.
     
    “Total revenues” include revenues from all taxes and fees but does
    not include the proceeds from borrowing or asset sales, excluding
    revenue from funds managed by a unit of local government on
    behalf of a specific third party.
     
    “Total expenditures” include all expenditures excluding capital
    outlays and debt repayment.
     
    b) Public notice component.
     
    1) The unit of local government owner or operator shall must place a
    reference to the closure and post-closure care costs assured through the
    financial test into its next comprehensive annual financial report (CAFR)
    after November 27, 1997, or prior to the initial receipt of waste at the
    facility, whichever is later.
     
    2) Disclosure must include the nature and source of closure and post-closure
    care requirements, the reported liability at the balance sheet date, the
    estimated total closure and post-closure care cost remaining to be
    recognized, the percentage of landfill capacity used to date, and the
    estimated landfill life in years.
     
    3) A reference to corrective action costs must be placed in the CAFR not
    later than 120 days after the corrective action remedy has been selected in
    accordance with the requirements of Sections 811.319(d) and 811.325.
     
    4) For the first year the financial test is used to assure costs at a particular
    facility, the reference may instead be placed in the operating record until
    issuance of the next available CAFR if timing does not permit the
    reference to be incorporated into the most recently issued CAFR or
    budget.
     
    5) For closure and post-closure costs, conformance with Government
    Accounting Standards Board Statement 18, incorporated by reference in
    35 Ill. Adm. Code 810.104, assures compliance with this public notice
    component.
     
    c) Recordkeeping and reporting requirements.
     
    1) The unit of local government owner or operator must place the following
    items in the facility's operating record:
     
    A) A letter signed by the unit of local government's chief financial
    officer that provides the following information:

     
    1039
     
    i) Lists
    It lists all the current cost estimates covered by a
    financial test, as described in subsection (d) of this Section;
     
    ii) Provides
    It provides evidence and certifies that the unit of
    local government meets the conditions of subsections
    (a)(1), (a)(2), and (a)(3) of this Section; and
     
    iii) Certifies
    It certifies that the unit of local government meets
    the conditions of subsections (b) and (f)(4) (d) of this
    Section.
     
    B) The unit of local government's independently audited year-end
    financial statements for the latest fiscal year (except for a unit of
    local government where audits are required every two years, where
    unaudited statements may be used in years when audits are not
    required), including the unqualified opinion of the auditor who
    must be an independent certified public accountant (CPA) or the
    Comptroller of the State of Illinois pursuant to the Governmental
    Account Audit Act [50 ILCS 310].
     
    C) A report to the unit of local government from the unit of local
    government's independent CPA or the Comptroller of the State of
    Illinois pursuant to the Governmental Account Audit Act [50 ILCS
    310] based on performing an agreed upon procedures engagement
    relative to the financial ratios required by subsection (a)(1)(B) of
    this Section, if applicable, and the requirements of subsections
    (a)(2), (a)(3)(C), and (a)(3)(D) of this Section. The CPA or
    Comptroller's report should state the procedures performed and the
    CPA or Comptroller's findings; and
     
    D) A copy of the comprehensive annual financial report (CAFR) used
    to comply with subsection (b) of this Section or certification that
    the requirements of General Accounting Standards Board
    Statement 18, incorporated by reference in Section 810.104, have
    been met.
     
    2) The items required in subsection (c)(1) of this Section must be placed in
    the facility operating record as follows:
     
    A) In the case of closure and post-closure care, either before
    November 27, 1997, or prior to the initial receipt of waste at the
    facility, whichever is later; or
     
    B) In the case of corrective action, not later than 120 days after the
    corrective action remedy is selected in accordance with the

     
    1040
    requirements of Sections 811.319(d) and 811.325.
     
    3) After the initial placement of the items in the facility operating record, the
    unit of local government owner or operator shall must update the
    information and place the updated information in the operating record
    within 180 days following the close of the owner or operator's fiscal year.
     
    4) The unit of local government owner or operator is no longer required to
    meet the requirements of subsection (c) of this Section when either of the
    following occurs:
     
    A) The owner or operator substitutes alternative financial assurance as
    specified in this Section; or
     
    B) The owner or operator is released from the requirements of this
    Section in accordance with Section 811.326(g), 811.702(b), or
    811.704(j) or (k)(6).
     
    5) A unit of local government must satisfy the requirements of the financial
    test at the close of each fiscal year. If the unit of local government owner
    or operator no longer meets the requirements of the local government
    financial test it shall must, within 210 days following the close of the
    owner or operator's fiscal year, obtain alternative financial assurance that
    meets the requirements of this Subpart, place the required submissions for
    that assurance in the operating record, and notify the Agency that the
    owner or operator no longer meets the criteria of the financial test and that
    alternative assurance has been obtained.
     
    6) The Agency, based on a reasonable belief that the unit of local
    government owner or operator may no longer meet the requirements of the
    local government financial test, may require additional reports of financial
    condition from the unit of local government at any time. If the Agency
    determines, on the basis of such reports or other information, that the
    owner or operator no longer meets the requirements of the local
    government financial test, the unit of local government must provide
    alternative financial assurance in accordance with this Subpart.
     
    d) Calculation of Costs to be Be Assured. The portion of the closure, post-closure,
    and corrective action costs that an owner or operator may assure under this
    Section is determined as follows:
     
    1) If the unit of local government owner or operator does not assure other
    environmental obligations through a financial test, it may assure closure,
    post-closure, and corrective action costs that equal up to 43 percent of the
    unit of local government's total annual revenue.
     

     
    1041
    2) If the unit of local government assures other environmental obligations
    through a financial test, including those associated with UIC facilities
    under 35 Ill. Adm. Code 704.213, petroleum underground storage tank
    facilities under 40 CFR 280, PCB storage facilities under 40 CFR 761, and
    hazardous waste treatment, storage, and disposal facilities under 35 Ill.
    Adm. Code 724 and 725, it must add those costs to the closure, post-
    closure, and corrective action costs it seeks to assure under this Section.
    The total that may be assured must not exceed 43 percent of the unit of
    local government's total annual revenue.
     
    3) The owner or operator must obtain an alternative financial assurance
    instrument for those costs that exceed the limits set in subsections (d)(1)
    and (d)(2) of this Section.
     
    BOARD NOTE: Derived from 40 CFR 258.74(f), added at 61 Fed. Reg. 60327 (Nov. 27, 1996)
    (2005).
     
    (Source: Amended at 30 Ill. Reg. ________, effective ______________________)
     
    IT IS SO ORDERED.
     
    I, Dorothy M. Gunn, Clerk of the Illinois Pollution Control Board, certify that the Board
    adopted the above order on October 20, 2005, by a vote of 5-0.
     
    Dorothy M. Gunn, Clerk
    Illinois Pollution Control Board

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