ILLINOIS POLLUTION CONTROL BOARD
    March 2, 2000
    IN THE MATTER OF:
    )
    )
    RCRA SUBTITLE C UPDATE, USEPA
    )
    R00-13
    AMENDMENTS (July 1, 1999, through
    )
    (Identical-in-Substance
    December 31, 1999)
    )
    Rulemaking - Land)
    Proposed Rule. Proposal for Public Comment.
    ORDER OF THE BOARD (by E.Z. Kezelis):
    Under Sections 7.2 and 22.4(a) of the Environmental Protection Act (Act) (415 ILCS
    5/7.2 and 22.4(a) (1998)), the Board proposes amendments to the Illinois regulations that are
    “identical in substance” to hazardous waste regulations that the United States Environmental
    Protection Agency (USEPA) adopted to implement Subtitle C of the federal Resource
    Conservation and Recovery Act of 1976 (RCRA Subtitle C) (42 U.S.C. §§ 6921
    et seq
    .
    (1998)). The nominal timeframe of this docket includes federal RCRA Subtitle C amendments
    that USEPA adopted in the period July 1, 1999, through December 31, 1999.
    Sections 7.2 and 22.4(a) provide for quick adoption of regulations that are identical in
    substance to federal regulations that USEPA adopts to implement Sections 3001 through 3005
    of RCRA (42 U.S.C. §§ 6921-6925 (1998)). Section 22.4(a) also provides that Title VII of the
    Act and Section 5 of the Administrative Procedure Act (APA) (5 ILCS 100/5-35 and 5-40
    (1998)) do not apply to the Board’s adoption of identical-in-substance regulations. The federal
    RCRA Subtitle C regulations are found at 40 C.F.R. 260 through 266, 268, 270, 271, 273,
    and 279.
    This proposed order is supported by a proposed opinion that the Board also adopts
    today. The Board will cause the proposed amendments to be published in the
    Illinois Register
    and will receive public comments for 45 days after the date of publication.
    IT IS SO ORDERED.
    I, Dorothy M. Gunn, Clerk of the Illinois Pollution Control Board, do hereby certify
    that the above order was adopted on the 2nd day of March 2000 by a vote of 6-0.
    Dorothy M. Gunn, Clerk
    Illinois Pollution Control Board

    2
    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
    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

    3
    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
    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
    703.221 Emergency Permits
    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

    4
    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
    Why This Subpart Is Written in a Special Format
    703.301
    General Information
    703.302
    Applying for a RAP
    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
    703.Appendix A
    Classification of Permit Modifications
    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 R82-19, 53 PCB 131, 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

    5
    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.
    ________, effective ______________________.
    SUBPART B: PROHIBITIONS
    Section 703.123
    Specific Exclusions from Permit Program
    The following persons are among those who that are not required to obtain a RCRA permit:
    a)
    Generators who that accumulate hazardous waste on-site for less than the time
    periods provided in 35 Ill. Adm. Code 722.134;
    b)
    Farmers who that dispose of hazardous waste pesticides from their own use as
    provided in 35 Ill. Adm. Code 722.170;
    c)
    Persons who that own or operate facilities solely for the treatment, storage or
    disposal of hazardous waste excluded from regulations under this Part by 35 Ill.
    Adm. Code 721.104 or 721.105 (small generator exemption);
    d)
    Owners or operators of totally enclosed treatment facilities as defined in 35 Ill.
    Adm. Code 720.110;
    e)
    Owners and operators of elementary neutralization units or wastewater treatment
    units as defined in 35 Ill. Adm. Code 720.110;
    f)
    Transporters 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;
    g)
    Persons adding absorbent material to waste in a container (as defined in 35 Ill.

    6
    Adm. Code 720.110) and persons adding waste to absorbent material in a
    container, provided that these actions occur at the time waste is first placed in the
    container; and 35 Ill. Adm. Code 724.117(b), 724.271 and 724.272 are
    complied with; and
    h)
    A universal waste handler or universal waste transporter (as defined in 35 Ill.
    Adm. Code 720.110) that manages the wastes listed below. Such a handler or
    transporter is subject to regulation under 35 Ill. Adm. Code 733.
    1)
    Batteries, as described in 35 Ill. Adm. Code 733.102;
    2)
    Pesticides, as described in 35 Ill. Adm. Code 733.103;
    3)
    Thermostats, as described in 35 Ill. Adm. Code 733.104; and
    4)
    Mercury-containing lampsLamps, as described in 35 Ill. Adm. Code
    733.107 733.105.
    BOARD NOTE: Derived from 40 CFR 270.1(c)(2) (1996) (1999), as amended at 64 Fed.
    Reg. 36488 (July 6, 1999). Subsection (h)(4) of this Section was added pursuant to Section
    22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19, 1997).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    SUBPART C: AUTHORIZATION BY RULE AND INTERIM STATUS
    Section 703.161
    Enforceable Document for Post-Closure Care
    a)
    An owner or operator may obtain an enforceable document containing alternative
    requirements for post-closure care that imposes the requirements of 35 Ill. Adm.
    Code 725.221. “Enforceable document containing alternative requirements” or
    “other enforceable document,” as used in this Part and in 35 Ill. Adm. Code 724
    and 725, means an order of the Board, an Agency-approved plan, or an order of
    a court of competent jurisdiction that meets the requirements of subsection (b) of
    this Section. An “enforceable document containing alternative requirements” or
    “other enforceable document,” may also mean an order of USEPA (such as
    pursuant to section 3008(h) of RCRA, 42 USC 6928(h), or under section 106 of
    the federal Comprehensive Environmental Response, Compensation and Liability
    Act, 42 USC 9606).
    BOARD NOTE: Derived from 40 CFR 270.1(c)(7), as added at 63 Fed. Reg.
    56735 (Oct. 22, 1998) (1999).

    7
    b)
    Any alternative requirements issued under this Section or established to satisfy
    the requirements of 35 Ill. Adm. Code 724.190(f), 724.210(c), 724.240(d),
    725.190(f), 725.210(c), or 725.240(d) shall be embodied in a document that is
    enforceable and subject to appropriate compliance orders and civil penalties
    under Titles VIII and XII of the Act.
    BOARD NOTE: Derived from 40 CFR 271.16(e), as added at 63 Fed. Reg.
    56735 (Oct. 22, 1998) (1999).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    SUBPART D: APPLICATIONS
    Section 703.183
    General Information
    The following information is required in the Part B application for all HWM facilities, except as
    35 Ill. Adm. Code 724.101 provides otherwise:
    a)
    A general description of the facility;
    b)
    Chemical and physical analyses of the hazardous wastes and hazardous debris to
    be handled at the facility. At a minimum, these analyses must contain all the
    information which must be known to treat, store, or dispose of the wastes
    properly in accordance with 35 Ill. Adm. Code 724;
    c)
    A copy of the waste analysis plan required by 35 Ill. Adm. Code 724.113(b)
    and, if applicable, 35 Ill. Adm. Code 724.113(c);
    d)
    A description of the security procedures and equipment required by 35 Ill. Adm.
    Code 724.114, or a justification demonstrating the reasons for requesting a
    waiver of this requirement;
    e)
    A copy of the general inspection schedule required by 35 Ill. Adm. Code
    724.115(b). Include where applicable, as part of the inspection schedule,
    specific requirements in 35 Ill. Adm. Code 724.274, 724.293(i), 724.295,
    724.326, 724.354, 724.373, 724.403, 724.702, 724.933, 724.952, 724.953,
    724.958, 724.984, 724.985, 724.986, and 724.988;
    f)
    A justification of any request for a waiver of the preparedness and prevention
    requirements of 35 Ill. Adm. Code 724.Subpart C;
    g)
    A copy of the contingency plan required by 35 Ill. Adm. Code 724.Subpart D;

    8
    BOARD NOTE: Include, where applicable, as part of the contingency plan,
    specific requirements in 35 Ill. Adm. Code 724.200 and 724.327.
    Corresponding 40 CFR 270.14(b)(7) refers to the requirements of 40 CFR
    264.255 (corresponding with 35 Ill. Adm. Code 724.355), marked “reserved”
    by USEPA.
    h)
    A description of procedures, structures, or equipment used at the facility to:
    1)
    Prevent hazards in unloading operations (for example, ramps, or special
    forklifts);
    2)
    Prevent runoff from hazardous waste handling areas to other areas of the
    facility or environment, or to prevent flooding (for example, berms,
    dikes, or trenches);
    3)
    Prevent contamination of water supplies;
    4)
    Mitigate effects of equipment failure and power outages;
    5)
    Prevent undue exposure of personnel to hazardous waste (for example,
    protective clothing); and
    6)
    Prevent releases to the atmosphere;
    i)
    A description of precautions to prevent accidental ignition or reaction of
    ignitable, reactive, or incompatible wastes, as required to demonstrate
    compliance with 35 Ill. Adm. Code 724.117, including documentation
    demonstrating compliance with 35 Ill. Adm. Code 724.117(c);
    j)
    Traffic A description of the area traffic pattern, the estimated traffic volume
    (number and types of vehicles), and area traffic control (for example, show turns
    across traffic lanes and stacking lanes, if appropriate); describe a description of
    access road surfacing and load bearing capacity; and show an indication of traffic
    control signals;
    k)
    Facility location information, as required by Section 703.184;
    l)
    An outline of both the introductory and continuing training programs by the
    owner or operator to prepare persons to operate or maintain the HWM facility in
    a safe manner, as required to demonstrate compliance with 35 Ill. Adm. Code
    724.116. A brief description of how training will be designed to meet actual job
    tasks in accordance with requirements in 35 Ill. Adm. Code 724.116(a)(3);
    m)
    A copy of the closure plan and, where applicable, the post-closure plan required
    by 35 Ill. Adm. Code 724.212, 724.218, and 724.297. Include where

    9
    applicable, as part of the plans, specific requirements in 35 Ill. Adm. Code
    724.278, 724.297, 724.328, 724.358, 724.380, 724.410, 724.451, 724.701, and
    724.703;
    n)
    For hazardous waste disposal units that have been closed, documentation that
    notices required under 35 Ill. Adm. Code 724.219 have been filed;
    o)
    The most recent closure cost estimate for the facility, prepared in accordance
    with 35 Ill. Adm. Code 724.242, and a copy of the documentation required to
    demonstrate financial assurance under 35 Ill. Adm. Code 724.243. For a new
    facility, a copy of the required documentation may be submitted 60 days prior to
    the initial receipt of hazardous wastes, if it is later than the submission of the Part
    B permit application;
    p)
    Where applicable, the most recent post-closure cost estimate for the facility,
    prepared in accordance with 35 Ill. Adm. Code 724.244, plus a copy of the
    documentation required to demonstrate financial assurance under 35 Ill. Adm.
    Code 724.245. For a new facility, a copy of the required documentation may be
    submitted 60 days prior to the initial receipt of hazardous wastes, if it is later
    than the submission of the Part B permit application;
    q)
    Where applicable, a copy of the insurance policy or other documentation which
    comprises compliance with the requirements of 35 Ill. Adm. Code 724.247. For
    a new facility, documentation showing the amount of insurance meeting the
    specification of 35 Ill. Adm. Code 724.247(a) and, if applicable, 35 Ill. Adm.
    Code 724.247(b) that the owner or operator plans to have in effect before initial
    receipt of hazardous waste for treatment, storage, or disposal. A request for an
    alternative level of required coverage for a new or existing facility may be
    submitted as specified in 35 Ill. Adm. Code 724.247(c);
    r)
    This subsection corresponds with 40 CFR 270.14(b)(18), pertaining to state
    financial mechanisms that do not apply in Illinois. This statement maintains
    structural parity with the federal regulations.
    s)
    A topographic map showing a distance of 1000 feet around the facility at a scale
    of 2.5 centimeters (1 inch) equal to not more than 61.0 meters (200 feet).
    Contours must be shown on the map. The contour interval must be sufficient to
    clearly show the pattern of surface water flow in the vicinity of and from each
    operational unit of the facility. For example, contours with an interval of 1.5
    meters (5 feet), if relief is greater than 6.1 meters (20 feet), or an interval of 0.6
    meters (2 feet), if relief is less than 6.1 meters (20 feet). Owners and operators
    of HWM facilities located in mountainous areas shall use larger contour intervals
    to adequately show topographic profiles of facilities. The map must clearly show
    the following:

    10
    1)
    Map scale and date;
    2)
    100-year floodplain area;
    3)
    Surface waters including intermittent streams;
    4)
    Surrounding land uses (e.g., residential, commercial, agricultural,
    recreational, etc.);
    5)
    A wind rose (i.e., prevailing windspeed and direction);
    6)
    Orientation of the map (north arrow);
    7)
    Legal boundaries of the HWM facility site;
    8)
    Access control (e.g., fences, gates, etc.);
    9)
    Injection and withdrawal wells both on-site and off-site;
    10)
    Buildings; treatment, storage, or disposal operations; or other structures
    (e.g., recreation areas, runoff control systems, access and internal roads,
    storm, sanitary and process sewage systems, loading and unloading areas,
    fire control facilities, etc.);
    11)
    Barriers for drainage or flood control;
    12)
    Location of operational units within the HWM facility site, where
    hazardous waste is (or will be) treated, stored, or disposed (include
    equipment cleanup areas);
    BOARD NOTE: For large HWM facilities, the Agency shall allow the
    use of other scales on a case by case case-by-case basis.
    t)
    Applicants shall submit such information as the Agency determines is necessary
    for it to determine whether to issue a permit and what conditions to impose in
    any permit issued;
    u)
    For land disposal facilities, if a case-by-case extension has been approved under
    35 Ill. Adm. Code 728.105 or if a petition has been approved under 35 Ill.
    Adm. Code 728.106, a copy of the notice of approval of the extension or of
    approval of the petition is required; and
    v)
    A summary of the pre-application meeting, along with a list of attendees and
    their addresses, and copies of any written comments or materials submitted at the
    meeting, as required under 35 Ill. Adm. Code 703.191(c).

    11
    BOARD NOTE: Derived from 40 CFR 270.14(b) (1998) (1999).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 703.205
    Incinerators that Burn Hazardous Waste
    For facilities that incinerate hazardous waste, except as 35 Ill. Adm. Code 724.440 provides
    and subsection (e) of this Section provide otherwise, the applicant must fulfill the requirements
    of subsections (a), (b), or (c) below 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):
    1)
    Documentation that the waste is listed as a hazardous waste in 35 Ill.
    Adm. Code 721.Subpart D solely because it is ignitable (Hazard Code I),
    corrosive (Hazard Code C), or both; or
    2)
    Documentation that the waste is listed as a hazardous waste in 35 Ill.
    Adm. Code 721.Subpart D 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; or
    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 35
    Ill. Adm. Code 721.Subpart C; 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;
    or
    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.; or

    12
    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:
    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 35
    Ill. Adm. Code 721.Appendix H that are present in the waste to
    be burned, except that the applicant need not analyze for
    constituents listed in 35 Ill. Adm. Code 721.Appendix H 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
    analytical techniques specified in “Test Methods for the Evaluation
    of Solid Waste, Physical/Chemical Methods”, U.S. EPA USEPA
    Publication SW-846, as incorporated by reference at 35 Ill. Adm.
    Code 720.111 and Section 703.110, or their equivalent;
    D)
    An approximate quantification of the hazardous constituents
    identified in the waste, within the precision produced by the
    analytical methods specified in “Test Methods for the Evaluation
    of Solid Waste, Physical/Chemical Methods”, U.S. EPA USEPA
    Publication SW-846, as incorporated by reference at 35 Ill. Adm.
    Code 720.111 and Section 703.110;
    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:
    A)
    Manufacturer’s name and model number of incinerator;

    13
    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 system(s) systems;
    G)
    Stack gas monitoring and pollution control monitoring system;
    H)
    Nozzle and burner design;
    I)
    Construction materials;
    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
    include those items listed in subsection (c)(1) above 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
    burn(s) burns including:
    A)
    Sampling and analysis techniques used to calculate performance
    standards in 35 Ill. Adm. Code 724.443;

    14
    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);
    C)
    The certification and results required by subsection (b) above of
    this Section;
    6)
    The expected incinerator operation information to demonstrate compliance
    with 35 Ill. Adm. Code 724.443 and 724.445 including:
    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;
    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
    whether the incinerator meets the requirements of 35 Ill. Adm. Code
    724.Subpart 0 and what conditions are required by that Subpart and
    Section 39(d) of the Environmental Protection Act;

    15
    8)
    Waste analysis data, including that submitted in subsection (c)(1) above 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 shall approve a permit application without a trial burn if it finds
    that:
    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 40 CFR 63, subpart EEE, incorporated
    by reference in 35 Ill. Adm. Code 720.111 (i.e., by conducting a comprehensive
    performance test and submitting a Notification of Compliance), the requirements
    of this Section do not apply. 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).
    BOARD NOTE: Derived from 40 CFR 270.19 (1992) (1999), as amended at 58 64 Fed. Reg.
    46051 (Aug. 31, 1993) 53076 (September 30, 1999).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 703.208
    Boilers and Industrial Furnaces Burning Hazardous Waste
    When an 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 40 CFR part 63, subpart EEE, incorporated by
    reference in 35 Ill. Adm. Code 720.111 (i.e., by conducting a comprehensive performance test
    and submitting a Notification of Compliance), the requirements of this Section do not apply.
    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).

    16
    a)
    Trial burns.
    1)
    General. Except as provided below, owners and operators that are
    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 shall conduct a trial burn to demonstrate
    conformance with those standards and shall submit a trial burn plan or the
    results of a trial burn, including all required determinations, in
    accordance with Section 703.232.
    A)
    Under subsection (a)(2) through (a)(5) below 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) below 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 shall submit documentation that the
    boiler operates under the special operating requirements provided
    by 35 Ill. Adm. Code 726.210.
    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 shall
    submit:
    i)
    Documentation that the device is operated in conformance

    17
    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 35 Ill. Adm. Code 721.Appendix H, 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 analytical techniques
    specified in Test Methods for the Evaluation of Solid
    Waste, Physical/Chemical Methods, (incorporated by
    reference, see 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) above
    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) above of this Section
    using modeling procedures prescribed by 35 Ill. Adm.
    Code 726.206(h). The Agency shall review the emission
    modeling conducted by the applicant to determine
    conformance with these procedures. The Agency shall
    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) above of this Section quantified in
    conformance with subsection (a)(2)(B)(iv) above of this
    Section does not exceed the allowable ambient level
    established in 35 Ill. Adm. Code 726.Appendix D or E.
    The acceptable ambient concentration for emitted
    constituents for which a specific reference air
    concentration has not been established in 35 Ill. Adm.

    18
    Code 726.Appendix D or risk-specific does doses has not
    been established in 35 Ill. Adm. Code 726.Appendix E is
    0.1 micrograms per cubic meter, as noted in the footnote
    to 35 Ill. Adm. Code 726.Appendix D.
    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 shall submit:
    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

    19
    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 shall
    submit documentation supporting conformance with subsections (a)(2)(B)
    and (a)(3) above 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 total chlorine and chloride provided by 35 Ill. Adm. Code
    726.207(b)(1) and (e) that control emissions by HCl and chlorine gas
    without requiring a trial burn, the owner or operator shall submit:
    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

    20
    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 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 shall 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 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 shall be
    submitted:
    A)
    For a waiver from any trial burn:
    i)
    A description and analysis of the hazardous waste to be
    burned compared with the hazardous waste for which data

    21
    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.
    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 which demonstrate compliance
    with the DRE performance standard in 35 Ill. Adm. Code
    726.204(a). This analysis should specify the constituents in 35 Ill.
    Adm. Code 721.Appendix H 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.
    Owners and operators of industrial furnaces requesting an alternative HC limit
    under 35 Ill. Adm. Code 726.204(f) shall 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
    information on the type and flow rate of all feedstreams, point of

    22
    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 fuel(s) fuels and destruction
    of hydrocarbon emissions from nonfuel sources;
    4)
    Trial burn plan to:
    A)
    Demonstrate that flue gas HC (and CO) concentrations when
    burning hazardous waste do not exceed the baseline HC (and CO)
    level; and
    B)
    Identify, in conformance with Section 703.232(d), the types and
    concentrations of organic compounds listed in 35 Ill. Adm. Code
    721.Appendix H 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.
    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 shall 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 shall provide such other
    information that the Agency finds necessary to achieve the purposes of this
    subsection.
    d)
    Automatic waste feed cutoff system. Owners and operators shall submit
    information describing the automatic waste feed cutoff system, including any pre-
    alarm systems that may be used.
    e)
    Direct transfer. Owners and operators that use direct transfer operations to feed
    hazardous waste from transport vehicles (containers, as defined in 35 Ill. Adm.

    23
    Code 726.211) directly to the boiler or industrial furnace shall submit
    information supporting conformance with the standards for direct transfer
    provided by 35 Ill. Adm. Code 726.211.
    f)
    Residues. Owners and operators that claim that their residues are excluded from
    regulation under the provisions of 35 Ill. Adm. Code 726.212 shall submit
    information adequate to demonstrate conformance with those provisions.
    BOARD NOTE: Derived from 40 CFR 270.22 (1992) (1999), as amended at 64 Fed. Reg.
    53077 (September 30, 1999).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    SUBPART E: SHORT TERM AND PHASED PERMITS
    Section 703.221 Emergency Permits
    Section 703.220 Emergency Permits
    a)
    Notwithstanding any other provision of this Part or 35 Ill. Adm. Code 702 or
    705, in the event that the Agency finds an imminent and substantial
    endangerment to human health or the environment the Agency may issue a
    temporary emergency permit:
    1)
    To a non-permitted facility to allow treatment, storage or disposal of
    hazardous waste; or
    2)
    To a permitted facility to allow treatment, storage or disposal of a
    hazardous waste not covered by an effective permit.
    b)
    This emergency permit must comply with all of the following requirements:
    1)
    May be oral or written. If oral, it must be followed in five days by a
    written emergency permit;.
    2)
    Shall not exceed 90 days in duration;.
    3)
    Shall clearly specify the hazardous wastes to be received and the manner
    and location of their treatment, storage or disposal;.
    4)
    May be terminated by the Agency at any time without process if it
    determines that termination is appropriate to protect human health and the

    24
    environment;.
    5)
    Shall be accompanied by a public notice published under 35 Ill. Adm.
    Code 705.162 including:
    A)
    Name and address of the office granting the emergency
    authorization;
    B)
    Name and location of the permitted HWM facility;
    C)
    A brief description of the wastes involved;
    D)
    A brief description of the action authorized and reasons for
    authorizing it; and
    E)
    Duration of the emergency permit; and.
    6)
    Shall incorporate, to the extent possible and not inconsistent with the
    emergency situation, all applicable requirements of this Part and 35 Ill.
    Adm. Code 724.
    7)
    Emergency permits which that would authorize actions not in compliance
    with Board rules, other than procedural requirements, require a variance
    or provisional variance pursuant to Title IX of the Environmental
    Protection Act and 35 Ill. Adm. Code 104.
    BOARD NOTE: Derived from 40 CFR 270.61 (1996) (1999).
    (Source: Former Section 703.221 renumbered and amended at 24 Ill. Reg. ________, effective
    ______________________)
    Secction 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 40 CFR part 63, subpart EEE, incorporated by reference in 35 Ill. Adm. Code 720.111
    (i.e., by conducting a comprehensive performance test and submitting a Notification of
    Compliance), the requirements of Sections 703.221 through 703.225 do not apply.
    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 (1999), as added at 64 Fed. Reg.
    53077 (September 30, 1999).

    25
    (Source: Added at 24 Ill. Reg. ________, effective ______________________)
    Section 703.232
    Permits for Boilers and Industrial Furnaces Burning Hazardous Waste
    When an owner or operator of a cement or lightweight aggregate kiln demonstrates compliance
    with the air emission standards and limitations in of the federal National Emission Standards for
    Hazardous Air Pollutants (NESHAPs) of in 40 CFR part 63, subpart EEE, incorporated by
    reference in 35 Ill. Adm. Code 720.111 (i.e., by conducting a comprehensive performance test
    and submitting a Notification of Compliance), the requirements of this Section do not apply.
    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. Owners and operators of new boilers and industrial furnaces (those not
    operating under the interim status standards of 35 Ill. Adm. Code 726.203) are
    subject to subsections (b) through (f) of this Section. Boilers and industrial
    furnaces operating under the interim status standards of 35 Ill. Adm. Code
    726.203 are subject to subsection (g) of this Section.
    b)
    Permit operating periods for new boilers and industrial furnaces. 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 shall
    establish permit conditions in the Pretrial Burn Period pretrial burn
    period, including but not limited to allowable hazardous waste feed rates
    and operating conditions. The Agency shall 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 most be modified to
    reflect the extension according to Section 703.280 et seq.
    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 shall 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

    26
    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 shall
    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 shall 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 shall establish the operating requirements
    most likely to ensure compliance with the performance standards
    of 35 Ill. Adm. Code 726.204 through 726.207 based on the
    Agency’s engineering judgment.
    B)
    Applicants shall 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 shall 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 shall
    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
    shall make any necessary modifications to the operating requirements to
    ensure compliance with the performance standards. The permit
    modification must proceed according to Section 703.280 et seq.

    27
    c)
    Requirements for trial burn plans. The trial burn plan must include the following
    information. The Agency, in reviewing the trial burn plan, shall 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.
    1)
    An analysis of each feed stream, including hazardous waste, other fuels,
    and industrial furnace feed stocks, as fired, that includes:
    A)
    Heating value, levels of antimony, arsenic, barium, beryllium,
    cadmium, chromium, lead, mercury, silver, thallium, total
    chlorine/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:
    A)
    An identification of any hazardous organic constituents listed in 35
    Ill. Adm. Code 721.Appendix H that are present in the feed
    stream, except that the applicant need not analyze for constituents
    listed in 721.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
    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 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:
    A)
    Manufacturer’s name and model number of the boiler or industrial

    28
    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 system(s)
    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
    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 date(s) 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 and the criteria in subsection (b)(2) of this Section.

    29
    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 shall approve a trial burn plan if the Agency finds that:
    A)
    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)
    The trial burn itself will not present an imminent hazard to human
    health and the environment;
    C)
    The trial burn will help the Agency to determine operating
    requirements to be specified under 35 Ill. Adm. Code 726.102(e);
    and
    D)
    The information sought in the trial burn cannot reasonably be
    developed through other means.
    3)
    The Agency shall 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.
    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:
    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

    30
    completion of the trial burn.
    4)
    The applicant shall 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 shall, 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 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 shall 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
    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 35 Ill. Adm. Code 721.Subpart D, the hazardous waste organic
    constituent(s) constituents identified in 35 Ill. Adm. Code 721.Appendix G 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 shall 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):
    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

    31
    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/Chlorine 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/Chlorine 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/chloride
    chlorine and chloride;
    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, applicants owning or operating existing
    boilers or industrial furnaces operated under the interim status standards of 35 Ill.

    32
    Adm. Code 726.203 shall either prepare and submit a trial burn plan and
    perform a trial burn in accordance with the requirements of the Section or submit
    other information as specified in Section 703.208(a)(6). The Agency shall
    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 shall 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 shall 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 (1996) (1999), as amended at 64 Fed. Reg.
    53077 (September 30, 1999).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    SUBPART H: REMEDIAL ACTION PLANS
    Section 703.301
    General Information
    a)
    What is a RAP?
    1)
    A RAP is a special form of RCRA permit that an owner or operator may
    obtain, instead of a permit issued under 35 Ill. Adm. Code 702 and this
    Part, to authorize the owner or operator to treat, store, or dispose of
    hazardous remediation waste (as defined in 35 Ill. Adm. Code 720.110)
    at a remediation waste management site. A RAP may only be issued for
    the area of contamination where the remediation wastes to be managed
    under the RAP originated, or areas in close proximity to the contaminated
    area, except as allowed in limited circumstances under Section 703.306.
    2)
    The requirements in 35 Ill. Adm. Code 702 and this Part do not apply to
    RAPs unless those requirements for traditional RCRA permits are

    33
    specifically required under this Subpart H. The definitions in 35 Ill.
    Adm. Code 702.110 apply to RAPs.
    3)
    Notwithstanding any other provision of 35 Ill. Adm. Code 702 or this
    Part, any document that meets the requirements in this Section constitutes
    a RCRA permit, as defined in 35 Ill. Adm. Code 702.110.
    4)
    A RAP may be either of the following:
    A)
    A stand-alone document that includes only the information and
    conditions required by this Subpart H; or
    B)
    A part (or parts) of another document that includes information or
    conditions for other activities at the remediation waste
    management site, in addition to the information and conditions
    required by this Subpart H.
    5)
    If an owner or operator is treating, storing, or disposing of hazardous
    remediation wastes as part of a cleanup compelled by authorities issued
    by USEPA or the State of Illinois, a RAP does not affect the obligations
    under those authorities in any way.
    6)
    If an owner or operator receives a RAP at a facility operating under
    interim status, the RAP does not terminate the facility’s interim status.
    BOARD NOTE: Derived from 40 CFR 270.80, added at 63 Fed. Reg. 65942
    (Nov. 30, 1998) (1999).
    b)
    When does an owner or operator need a RAP?
    1)
    Whenever an owner or operator treats, stores, or disposes of hazardous
    remediation wastes in a manner that requires a RCRA permit under
    Section 703.121, an owner or operator shall obtain either of the
    following:
    A)
    A RCRA permit according to 35 Ill. Adm. Code 702 and this
    Part; or
    B)
    A RAP according to this Subpart H.
    2)
    Treatment units that use combustion of hazardous remediation wastes at a
    remediation waste management site are not eligible for RAPs under this
    Subpart H.
    3)
    An owner or operator may obtain a RAP for managing hazardous

    34
    remediation waste at an already permitted RCRA facility. An owner or
    operator shall have the RAP approved as a modification to the owner’s or
    operator’s existing permit according to the requirements of Sections
    703.270 through 703.273 or Sections 703.280 through 703.283 instead
    of the requirements in this Subpart H. However, when an owner or
    operator submits an application for such a modification, the information
    requirements in Sections 703.281(a)(1), 703.282(a)(4), and 703.283(a)(4)
    do not apply. Instead, an owner or operator shall submit the information
    required under Section 703.302(d). When the owner’s or operator’s
    RCRA permit is modified, the RAP becomes part of the RCRA permit.
    Therefore, when the owner’s or operator’s RCRA permit (including the
    RAP portion) is modified, revoked and reissued, or terminated, or when
    it expires, the permit will be modified, according to the applicable
    requirements in Sections 703.270 through 703.273 or 703.280 through
    703.283;, it will be revoked and reissued, according to the applicable
    requirements in 35 Ill. Adm. Code 702.186 and Sections 703.270
    through 703.273;, or it will be terminated, according to the applicable
    requirements in 35 Ill. Adm. Code 702.186, or the permit will expire,
    according to the applicable requirements in 35 Ill. Adm. Code 702.125
    and 702.161.
    BOARD NOTE: Derived from 40 CFR 270.85, added at 63 Fed. Reg. 65942
    (Nov. 30, 1998) (1999).
    c)
    Does a RAP grant an owner or operator any rights or relieve it of any
    obligations? The provisions of 35 Ill. Adm. Code 702.181 apply to RAPs.
    BOARD NOTE: Derived from 40 CFR 270.90, added at 63 Fed. Reg. 65942
    (Nov. 30, 1998) (1999). The corresponding federal provision includes an
    explanation that 40 CFR 270.4 provides that compliance with a permit constitutes
    compliance with RCRA. This is contrary to Illinois law, under which
    compliance with a permit does not constitute an absolute defense to a charge of
    violation of a substantive standard other than a failure to operate in accordance
    with the terms of a permit. See 35 Ill. Adm. Code 702.181(a) and
    accompanying Board Note.
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 703.303
    Getting a RAP Approved
    a)
    What is the process for approving or denying an application for a RAP?
    1)
    If the Agency tentatively finds that an owner’s or operator’s RAP
    application includes all of the information required by Section 703.302(d)
    and that the proposed remediation waste management activities meet the

    35
    regulatory standards, the Agency shall make a tentative decision to
    approve the RAP application. The Agency shall then prepare a draft
    RAP and provide an opportunity for public comment before making a
    final decision on the RAP application, according to this Subpart H.
    2)
    If the Agency tentatively finds that the owner’s or operator’s RAP
    application does not include all of the information required by Section
    703.302(d) or that the proposed remediation waste management activities
    do not meet the regulatory standards, the Agency may request additional
    information from an owner or operator or ask an owner or operator to
    correct deficiencies in the owner’s or operator’s application. If an owner
    or operator fails or refuses to provide any additional information the
    Agency requests, or to correct any deficiencies in its RAP application,
    the Agency may either make a tentative decision to deny that owner’s or
    operator’s RAP application or to approve that application with certain
    changes, as allowed under Section 39 of the Act [415 ILCS 5/39]. After
    making this tentative decision, the Agency shall prepare a notice of intent
    to deny the RAP application (“notice of intent to deny”) or to approve
    that application with certain changes and provide an opportunity for
    public comment before making a final decision on the RAP application,
    according to the requirements in this Subpart H.
    BOARD NOTE: Derived from 40 CFR 270.130, added at 63 Fed. Reg. 65943
    (Nov. 30, 1998) (1999).
    b)
    What must the Agency include in a draft RAP? If the Agency prepares a draft
    RAP, the draft must include the following information:
    1)
    The information required under Section 703.302(d)(1) through (d)(6);
    2)
    The following terms and conditions:
    A)
    Terms and conditions necessary to ensure that the operating
    requirements specified in the RAP comply with applicable
    requirements of 35 Ill. Adm. Code 724, 726, and 728 (including
    any recordkeeping and reporting requirements). In satisfying this
    provision, the Agency may incorporate, expressly or by
    reference, applicable requirements of 35 Ill. Adm. Code 724,
    726, and 728 into the RAP or establish site-specific conditions, as
    required or allowed by 35 Ill. Adm. Code 724, 726, and 728;
    B)
    The terms and conditions in Subpart F of this Part;
    C)
    The terms and conditions for modifying, revoking and reissuing,
    and terminating the RAP, as provided in Section 703.304(a); and

    36
    D)
    Any additional terms or conditions that the Agency determines are
    necessary to protect human health and the environment, including
    any terms and conditions necessary to respond to spills and leaks
    during use of any units permitted under the RAP; and
    3)
    If the draft RAP is part of another document, as described in Section
    703.301(a)(4)(B), the Agency shall clearly identify the components of that
    document that constitute the draft RAP.
    BOARD NOTE: Derived from 40 CFR 270.135, added at 63 Fed. Reg. 65943
    (Nov. 30, 1998) (1999).
    c)
    What else must the Agency prepare in addition to the draft RAP or notice of
    intent to deny? Once the Agency has prepared the draft RAP or notice of intent
    to deny, it shall then do the following:
    1)
    Prepare a statement of basis that briefly describes the derivation of the
    conditions of the draft RAP and the reasons for them, or the rationale for
    the notice of intent to deny;
    2)
    Compile an administrative record, including the following information:
    A)
    The RAP application, and any supporting data furnished by the
    applicant;
    B)
    The draft RAP or notice of intent to deny;
    C)
    The statement of basis and all documents cited therein (material
    readily available at the applicable Agency office or published
    material that is generally available need not be physically included
    with the rest of the record, as long as it is specifically referred to
    in the statement of basis); and
    D)
    Any other documents that support the decision to approve or deny
    the RAP; and
    3)
    Make information contained in the administrative record available for
    review by the public upon request.
    BOARD NOTE: Derived from 40 CFR 270.140, added at 63 Fed. Reg. 65943
    (Nov. 30, 1998) (1999).
    d)
    What are the procedures for public comment on the draft RAP or notice of intent
    to deny?

    37
    1)
    The Agency shall publish notice of its intent as follows:
    A)
    Send notice to an owner or operator of its intention to approve or
    deny the owner’s or operator’s RAP application, and send an
    owner or operator a copy of the statement of basis;
    B)
    Publish a notice of its intention to approve or deny the owner’s or
    operator’s RAP application in a major local newspaper of general
    circulation;
    C)
    Broadcast its intention to approve or deny the owner’s or
    operator’s RAP application over a local radio station; and
    D)
    Send a notice of its intention to approve or deny the owner’s or
    operator’s RAP application to each unit of local government
    having jurisdiction over the area in which the owner’s or
    operator’s site is located, and to each State agency having any
    authority under State law with respect to any construction or
    operations at the site.
    2)
    The notice required by subsection (d)(1) of this Section must provide an
    opportunity for the public to submit written comments on the draft RAP
    or notice of intent to deny within at least 45 days.
    3)
    The notice required by subsection (d)(1) of this Section must include the
    following information:
    A)
    The name and address of the Agency office processing the RAP
    application;
    B)
    The name and address of the RAP applicant, and if different, the
    remediation waste management site or activity the RAP will
    regulate;
    C)
    A brief description of the activity the RAP will regulate;
    D)
    The name, address, and telephone number of a person from
    whom interested persons may obtain further information,
    including copies of the draft RAP or notice of intent to deny,
    statement of basis, and the RAP application;
    E)
    A brief description of the comment procedures in this Section, and
    any other procedures by which the public may participate in the
    RAP decision;

    38
    F)
    If a hearing is scheduled, the date, time, location, and purpose of
    the hearing;
    G)
    If a hearing is not scheduled, a statement of procedures to request
    a hearing;
    H)
    The location of the administrative record, and times when it will
    be open for public inspection; and
    I)
    Any additional information that the Agency considers necessary or
    proper.
    4)
    If, within the comment period, the Agency receives written notice of
    opposition to its intention to approve or deny the owner’s or operator’s
    RAP application and a request for a hearing, the Agency shall hold an
    informal public hearing to discuss issues relating to the approval or denial
    of the owner’s or operator’s RAP application. The Agency may also
    determine on its own initiative that an informal hearing is appropriate.
    The hearing must include an opportunity for any person to present
    written or oral comments. Whenever possible, the Agency shall schedule
    this hearing at a location convenient to the nearest population center to the
    remediation waste management site and give notice according to the
    requirements in subsection (d)(1) of this Section. This notice must, at a
    minimum, include the information required by subsection (d)(3) of this
    Section and the following additional information:
    A)
    A reference to the date of any previous public notices relating to
    the RAP application;
    B)
    The date, time, and place of the hearing; and
    C)
    A brief description of the nature and purpose of the hearing,
    including the applicable rules and procedures.
    BOARD NOTE: Derived from 40 CFR 270.145, added at 63 Fed. Reg. 65943
    (Nov. 30, 1998) (1999).
    e)
    How must the Agency make a final decision on a RAP application?
    1)
    The Agency shall consider and respond to any significant comments
    raised during the public comment period or during any hearing on the
    draft RAP or notice of intent to deny, and the Agency may revise the
    draft RAP based on those comments, as appropriate.

    39
    2)
    If the Agency determines that the owner’s or operator’s RAP includes the
    information and terms and conditions required in subsection (b) of this
    Section, then it will issue a final decision approving the owner’s or
    operator’s RAP and, in writing, notify the owner or operator and all
    commenters on the owner’s or operator’s draft RAP that the RAP
    application has been approved.
    3)
    If the Agency determines that the owner’s or operator’s RAP does not
    include the information required in subsection (b) of this Section, then it
    will issue a final decision denying the RAP and, in writing, notify the
    owner or operator and all commenters on the owner’s or operator’s draft
    RAP that the RAP application has been denied.
    4)
    If the Agency’s final decision is that the tentative decision to deny the
    RAP application was incorrect, it shall withdraw the notice of intent to
    deny and proceed to prepare a draft RAP, according to the requirements
    in this Subpart H.
    5)
    When the Agency issues its final RAP decision, it shall refer to the
    procedures for appealing the decision under subsection (f) of this Section.
    6)
    Before issuing the final RAP decision, the Agency shall compile an
    administrative record. Material readily available at the applicable Agency
    office or published materials that are generally available and which are
    included in the administrative record need not be physically included with
    the rest of the record, as long as it is specifically referred to in the
    statement of basis or the response to comments. The administrative
    record for the final RAP must include information in the administrative
    record for the draft RAP (see subsection (c)(2) of this Section) and the
    following items:
    A)
    All comments received during the public comment period;
    B)
    Tapes or transcripts of any hearings;
    C)
    Any written materials submitted at these hearings;
    D)
    The responses to comments;
    E)
    Any new material placed in the record since the draft RAP was
    issued;
    F)
    Any other documents supporting the RAP; and
    G)
    A copy of the final RAP.

    40
    7)
    The Agency shall make information contained in the administrative record
    available for review by the public upon request.
    BOARD NOTE: Derived from 40 CFR 270.150, added at 63 Fed. Reg. 65944
    (Nov. 30, 1998) (1999).
    f)
    May the decision to approve or deny a RAP application be administratively
    appealed?
    1)
    Any commenter on the draft RAP or notice of intent to deny, or any
    participant in any public hearing on the draft RAP, may appeal the
    Agency’s decision to approve or deny the owner’s or operator’s RAP
    application to the Board under 35 Ill. Adm. Code 705.212. Any person
    that did not file comments, or did not participate in any public hearing(s)
    hearings on the draft RAP, may petition for administrative review only to
    the extent of the changes from the draft to the final RAP decision.
    Appeals of RAPs may be made to the same extent as for final permit
    decisions under 35 Ill. Adm. Code 705.201 (or a decision under Section
    703.240 to deny a permit for the active life of a RCRA hazardous waste
    management facility or unit). Instead of the notice required under 35 Ill.
    Adm. Code 705.Subpart D and 705.212(c), the Agency shall give public
    notice of any grant of review of a RAP through the same means used to
    provide notice under subsection (d) of this Section. The notice will
    include the following information:
    A)
    The public hearing and any briefing schedule for the appeal, as
    provided by the Board;
    B)
    A statement that any interested person may participate in the
    public hearing or file public comments or an amicus brief with the
    Board; and
    C)
    The information specified in subsection (d)(3) of this Section, as
    appropriate.
    2)
    This appeal is a prerequisite to seeking judicial review of these Agency
    actions.
    BOARD NOTE: Derived from 40 CFR 270.155, added at 63 Fed. Reg. 65944
    (Nov. 30, 1998) (1999).
    g)
    When does a RAP become effective? An A RAP becomes effective 35 days
    after the Agency notifies the owner or operator and all commenters that the RAP
    is approved, unless any of the following is true:

    41
    1)
    The Agency specifies a later effective date in its decision;
    2)
    An owner or operator or another person has appealed the RAP under
    subsection (f) of this Section (if the RAP is appealed, and the request for
    review is granted under subsection (f), conditions of the RAP are stayed
    according to 35 Ill. Adm. Code 705.202 through 705.204); or
    3)
    No commenters requested a change in the draft RAP, in which case the
    RAP becomes effective immediately when it is issued.
    BOARD NOTE: Derived from 40 CFR 270.160, added at 63 Fed. Reg. 65944
    (Nov. 30, 1998) (1999). The corresponding federal provision provides 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)].
    h)
    When may an owner or operator begin physical construction of new units
    permitted under the RAP? An owner or operator shall not begin physical
    construction of new units permitted under the RAP for treating, storing, or
    disposing of hazardous remediation waste before receiving a finally final,
    effective RAP.
    BOARD NOTE: Derived from 40 CFR 270.165, added at 63 Fed. Reg. 65944
    (Nov. 30, 1998) (1999).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 703.304
    How a RAP May Be Modified, Revoked and Reissued, or Terminated
    a)
    After a RAP is issued, how may it be modified, revoked and reissued, or
    terminated? In a RAP, the Agency shall specify, either directly or by reference,
    procedures for any future modification, revocation and reissuance, or termination
    of the RAP. These procedures must provide adequate opportunities for public
    review and comment on any modification, revocation and reissuance, or
    termination that would significantly change the owner’s or operator’s
    management of its remediation waste, or that otherwise merits public review and
    comment. If the RAP has been incorporated into a traditional RCRA permit, as
    allowed under Section 703.301(b)(3), then the RAP will be modified according
    to the applicable requirements in Sections 703.260 through 703.283, revoked
    and reissued according to the applicable requirements in 35 Ill. Adm. Code
    702.186 and Sections 703.270 through 703.273, or terminated according to the
    applicable requirements of 35 Ill. Adm. Code 702.186.
    BOARD NOTE: Derived from 40 CFR 270.170, added at 63 Fed. Reg. 65944

    42
    (Nov. 30, 1998) (1999).
    b)
    For what reasons may the Agency choose to modify a final RAP?
    1)
    The Agency may modify the owner’s or operator’s final RAP on its own
    initiative only if one or more of the following reasons listed in this
    Section exist. If one or more of these reasons do not exist, then the
    Agency shall not modify a final RAP, except at the request of the owner
    or operator. Reasons for modification are the following:
    A)
    The owner or operator made material and substantial alterations or
    additions to the activity that justify applying different conditions;
    B)
    The Agency finds new information that was not available at the
    time of RAP issuance and would have justified applying different
    RAP conditions at the time of issuance;
    C)
    The standards or regulations on which the RAP was based have
    changed because of new or amended statutes, standards, or
    regulations or by judicial decision after the RAP was issued;
    D)
    If the RAP includes any schedules of compliance, the Agency
    may find reasons to modify the owner’s or operator’s compliance
    schedule, such as an act of God, strike, flood, or materials
    shortage or other events over which an owner or operator has
    little or no control and for which there is no reasonably available
    remedy;
    E)
    The owner or operator is not in compliance with conditions of its
    RAP;
    F)
    The owner or operator failed in the application or during the RAP
    issuance process to disclose fully all relevant facts, or an owner or
    operator misrepresented any relevant facts at the time;
    G)
    The Agency has determined that the activity authorized by the
    owner’s or operator’s RAP endangers human health or the
    environment and can only be remedied by modifying the RAP; or
    H)
    The owner or operator has notified the Agency (as required in the
    RAP and under 35 Ill. Adm. Code 702.152(c)) of a proposed
    transfer of a RAP.
    2)
    Notwithstanding any other provision in this Section, when the Agency
    reviews a RAP for a land disposal facility under Section 703.304(f), it

    43
    may modify the permit as necessary to assure that the facility continues to
    comply with the currently applicable requirements in 35 Ill. Adm. Code
    702, 703, 705, and 720 through 726.
    3)
    The Agency shall not reevaluate the suitability of the facility location at
    the time of RAP modification unless new information or standards
    indicate that a threat to human health or the environment exists that was
    unknown when the RAP was issued.
    BOARD NOTE: Derived from 40 CFR 270.175, added at 63 Fed. Reg. 65944
    (Nov. 30, 1998) (1999).
    c)
    For what reasons may the Agency choose to revoke and reissue a final RAP?
    1)
    The Agency may revoke and reissue a final RAP on its own initiative
    only if one or more reasons for revocation and reissuance exist. If one
    or more reasons do not exist, then the Agency shall not modify or revoke
    and reissue a final RAP, except at the owner’s or operator’s request.
    Reasons for modification or revocation and reissuance are the same as the
    reasons listed for RAP modifications in subsections (b)(1)(E) through
    (b)(1)(H) of this Section if the Agency determines that revocation and
    reissuance of the RAP is appropriate.
    2)
    The Agency shall not reevaluate the suitability of the facility location at
    the time of RAP revocation and reissuance, unless new information or
    standards indicate that a threat to human health or the environment exists
    that was unknown when the RAP was issued.
    BOARD NOTE: Derived from 40 CFR 270.180, added at 63 Fed. Reg. 65945
    (Nov. 30, 1998) (1999).
    d)
    For what reasons may the Agency choose to terminate a final RAP, or deny a
    renewal application? The Agency may terminate a final RAP on its own
    initiative, or deny a renewal application for the same reasons as those listed for
    RAP modifications in subsections (b)(1)(E) through (b)(1)(G) of this Section if
    the Agency determines that termination of the RAP or denial of the RAP
    renewal application is appropriate.
    BOARD NOTE: Derived from 40 CFR 270.185, added at 63 Fed. Reg. 65945
    (Nov. 30, 1998) (1999).
    e)
    May the decision to approve or deny a modification, revocation and reissuance,
    or termination of a RAP be administratively appealed?
    1)
    Any commenter on the modification, revocation and reissuance, or

    44
    termination, or any person that participated in any hearing on these
    actions, may appeal the Agency’s decision to approve a modification,
    revocation and reissuance, or termination of a RAP, according to Section
    703.303(f). Any person that did not file comments or did not participate
    in any public hearing on the modification, revocation and reissuance, or
    termination may petition for administrative review only of the changes
    from the draft to the final RAP decision.
    2)
    Any commenter on the modification, revocation and reissuance, or
    termination, or any person that participated in any hearing on these
    actions, may appeal the Agency’s decision to deny a request for
    modification, revocation and reissuance, or termination to the Board.
    Any person that did not file comments or which did not participate in any
    public hearing on the modification, revocation and reissuance, or
    termination may petition for administrative review only of the changes
    from the draft to the final RAP decision.
    3)
    The procedure for appeals of RAPs is as follows:
    A)
    The person appealing the decision shall send a petition to the
    Board pursuant to 35 Ill. Adm. Code 101 and 105. The petition
    must briefly set forth the relevant facts, state the defect or fault
    that serves as the basis for the appeal, and explain the basis for the
    petitioner’s legal standing to pursue the appeal.
    B)
    The Board has 120 days after receiving the petition to act on it.
    C)
    If the Board does not take action on the petition within 120 days
    after receiving it, the appeal shall be considered denied.
    BOARD NOTE: Corresponding 40 CFR 270.190(c)(2) and
    (c)(3), as added at 63 Fed. Reg. 65945 (Nov. 30, 1998) (1999)
    allow 60 days for administrative review, which is too short a time
    for the Board to publish the appropriate notices, conduct public
    hearings, and conduct its review. Rather, the Board has
    borrowed the 120 days allowed as adequate time for Board
    review of permit appeals provided in Section 40(a)(2) of the Act
    [415 ILCS 5/40(a)(2)].
    4)
    This appeal is a prerequisite to seeking judicial review of the Agency
    action on the RAP.
    BOARD NOTE: Derived from 40 CFR 270.190, added at 63 Fed. Reg. 65945
    (Nov. 30, 1998) (1999). The corresponding federal provisions provide for
    informal appeal of an Agency RAP decision. There is no comparable informal

    45
    procedure under Sections 39 and 40 of the Act [415 ILCS 5/39 and 40].
    f)
    When will a RAP expire? RAPs must be issued for a fixed term, not to exceed
    10 years, although they may be renewed upon approval by the Agency in fixed
    increments of no more than ten years. In addition, the Agency shall review any
    RAP for hazardous waste land disposal five years after the date of issuance or
    reissuance and the owner or operator or the Agency shall follow the
    requirements for modifying the RAP as necessary to assure that the owner or
    operator continues to comply with currently applicable requirements in the Act
    and RCRA sections 3004 and 3005.
    BOARD NOTE: Derived from 40 CFR 270.195, added at 63 Fed. Reg. 65945
    (Nov. 30, 1998) (1999).
    g)
    How may an owner or operator renew a RAP that is expiring? If an owner or
    operator wishes to renew an expiring RAP, the owner or operator shall follow
    the process for application for and issuance of RAPs in this Subpart H.
    BOARD NOTE: Derived from 40 CFR 270.200, added at 63 Fed. Reg. 65945
    (Nov. 30, 1998) (1999).
    h)
    What happens if the owner or operator has applied correctly for a RAP renewal
    but has not received approval by the time its old RAP expires? If the owner or
    operator has submitted a timely and complete application for a RAP renewal, but
    the Agency, through no fault of the owner or operator, has not issued a new
    RAP with an effective date on or before the expiration date of the previous
    RAP, the previous RAP conditions continue in force until the effective date of
    the new RAP or RAP denial.
    BOARD NOTE: Derived from 40 CFR 270.205, added at 63 Fed. Reg. 65945
    (Nov. 30, 1998) (1999).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 703.306
    Obtaining a RAP for an Off-Site Location
    May an owner or operator 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

    46
    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 shall approve a RAP for this alternative location.
    c)
    An owner or operator shall request the RAP, and the Agency shall approve or
    deny the RAP, according to the procedures and requirements in this Subpart H
    of this Part.
    d)
    A RAP for an alternative location must also meet the following requirements,
    which the Agency shall 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;
    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 shall 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 40 CFR 264, Appendix VI.
    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 35 Ill. Adm. Code
    724.Subparts B, C, and D.
    BOARD NOTE: Derived from 40 CFR 270.230, added at 63 Fed. Reg. 65946 (Nov. 30,
    1998) (1999).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)

    47
    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.
    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.

    48
    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/control 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.
    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:

    49
    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 shall 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.
    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:

    50
    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.
    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.

    51
    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 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.
    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).

    52
    1
    c.
    Or 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 or to treat wastes to satisfy (in whole or in part) the
    standard of “use of practically available technology that yields
    the greatest environmental benefit” contained in 40 CFR
    268.8(a)(2)(ii), incorporated by reference in 35 Ill. Adm. Code
    728.108, 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:

    53
    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, or are to be treated to satisfy
    (in whole or in part) the standard of “use of practically
    available technology that yields the greatest environmental
    benefit” contained in 40 CFR 268.8(a)(2)(ii), incorporated by
    reference in 35 Ill. Adm. Code 728.108. 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.

    54
    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 or to treat wastes to satisfy (in whole or in part) the
    standard of “use of practically available technology that yields
    the greatest environmental benefit” contained in 40 CFR
    268.8(a)(2)(ii), incorporated by reference in 35 Ill. Adm. Code
    728.108, 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.
    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.

    55
    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, or that are to be
    treated to satisfy (in whole or in part) the standard of “use of
    practically available technology that yields the greatest
    environmental benefit” contained in 40 CFR 268.8(a)(2)(ii),
    incorporated by reference in 35 Ill. Adm. Code 728.108. 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
    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.

    56
    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 or that are treated to satisfy the
    standard of “use of practically available technology that yields
    the greatest environmental benefit” contained in 40 CFR
    268.8(a)(2)(ii), incorporated by reference in 35 Ill. Adm. Code
    728.108, and provided that the unit meets the minimum
    technological requirements stated in 40 CFR 268.5(h)(2),
    incorporated by reference in 35 Ill. Adm. Code 728.105. 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),
    incorporated by reference in 35 Ill. Adm. Code 728.105, 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).
    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.

    57
    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.
    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.

    58
    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 or that are treated to satisfy the
    standard of “use of practically available technology that yields
    the greatest environmental benefit” contained in 40 CFR
    268.8(a)(2)(ii), incorporated by reference in 35 Ill. Adm. Code
    728.108, and provided that the landfill unit meets the minimum
    technological requirements stated in 40 CFR 268.5(h)(2),
    incorporated by reference in 35 Ill. Adm. Code 728.105. 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 landfill unit that meets the
    minimum technological requirements stated in 40 CFR
    268.5(h)(2), incorporated by reference in 35 Ill. Adm. Code
    728.105, 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.

    59
    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.
    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.

    60
    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.
    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.

    61
    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 shall 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 shall 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/Cl
    2
    , 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 shall require a new trial burn to substantiate
    compliance with the regulatory performance standards, unless this
    demonstration can be made through other means.
    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:

    62
    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 shall 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 shall 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.
    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.

    63
    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 alternate type of non-hazardous waste fuel that is not
    specified in the permit.
    1*
    9.
    Technology changes needed to meet standards under federal 40 CFR
    63 (Subpart EEE--National Emission Standards for Hazardous Air
    Pollutants From Hazardous Waste Combustors), 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.
    1
    b.
    The replacement containment building meets the same
    conditions in the permit.
    2
    4.
    Modification of a containment building management practice.

    64
    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 40 CFR 270.42, Appendix I (1998) (1999), as amended at 63
    64 Fed. Reg. 65941 (Nov. 30, 1998) 53077 (September 30, 1999).
    (Source: Amended at 24 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
    SUBPART B: DEFINITIONS
    Section
    720.110
    Definitions
    720.111
    References

    65
    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, Subtitle C 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, 43 PCB 427, at 5 Ill. Reg. 9781, effective May 17, 1982;
    amended and codified in R81-22, 45 PCB 317, 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, 53
    PCB 131 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. 9508,
    effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 10929, 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,

    66
    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. ________, effective ______________________; amended in
    R00-13 at 24 Ill. Reg. ________, effective ______________________.
    SUBPART B: DEFINITIONS
    Section 720.110
    Definitions
    When used in 35 Ill. Adm. Code 720 through 726 and 728 only, the following terms have the
    meanings given below:
    “Aboveground tank” means a device meeting the definition of “tank” 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.
    “Act” or “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.)
    “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 U.S. 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 tank(s) 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.

    67
    “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 consisting of one or more electrically connected
    electrochemical cells that 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:
    Physical 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 section(s) sections must be of integral design. To
    be of integral design, the combustion chamber and the primary
    energy recovery section(s) 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 section(s) 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 shall be given for recovered heat used

    68
    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
    Boiler by designation. The unit is one which 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 which 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 35 Ill. Adm. Code
    724.Subpart DD and 35 Ill. Adm. Code 725.Subpart DD.
    “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 which that could
    threaten human health or the environment.
    “Corrective action management unit” or “CAMU” means an area within a
    facility that is used only for managing remediation wastes for implementing
    corrective action or cleanup at the facility.
    BOARD NOTE: USEPA must also designate a CAMU until it grants this
    authority to the Agency. See the note following 35 Ill. Adm. Code 724.652.
    “Corrosion expert” means a person who, by reason of knowledge of the
    physical sciences and the principles of engineering and mathematics, acquired by

    69
    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,
    WhichOf which any of the following is true:
    Has The facility has received a RCRA permit (or interim status)
    pursuant to 35 Ill. Adm. Code 702, 703 and 705;
    Has The facility has received a RCRA permit from USEPA
    pursuant to 40 CFR 124 and 270 (1992) (1999);
    Has The facility has received a RCRA permit from a state
    authorized by USEPA pursuant to 40 CFR 271 (1992) (1999); or
    Is The facility is regulated under 35 Ill. Adm. Code 721.106(c)(2)
    or 266.Subpart F; and
    Which The facility has been designated on the manifest by the generator
    pursuant to 35 Ill. Adm. Code 722.120.
    If a waste is destined to a facility in a state, other than Illinois, which 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-

    70
    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 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.
    “Electric lamp” means the bulb or tube portion of a lighting device specifically
    designed to produce radiant energy, most often in the ultraviolet, visible, and
    infrared regions of the electromagnetic spectrum.
    BOARD NOTE: The definition of “electric lamp” was added pursuant to
    Section 22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective
    August 19, 1997).
    “Elementary neutralization unit” means a device which:
    Is used for neutralizing wastes which are hazardous only because they
    exhibit the corrosivity characteristic defined in 35 Ill. Adm. Code
    721.122 or are listed in 35 Ill. Adm. Code 721.Subpart D only for this
    reason; and
    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 35 Ill. Adm.
    Code 721.Subpart D and to each characteristic identified in 35 Ill. Adm. Code
    721.Subpart C.

    71
    “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 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 which 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:
    A continuous on-site, physical construction program had begun; or

    72
    The owner or operator had entered into contractual obligations, which
    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 is in operation or for which installation has 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:
    A continuous on-site physical construction or installation program has
    begun; or
    The owner or operator has entered into contractual obligations, which
    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

    73
    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 U.S. United States Department
    of Defense (U.S. DODUSDOD) emergency explosive ordnance disposal (EOD),
    technical escort unit (TEU), and U.S. DODUSDOD-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:
    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 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

    74
    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 which readily separate from the solid portion of a
    waste under ambient temperature and pressure.
    “Generator” means any person, by site, whose act or process produce 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 which that caused the
    hazardous waste to be listed in 35 Ill. Adm. Code 721.Subpart D, 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 which is not operated after
    November 19, 1980. (See also “active portion” and “closed portion”.)
    “Incinerator” means any enclosed device that of which the following is true:
    Uses The facility uses controlled flame combustion, and it neither:
    Meets the criteria for classification as a boiler, sludge dryer, or
    carbon regeneration unit, nor
    Is listed as an industrial furnace; or

    75
    Meets The facility meets the definition of infrared incinerator or plasma
    arc incinerator.
    “Incompatible waste” means a hazardous waste which that is unsuitable for:
    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 35 Ill. Adm. Code 725.Appendix E 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;
    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;

    76
    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” 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;
    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 which 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.

    77
    “In operation” refers to a facility which 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 which 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 infra-red 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.
    “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 which 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.

    78
    “Liner” means a continuous layer of natural or manmade materials beneath or on
    the sides of a surface impoundment, landfill, or landfill cell, which 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 originated and signed by the generator
    which that contains the information required by 35 Ill. Adm. Code 722.Subpart
    B.
    “Manifest document number” means 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.
    “Mercury-containing lamp” means an electric lamp into which mercury is
    purposely introduced by the manufacturer for the operation of the lamp.
    Mercury-containing lamps include, but are not limited to, fluorescent lamps and
    high-intensity discharge lamps.
    BOARD NOTE: The definition of “mercury-containing lamp” was added
    pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502,
    effective August 19, 1997).
    “Military munitions” means all ammunition products and components produced
    or used by or for the U.S. United States Department of Defense or the U.S.
    United States Armed Services for national defense and security, including
    military munitions under the control of the U.S. United States Department of
    Defense, the U.S. United States Coast Guard, the U.S. United States
    Department of Energy (U.S. DOE 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 U.S. DOD USDOD components, including bulk
    explosives and chemical warfare agents, chemical munitions, rockets, guided and

    79
    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 U.S. DOE USDOE’s
    nuclear weapons program after all sanitization operations required under the
    Atomic Energy Act of 1954, as amended, have been completed.
    “Mining overburden returned to the mine site” means any material overlying an
    economic mineral deposit which 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 that hazardous waste transported to a facility in an individual
    vehicle.
    “New hazardous waste management facility” or “new facility” means a facility
    which 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 commences 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 which 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

    80
    opposed to going along the right-of-way. Noncontiguous properties owned by
    the same person but connected by a right-of-way which he 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
    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 which 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

    81
    in Section 720.111,;
    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, incorporated by reference in Section 720.111, 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, that bears or contains any
    substances described in either of the two preceding subsections 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 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 which 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

    82
    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.
    “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
    contain listed hazardous wastes or which themselves exhibit a hazardous waste
    characteristic which that are managed for the purpose of implementing cleanup.
    “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) which 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” means Standard Industrial Code as defined in Standard Industrial

    83
    Classification Manual, incorporated by reference in Section 720.111.
    “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 which that is used
    to dehydrate sludge and which has a total thermal input, excluding the heating
    value of the sludge itself, of 2500 Btu/lb or less of sludge treated on a wet
    weight basis.
    “Small Quantity Generator” means a generator which that generates less than
    1000 kg of hazardous waste in a calendar month.
    “Solid waste” means a solid waste as defined in 35 Ill. Adm. Code 721.102.
    “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
    which that is a natural topographic depression, manmade excavation, or diked
    area formed primarily of earthen materials (although it may be lined with

    84
    manmade materials) which 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) which 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 which
    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 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 which that is directly connected to an industrial production
    process and which is constructed and operated in a manner which 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.

    85
    “Transporter” means a person engaged in the off-site transportation of hazardous
    waste by air, rail, highway, or water.
    “Treatability study” means:
    A study in which a hazardous waste is subjected to a treatment process to
    determine:
    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
    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 such the waste, so as to recover
    energy or material resources from the waste, or so as to render such 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.

    86
    “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; and
    Mercury-containing lampsLamps, as described in 35 Ill. Adm. Code
    733.107 733.105.
    BOARD NOTE: Mercury-containing lamps were added as universal
    waste pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see
    P.A. 90-502, effective August 19, 1997).
    “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:
    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.

    87
    “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:
    Is It is part of a wastewater treatment facility which 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
    Receives It receives and treats or stores an influent wastewater which that
    is a hazardous waste as defined in 35 Ill. Adm. Code 721.103, or
    generates and accumulates a wastewater treatment sludge which is a
    hazardous waste as defined in 35 Ill. Adm. Code 721.103, or treats or
    stores a wastewater treatment sludge which is a hazardous waste as
    defined in 35 Ill. Adm. Code 721.103; and
    Meets It meets the definition of tank or tank system in this Section.
    “Water (bulk shipment)” means the bulk transportation of hazardous waste which
    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.

    88
    “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 24 Ill. Reg. ________, effective ______________________)
    Section 720.111
    References
    a)
    The following publications 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:
    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.
    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.
    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.
    “Evaporative Loss from External Floating-Roof Tanks”, API
    Publication 2517, Third Edition, February, 1989.
    “Guide for Inspection of Refinery Equipment, Chapter XIII,
    Atmospheric and Low Pressure Storage Tanks”, 4th Edition,
    1981, reaffirmed December, 1987.
    “Installation of Underground Petroleum Storage Systems”, API
    Recommended Practice 1615, Fourth Edition, November, 1987.
    APTI. Available from the Air and Waste Management Association, Box
    2861, Pittsburgh, PA 15230, 412-232-3444:

    89
    APTI Course 415: Control of Gaseous Emissions, USEPA
    Publication EPA-450/2-81-005, December, 1981.
    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.
    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.
    Also available from ANSI.
    ASTM. Available from American Society for Testing and Materials,
    1916 Race Street, Philadelphia, PA 19103, 215-299-5400:
    ASTM C 94-90, Standard Specification for Ready-Mixed
    Concrete, approved March 30, 1990.
    ASTM D 88-87, Standard Test Method for Saybolt Viscosity,
    April 24, 1981, reapproved January, 1987.
    ASTM D 93-85, Standard Test Methods for Flash Point by
    Pensky-Martens Closed Tester, approved October 25, 1985.
    ASTM D 1946-90, Standard Practice for Analysis of Reformed
    Gas by Gas Chromatography, approved March 30, 1990.
    ASTM D 2161-87, Standard Practice for Conversion of
    Kinematic Viscosity to Saybolt Universal or to Saybolt Furol
    Viscosity, March 27, 1987.
    ASTM D 2267-88, Standard Test Method for Aromatics in Light
    Naphthas and Aviation Gasolines by Gas Chromatography,
    approved November 17, 1988.
    ASTM D 2382-88, Standard Test Method for Heat of Combustion
    of Hydrocarbon Fuels by Bomb Calorimeter (High Precision
    Method), approved October 31, 1988.
    ASTM D 2879-92, Standard Test Method for Vapor Pressure-
    Temperature Relationship and Initial Decomposition Temperature

    90
    of Liquids by Isoteniscope, approved 1992.
    ASTM D 3828-87, Standard Test Methods for Flash Point of
    Liquids by Setaflash Closed Tester, approved December 14,
    1988.
    ASTM E 168-88, Standard Practices for General Techniques of
    Infrared Quantitative Analysis, approved May 27, 1988.
    ASTM E 169-87, Standard Practices for General Techniques of
    Ultraviolet-Visible Quantitative Analysis, approved February 1,
    1987.
    ASTM E 260-85, Standard Practice for Packed Column Gas
    Chromatography, approved June 28, 1985.
    ASTM Method G 21-70 (1984a), — Standard Practice for
    Determining Resistance of Synthetic Polymer Materials to Fungi.
    ASTM Method G 22-76 (1984b), — Standard Practice for
    Determining Resistance of Plastics to Bacteria.
    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.
    “Test Methods for Evaluating Solid Waste, Physical/Chemical
    Methods”, USEPA Publication number SW-846 (Third Edition,
    November, 1986), as amended by Updates I (July, 1992), II
    (September, 1994), IIA (August, 1993), IIB (January, 1995), and
    III (December, 1996) (Document Number 955-001-00000-1).
    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

    91
    Buried, or Submerged Liquid Storage Systems”, NACE
    Recommended Practice RP-02-85, approved March, 1985.
    NFPA. Available from the National Fire Protection Association,
    Batterymarch Park, Boston, MA 02269, 617-770-3000 or 800-344-3555:
    “Flammable and Combustible Liquids Code” NFPA 30, issued
    July 17, 1987. 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:
    APTI Course 415: Control of Gaseous Emissions, USEPA
    Publication EPA-450/2-81-005, December, 1981.
    “Generic Quality Assurance Project Plan for Land Disposal
    Restrictions Program”, EPA/530-SW-87-011, March 15, 1987
    (Document document number PB 88-170766).
    “Guideline on Air Quality Models”, Revised 1986. (Document
    document number PB86-245-248 (Guideline) and PB88-150-958
    (Supplement), also set forth at 40 CFR 51, Appendix W).
    “Method 164, Revision A, n-Hexane Extractable Material (HEM;
    Oil and Grease) and Silica Gel Treated n-Hexane Extractable
    Material (SGT-HEM; Non-polar Material) by Extraction and
    Gravimetry.” Document (document number PB99-121949).
    “Methods for Chemical Analysis of Water and Wastes”, Third
    Edition, March, 1983 (Document document number PB 84-
    128677).
    “Methods Manual for Compliance with BIF Regulations”,
    December, 1990 (Document document number PB91-120-006).
    “Petitions to Delist Hazardous Wastes — A Guidance Manual,
    Second Edition”, EPA/530-R-93-007, March, 1993 (Document
    Number document number PB 93-169 365).
    “Screening Procedures for Estimating the Air Quality Impact of
    Stationary Sources”, October, 1992, Publication Number EPA-
    450/R-92-019.
    “Test Methods for Evaluating Solid Waste, Physical/Chemical

    92
    Methods”, USEPA Publication number SW-846 (Third Edition,
    November 1986), as amended by Updates I (July 1992), II
    (September 1994), IIA (August 1993), IIB (January 1995), III
    (December 1996), and IIIA (April 1998) (Document Number
    document number 955-001-00000-1).
    OECD. Organisation for Economic Co-operation and Development,
    Environment Directorate, 2 rue Andre Pascal, 75775 Paris Cedex 16,
    France):
    OECD Guideline for Testing of Chemicals, Method 301B: “CO
    2
    Evolution (Modified Sturm Test)”, adopted 17 July 1992.
    Table 2.B of the Annex of OECD Council Decision
    C(88)90(Final) of 27 May 1988.
    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).
    U.S. DODUSDOD. Available from the United States Department of
    Defense:
    “DOD Ammunition and Explosive Safety Standards” (DOD
    6055.9-STD), as in effect on November 8, 1995.
    The Motor Vehicle Inspection Report (DD Form 626), as in effect
    on November 8, 1995.
    Requisition Tracking Form (DD Form 1348), as in effect on
    November 8, 1995.
    The Signature and Tally Record (DD Form 1907), as in effect on
    November 8, 1995.
    Special Instructions for Motor Vehicle Drivers (DD Form 836),
    as in effect on November 8, 1995.
    USEPA. 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

    93
    Control in Injection Wells”, EPA 570/9-87-002, August, 1987.
    USEPA. Available from Receptor Analysis Branch, USEPA (MD-14),
    Research Triangle Park, NC 27711:
    “Screening Procedures for Estimating the Air Quality Impact of
    Stationary Sources, Revised”, October, 1992, Publication
    Number EPA-450/R-92-019.
    USEPA. Available from RCRA Information Center (RIC), 1235
    Jefferson-Davis Highway, first floor, Arlington, VA 22203 (Docket # F-
    94-IEHF-FFFFF):
    OECD Amber List of Wastes, Appendix 4 to the OECD Council
    Decision C(92)39/FINAL (Concerning the Control of
    Transfrontier Movements of Wastes Destined for Recovery
    Operations) (May 1993).
    OECD Green List of Wastes, Appendix 3 to the OECD Council
    Decision C(92)39/FINAL (Concerning the Control of
    Transfrontier Movements of Wastes Destined for Recovery
    Operations) (May 1994).
    OECD Red List of Wastes, Appendix 5 to the OECD Council
    Decision C(92)39/FINAL (Concerning the Control of
    Transfrontier Movements of Wastes Destined for Recovery
    Operations) (May 1993).
    Table 2.B of the Annex of OECD Council Decision
    C(88)90(Final) (May 27, 1988).
    U.S. GSA. Available from the United States Government Services
    Administration:
    Government Bill of Lading (GBL) (GSA Standard Form 1109), as
    in effect on November 8, 1995.
    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, Appendix B (19981999)
    40 CFR 51.100(ii) (19981999)
    40 CFR 51, Appendix W (19981999)

    94
    40 CFR 52.741, Appendix B (19981999)
    40 CFR 60 (19981999)
    40 CFR 61, Subpart V (19981999)
    40 CFR 63 (19981999)
    40 CFR 136 (19981999), as corrected at 63 Fed. Reg. 38756 (July 20,
    1998) and 63 Fed. Reg. 44146 (Aug. 18, 1998) and amended at 63 Fed.
    Reg. 50387 (Sep. 21, 1998), 64 Fed. Reg. 4975 (Feb. 2, 1999), 64 Fed.
    Reg. 26315 (May 14, 1999), and 64 Fed. Reg. 30417 73414 (June
    8December 30, 1999)
    40 CFR 142 (19981999)
    40 CFR 220 (19981999)
    40 CFR 232.2 (19981999)
    40 CFR 260.20 (19981999)
    40 CFR 264 (19981999)
    40 CFR 268.41 (1990)
    40 CFR 268.Appendix IX (19981999)
    40 CFR 270.5 (19981999)
    40 CFR 302.4, 302.5, and 302.6 (19981999)
    40 CFR 761 (19981999)
    49 CFR 171 (19981999)
    49 CFR 173 (19981999)
    49 CFR 178 (19981999)
    c)
    Federal Statutes
    Section 3004 of the Resource Conservation and Recovery Act (42 USC
    6901 et seq.), as amended through December 31, 1987.

    95
    Sections 201(v), 201(w), and 360b(j) of the Federal Food, Drug, and
    Cosmetic Act (FFDCA; 21 USC 321(v), 321(w), and 512(j)), as
    amended through October 25, 1994.
    Section 1412 of the Department of Defense Authorization Act of 1986,
    Pub. L. 99-145, 50 USC 1521(j)(1) (1997).
    d)
    This Section incorporates no later editions or amendments.
    (Source: Amended at 24 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

    96
    721.123
    Characteristic of Reactivity
    721.124
    Toxicity Characteristic
    SUBPART D: LISTS OF HAZARDOUS WASTE
    Section
    721.130
    General
    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 U.S. EPA under 40 CFR 260.20 and 260.22 from
    Non-Specific Sources
    Table B
    Wastes Excluded by USEPA under 40 CFR 260.20 and 260.22 from
    Specific Sources
    Table C
    Wastes Excluded by U.S. EPA under 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, 43 PCB 427, at 5 Ill. Reg. 9781, effective May 17, 1982;
    amended and codified in R81-22, 45 PCB 317, at 6 Ill. Reg. 4828, effective May 17, 1982;
    amended in R82-18, 51 PCB 31, at 7 Ill. Reg. 2518, effective February 22, 1983; amended in
    R82-19, 53 PCB 131, at 7 Ill. Reg. 13999, effective October 12, 1983; amended in R84-34, 61
    PCB 247, 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

    97
    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;
    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. ________, effective ______________________.
    SUBPART A: GENERAL PROVISIONS
    Section 721.109
    Requirements for Universal Waste
    The wastes listed in this Section are exempt from regulation under 35 Ill. Adm. Code 702
    through 705, 722 through 726, and 728, except as specified in 35 Ill. Adm. Code 733, and are
    therefore not fully regulated as hazardous waste. The wastes listed in this Section are subject to
    regulation under 35 Ill. Adm. Code 733:
    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; and
    d)
    Mercury-containing lampsLamps, as described in 35 Ill. Adm. Code 733.107
    733.105.

    98
    BOARD NOTE: Subsection (d) of this Section was added pursuant to Section
    22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
    1997).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    SUBPART D: LISTS OF HAZARDOUS WASTE
    Section 721.132
    Hazardous Waste from Specific Sources
    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 in Appendix I of this Part.
    USEPA
    Hazardous
    Waste No.
    Industry and Hazardous Waste
    Hazard
    Code
    Wood Preservation:
    K001
    Bottom sediment sludge from the treatment of wastewaters from
    wood preserving processes that use creosote or pentachloro-
    phenol.
    (T)
    Inorganic Pigments:
    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)

    99
    K008
    Oven residue from the production of chrome oxide green
    pigments.
    (T)
    Organic Chemicals:
    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)
    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)

    100
    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)
    K027
    Centrifuge and distillation residues from toluene diisocyanate
    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-trichloroethane.
    (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)

    101
    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-di-
    methylhydrazine (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)
    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 dinitrotoluene 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 toluenedi-
    amine 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 di-
    nitrotoluene.
    (T)
    K116
    Organic condensate from the solvent recovery column in the
    production of toluene diisocyanate via phosgenation of toluenedi-
    amine.
    (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 dibromide in
    the production of ethylene dibromide via bromination of ethene.
    (T)

    102
    K136
    Still bottoms from the purification of ethylene dibromide in the
    production of ethylene dibromide via bromination of ethene.
    (T)
    K140
    Floor sweepings, off-specification product and spent filter media
    from the production of 2,4,6-tribromophenol.
    (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)
    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
    Bag house 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)
    Inorganic Chemicals:
    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)

    103
    Pesticides:
    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 cyclopenta-
    diene in the production of chlordane.
    (T)
    K034
    Filter solids from the filtration of hexachlorocyclopentadiene in
    the production of chlordane.
    (T)
    K097
    Vacuum stripper discharge from the chlordane chlorinator in the
    production of chlordane.
    (T)
    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 disulfoton.
    (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 tetra-
    chlorobenzene 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)

    104
    K123
    Process wastewater (including supernates, filtrates and
    washwaters) from the production of ethylenebisdithiocarbamic
    acid and its salts.
    (T)
    K124
    Reactor vent scrubber water from the production of ethylenebis-
    dithiocarbamic 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 ethylenebisdi-
    thiocarbamic acid and its salts.
    (T)
    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:
    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:
    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)

    105
    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)
    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:
    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 Copper:
    K064
    Acid plant blowdown slurry or sludge resulting from the
    thickening of blowdown slurry from primary copper production.
    (T)
    Primary Lead:
    K065
    Surface impoundment solids contained in and dredged from
    surface impoundments at primary lead smelting facilities.
    (T)
    Primary Zinc:
    K066
    Sludge from treatment of process wastewater or acid plant
    blowdown from primary zinc production.
    (T)
    BOARD NOTE: This waste listing is the subject of a judicial remand in American Mining
    Congress v. EPA, 907 F.2d 1179 (D.D.C. 1990). The Board intends that this listing not
    become enforceable in Illinois until the first date upon which the Board RCRA program
    becomes “not equivalent to the Federal program”, within the meaning of section 3006(b) of the
    RCRA Act, 42 USC 6926(b), the Board RCRA rules become “less stringent” than the

    106
    USEPA rules, as this phrase is used in section 3009, 42 USC 6929, or the Board RCRA rules
    are not “identical in substance” with the federal rules as that term is intended by 415 ILCS
    5/7.2 and 22.4 as a result of some action by USEPA with regard to this listing in response to
    the American Mining Congress remand.
    Primary Aluminum:
    K088
    Spent potliners from primary aluminum reduction.
    (T)
    Ferroalloys:
    K090
    Emission control dust or sludge from ferrochromiumsilicon
    production.
    (T)
    K091
    Emission control dust or sludge from ferrochromium production.
    (T)
    Secondary Lead:
    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:
    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)
    K102
    Residue from use of activated carbon for decolorization in the
    production of veterinary pharmaceuticals from arsenic or
    organo-arsenic compounds.
    (T)

    107
    Ink Formulation:
    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)
    Coking:
    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)
    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)

    108
    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)
    (Source: Amended at 24 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.
    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 (N
    2
    );
    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

    109
    target list of Appendix H constituents.
    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;
    ii)
    If the generator is a company that generates comparable or
    syngas fuel at more than one facility, the generator shall
    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 unit(s) units that will burn the
    comparable or syngas fuel;
    iii)
    A brief, general description of the manufacturing,

    110
    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 code(s) codes for
    the hazardous waste;
    iii)
    The name and address of the units that meet the
    requirements of subsection (c)(2) of this Section which that
    will burn the comparable or syngas fuel; and
    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

    111
    (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 subsection (a) or (b) and (c)(1) of this Section applies
    only if the fuel is burned in the following units that also shall 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;
    C)
    Hazardous waste incinerators subject to regulation under 35 Ill.
    Adm. Code 724.Subpart O or 35 Ill. Adm. Code 725.Subpart O
    or applicable CAA MACT standards.
    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

    112
    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
    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 shall in any way dilute a hazardous waste to meet the
    exclusion specifications of subsection (a)(1)(A), (a)(2) or (b) of this
    Section.

    113
    7)
    Waste analysis plans. The generator of a comparable or syngas fuel shall
    develop and follow a written waste analysis plan which describes the
    procedures for sampling and analysis of the hazardous waste to be
    excluded. The waste analysis plan shall be developed in accordance with
    the applicable sections of the “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods” (SW-846). The plan shall 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 which that will be used to test for these
    parameters;
    iii)
    The sampling method which 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
    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 person(s) 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

    114
    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 which 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 shall 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
    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;

    115
    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.
    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.
    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:
    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 which generates a solid waste to determine if that
    waste is a hazardous waste.
    E)
    In an enforcement action, the burden of proof to establish

    116
    conformance with the exclusion specification shall 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 shall 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 re-tested 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
    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;

    117
    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 includes 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 person(s) persons that
    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;

    118
    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 which 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 shall 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
    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 shall 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 their fuel off-site

    119
    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:
    Chemical name
    CAS No
    Concentration
    limit (mg/kg at
    10,000 Btu/lb)
    Minimum re-
    quired detection
    limit (mg/kg)
    Total Nitrogen as N
    na
    4900
    Total Halogens as Cl
    na
    540
    Total Organic Halogens as
    Cl
    na
    25 or individual
    halogenated
    organics listed
    below.
    Polychlorinated biphenyls,
    total [Arocolors, total]
    a
    1336-36-3
    Non-detect
    1.4
    Cyanide, total
    57-12-5
    Non-detect
    1.0
    Metals:
    Antimony, total
    7440-36-0
    7.9
    Arsenic, total
    7440-38-2
    0.23
    Barium, total
    7440-39-3
    23
    Beryllium, total
    7440-41-7
    1.2
    Cadmium, total
    7440-43-9
    1.2
    Chromium, total
    7440-47-3
    2.3
    Cobalt
    7440-48-4
    4.6

    120
    Lead, total
    7439-92-1
    31
    Manganese
    7439-96-5
    1.2
    Mercury, total
    7439-97-6
    0.24
    Nickel, total
    7440-02-0
    58
    Selenium, total
    7782-49-2
    0.15
    Silver, total
    7440-22-4
    2.3
    Thallium, total
    7440-28-0
    23
    Hydrocarbons:
    Benzo[a]anthracene
    56-55-3
    1100
    Benzene
    71-43-2
    4100
    Benzo[b]fluoranthene
    205-99-2
    960
    Benzo[k]fluoranthene
    207-08-9
    1900
    Benzo[a]pyrene
    50-32-8
    960
    Chrysene
    218-01-9
    1400
    Dibenzo[a,h]anthracene
    53-70-3
    960
    7,12-Dimethylbenz[a]-
    anthracene
    57-97-6
    1900
    Fluoranthene
    206-44-0
    1900
    Indeno(1,2,3-cd)pyrene
    193-39-5
    960
    3-Methylcholanthrene
    56-49-5
    1900
    Naphthalene
    91-20-3
    3200
    Toluene
    108-88-3
    36000
    Oxygetes:
    Acetophenone
    98-86-2
    1900
    Acrolein
    107-02-8
    37
    Allyl alcohol
    107-18-6
    30
    Bis(2-ethylhexyl)-
    phthalate [Di-2-ethyl-
    hexyl phthalate]
    117-81-7
    1900
    Butyl benzyl phthalate
    85-68-7
    1900
    o-Cresol [2-Methyl
    phenol]
    95-48-7
    220
    m-Cresol [3-Methyl
    phenol]
    108-39-4
    220
    p-Cresol [4-Methyl
    phenol]
    106-44-5
    220
    Di-n-butyl phthalate
    84-74-2
    1900
    Diethyl phthalate
    84-66-2
    1900
    2,4-Dimethylphenol
    105-67-9
    1900
    Dimethyl phthalate
    131-11-3
    1900
    Di-n-octyl phthalate
    117-84-0
    960
    Endothall
    145-73-3
    100
    Ethyl methacrylate
    97-63-2
    37

    121
    2-Ethoxyethanol
    [Ethylene glycol
    monoethyl ether].
    110-80-5
    100
    Isobutyl alcohol
    78-83-1
    37
    Isosafrole
    120-58-1
    1900
    Methyl ethyl ketone [2-
    Butanone]
    78-93-3
    37.
    Methyl methacrylate
    80-62-6
    37.
    1,4-Naphthoquinone
    130-15-4
    1900.
    Phenol
    108-95-2
    1900.
    Propargyl alcohol [2-
    Propyn-l-ol]
    107-19-7
    30.
    Safrole
    94-59-7
    1900.
    Sulfonated Organics:
    Carbon disulfide
    75-15-0
    Non-detect
    37
    Disulfoton
    298-04-4
    Non-detect
    1900
    Ethyl methanesulfonate
    62-50-0
    Non-detect
    1900
    Methyl methane-
    sulfonate
    66-27-3
    Non-detect
    1900
    Phorate
    298-02-2
    Non-detect
    1900
    1,3-Propane sultone
    1120-71-4
    Non-detect
    100
    Tetraethyldithiopyro-
    phosphate [Sulfotepp]
    3689-24-5
    Non-detect
    1900
    Thiophenol [Benzene-
    thiol]
    108-98-5
    Non-detect
    30
    O,O,O-Triethyl
    phosphorothioate
    126-68-1
    Non-detect
    1900
    Nitrogenated Organics:
    Acetonitrile [Methyl
    cyanide]
    75-05-8
    Non-detect
    37
    2-Acetylaminofluorene
    [2-AAF]
    53-96-3
    Non-detect
    1900
    Acrylonitrile
    107-13-1
    Non-detect
    37
    4-Aminobiphenyl
    92-67-1
    Non-detect
    1900
    4-Aminopyridine
    504-24-5
    Non-detect
    100
    Aniline
    62-53-3
    Non-detect
    1900
    Benzidine
    92-87-5
    Non-detect
    1900
    Dibenz[a,j]acridine
    224-42-0
    Non-detect
    1900
    O,O-Diethyl O-
    pyrazinyl phophoro-
    thioate [Thionazin].
    297-97-2
    Non-detect
    1900
    Dimethoate
    60-51-5
    Non-detect
    1900

    122
    p-(Dimethylamino)azo-
    benzene [4-Dimethyl-
    aminoazobenzene].
    60-11-7
    Non-detect
    1900
    3,3'-Dimethylbenzidine
    119-93-7
    Non-detect
    1900
    a,a-Dimethylphenethyl-
    amine.
    122-09-8
    Non-detect
    1900
    3,3'-Dimethoxy-
    benzidine
    119-90-4
    Non-detect
    100
    1,3-Dinitrobenzene [m-
    Dinitrobenzene]
    99-65-0
    Non-detect
    1900
    4,6-Dinitro-o-cresol
    534-52-1
    Non-detect
    1900
    2,4-Dinitrophenol
    51-28-5
    Non-detect
    1900
    2,4-Dinitrotoluene
    121-14-2
    Non-detect
    1900
    2,6-Dinitrotoluene
    606-20-2
    Non-detect
    1900
    Dinoseb [2-sec-Butyl-
    4,6-dinitrophenol]
    88-85-7
    Non-detect
    1900
    Diphenylamine
    122-39-4
    Non-detect
    1900
    Ethyl carbamate
    [Urethane]
    51-79-6
    Non-detect
    100
    Ethylenethiourea (2-
    Imidazolidinethione)
    96-45-7
    Non-detect
    110
    Famphur
    52-85-7
    Non-detect
    1900
    Methacrylonitrile
    126-98-7
    Non-detect
    37
    Methapyrilene
    91-80-5
    Non-detect
    1900
    Methomyl
    16752-77-5
    Non-detect
    57
    2-Methyllactonitrile
    [Acetone cyanohydrin].
    75-86-5
    Non-detect
    100
    Methyl parathion
    298-00-0
    Non-detect
    1900
    MNNG (N-Metyl-N-
    nitroso-N’-nitro-
    guanidine)
    70-25-7
    Non-detect
    110
    1-Naphthylamine, [
    α
    -
    Naphthylamine]
    134-32-7
    Non-detect
    1900
    2-Naphthylamine, [
    β
    -
    Naphthylamine]
    91-59-8
    Non-detect
    1900
    Nicotine
    54-11-5
    Non-detect
    100
    4-Nitroaniline, [p-
    Nitroaniline]
    100-01-6
    Non-detect
    1900
    Nitrobenzene
    98-95-3
    Non-detect
    1900
    p-Nitrophenol, [p-
    Nitrophenol]
    100-02-7
    Non-detect
    1900
    5-Nitro-o-toluidine
    99-55-8
    Non-detect
    1900

    123
    N-Nitrosodi-n-butyl-
    amine
    924-16-3
    Non-detect
    1900
    N-Nitrosodiethylamine
    55-18-5
    Non-detect
    1900
    N-Nitrosodiphenyl-
    amine, [Diphenylnitros-
    amine]
    86-30-6
    Non-detect
    1900
    N-Nitroso-N-methyl-
    ethylamine
    10595-95-6
    Non-detect
    1900
    N-Nitrosomorpholine
    59-89-2
    Non-detect
    1900
    N-Nitrosopiperidine
    100-75-4
    Non-detect
    1900
    N-Nitrosopyrrolidine
    930-55-2
    Non-detect
    1900
    2-Nitropropane
    79-46-9
    Non-detect
    30
    Parathion
    56-38-2
    Non-detect
    1900
    Phenacetin
    62-44-2
    Non-detect
    1900
    1,4-Phenylene diamine,
    [p-Phenylenediamine]
    106-50-3
    Non-detect
    1900
    N-Phenylthiourea
    103-85-5
    Non-detect
    57
    2-Picoline [alpha-
    Picoline]
    109-06-8
    Non-detect
    1900
    Propythioracil [6-
    Propyl-2-thiouracil]
    51-52-5
    Non-detect
    100
    Pyridine
    110-86-1
    Non-detect
    1900
    Strychnine
    57-24-9
    Non-detect
    100
    Thioacetamide
    62-55-5
    Non-detect
    57
    Thiofanox
    39196-18-4
    Non-detect
    100
    Thiourea
    62-56-6
    Non-detect
    57
    Toluene-2,4-diamine
    [2,4-Diaminotoluene]
    95-80-7
    Non-detect
    57
    Toluene-2,6-diamine
    [2,6-Diaminotoluene]
    823-40-5
    Non-detect
    57
    o-Toluidine
    95-53-4
    Non-detect
    2200
    p-Toluidine
    106-49-0
    Non-detect
    100
    1,3,5-Trinitrobenzne,
    [sym-Trinitobenzene]
    99-35-4
    Non-detect
    2000
    Halogenated Organics
    b
    :
    Allyl chloride
    107-05-1
    Non-detect
    37
    Aramite
    104-57-8
    Non-detect
    1900
    Benzal chloride [Di-
    chloromethyl benzene]
    98-87-3
    Non-detect
    100
    Benzyl chloride
    100-44-77
    Non-detect
    100
    Bis(2-chloroethyl)ether
    [Dichloroethyl ether]
    111-44-4
    Non-detect
    1900

    124
    Bromoform [Tribromo-
    methane]
    75-25-2
    Non-detect
    37
    Bromomethane [Methyl
    bromide]
    74-83-9
    Non-detect
    37
    4-Bromophenyl phenyl
    ether [p-Bromodiphenyl
    ether]
    101-55-3
    Non-detect
    1900
    Carbon tetrachloride
    56-23-5
    Non-detect
    37
    Chlordane
    57-74-9
    Non-detect
    14
    p-Chloroaniline
    106-47-8
    Non-detect
    1900
    Chlorobenzene
    108-90-7
    Non-detect
    37
    Chlorobenzilate
    510-15-6
    Non-detect
    1900
    p-Chloro-m-cresol
    59-50-7
    Non-detect
    1900
    2-Chloroethyl vinyl
    ether
    110-75-8
    Non-detect
    37
    Chloroform
    67-66-3
    Non-detect
    37
    Chloromethane [Methyl
    chloride]
    74-87-3
    Non-detect
    37
    2-Chlorophthalene
    [beta-Chlorophthalene]
    91-58-7
    Non-detect
    1900
    2-Chlorophenol [o-
    Chlorophenol]
    95-57-8
    Non-detect
    1900
    Chloroprene [2-Chloro-
    1,3-butadiene]
    1126-99-8
    Non-detect
    37
    2,4-D [2,4-Dichloro-
    phenoxyacetic acid]
    94-75-7
    Non-detect
    7.0
    Diallate
    2303-16-4
    Non-detect
    1900
    1,2-Dibromo-3-chloro-
    propane
    96-12-8
    Non-detect
    37
    1,2-Dichlorobenzene
    [o-Dichlorobenzene]
    95-50-1
    Non-detect
    1900
    1,3-Dichlorobenzene
    [m-Dichlorobenzene]
    541-73-1
    Non-detect
    1900
    1,4-Dichlorobenzene
    [p-Dichlorobenzene]
    106-46-7
    Non-detect
    1900
    3,3'-Dichlorobenzidine
    91-94-1
    Non-detect
    1900
    Dichlorodifluoro-
    methane [CFC-12]
    75-71-8
    Non-detect
    37
    1,2-Dichloroethane
    [Ethylene dichloride]
    107-06-2
    Non-detect
    37
    1,1-Dichloroethylene
    [Vinylidene chloride]
    75-35-4
    Non-detect
    37

    125
    Dichloromethoxy
    ethane [Bis(2-chloro-
    ethoxy)methane
    111-91-1
    Non-detect
    1900
    2,4-Dichlorophenol
    120-83-2
    Non-detect
    1900
    2,6-Dichlorophenol
    87-65-0
    Non-detect
    1900
    1,2-Dichloropropane
    [Propylene dichloride]
    78-87-5
    Non-detect
    37
    cis-1,3-Dichloro-
    propylene
    10061-01-5
    Non-detect
    37
    trans-1,3-Dichloro-
    propylene
    10061-02-6
    Non-detect
    37
    1,3-Dichloro-2-
    propanol
    96-23-1
    Non-detect
    30
    Endosulfan I
    959-98-8
    Non-detect
    1.4
    Endosulfan II
    33213-65-9
    Non-detect
    1.4
    Endrin
    72-20-8
    Non-detect
    1.4
    Endrin aldehyde
    7421-93-4
    Non-detect
    1.4
    Endrin Ketone
    53494-70-5
    Non-detect
    1.4
    Epichlorohydrin [1-
    Chloro-2,3-epoxy
    propane]
    106-89-8
    Non-detect
    30
    Ethylidene dichloride
    [1,1-Dichloroethane]
    75-34-3
    Non-detect
    37
    2-Fluoroacetamide
    640-19-7
    Non-detect
    100
    Heptachlor
    76-44-8
    Non-detect
    1.4
    Heptachlor epoxide
    1024-57-3
    Non-detect
    2.8
    Hexachlorobenzene
    118-74-1
    Non-detect
    1900
    Hexachloro-1,3-buta-
    diene [Hexachlorobuta-
    diene]
    87-68-3
    Non-detect
    1900
    Hexachlorocyclopenta-
    diene
    77-47-4
    Non-detect
    1900
    Hexachloroethane
    67-72-1
    Non-detect
    1900
    Hexachlorophene
    70-30-4
    Non-detect
    1000
    Hexachloropropene
    [Hexachloropropylene]
    1888-71-7
    Non-detect
    1900
    Isodrin
    465-73-6
    Non-detect
    1900
    Kepone [Chlordecone]
    143-50-0
    Non-detect
    3600
    Lindane [gamma-Hexa-
    chlorocyclohexane]
    [gamma-BHC]
    58-89-9
    non-detect
    1.4
    Methylene chloride
    [Dichloromethane]
    75-09-2
    non-detect
    37

    126
    4,4'-methylene-bis(2-
    chloroaniline)
    101-14-4
    non-detect
    100
    Methyl iodide [Iodo-
    methane]
    74-88-4
    non-detect
    37
    Pentachlorobenzene
    608-93-5
    non-detect
    1900
    Pentachloroethane
    76-01-7
    non-detect
    37
    Pentachloronitro-
    benzene [PCNB]
    [Quintobenzene]
    [Quintozene]
    82-68-8
    non-detect
    1900
    Pentachlorophenol
    87-86-5
    non-detect
    1900
    Pronamide
    23950-58-5
    non-detect
    1900
    Silvex [2,4,5-Trichloro-
    phenoxypropionic acid]
    93-72-1
    non-detect
    7.0
    2,3,7,8-Tetrachloro-
    dibenzo-p-dioxin
    [2,3,7,8-TCDD]
    1746-01-6
    non-detect
    30
    1,2,4,5-Tetrachloro-
    benzene
    95-94-3
    non-detect
    1900
    1,1,2,2-Tetrachloro-
    ethane
    79-34-5
    non-detect
    37
    Tetrachloroethylene
    [Perchloroethylene]
    127-18-4
    non-detect
    37
    2,3,4,6-Tetrachloro-
    phenol
    58-90-2
    non-detect
    1900
    1,2,4-Trichlorobenzene
    120-82-1
    non-detect
    1900
    1,1,1-Trichloroethane
    [Methyl chloroform]
    71-55-6
    non-detect
    37
    1,1,2-Trichloroethane
    [Vinyl trichloride]
    79-00-5
    non-detect
    37
    Trichloroethylene
    79-01-6
    non-detect
    37
    Trichlorofluoromethane
    [Trichloromonofluoro-
    methane]
    75-69-4
    non-detect
    37
    2,4,5-Trichlorophenol
    95-95-4
    non-detect
    1900
    2,4,6-Trichlorophenol
    88-06-2
    non-detect
    1900
    1,2,3-Trichloropropane
    96-18-4
    non-detect
    37
    Vinyl Chloride
    75-01-4
    non-detect
    37
    a
    Absence of PCBs can also be demonstrated by using appropriate screening
    methods, e.g., immunoassay kit for PCB in oils (Method 4020) or colorimetric
    analysis for PCBs in oil (Method 9079).
    b
    Some minimum required detection limits are above the total halogen limit of

    127
    540 ppm. The detection limits reflect what was achieved during USEPA testing
    and analysis and also analytical complexity associated with measuring all halogen
    compounds on Appendix H of this Part at low levels. USEPA stated that it
    recognizes that in practice the presence of these compounds will be functionally
    limited by the molecular weight and the total halogen limit of 540 ppm.
    (Source: Amended at 24 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)
    Total Nitrogen as N
    NA
    9000
    18400
    4900
    Total Halogens as Cl
    NA
    1000
    18400
    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
    31
    Manganese
    7439-96-5
    ND
    --
    1.2
    Mercury, total
    7439-97-6
    ND
    --
    0.25
    Nickel, total
    7440-02-0
    106
    18400
    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
    --
    2400
    Benzene
    71-43-2
    8000
    19600
    4100
    Benzo[b]fluoranthene
    205-99-2
    ND
    --
    2400
    Benzo[k]fluoranthene
    207-08-9
    ND
    --
    2400
    Benzo[a]pyrene
    50-32-8
    ND
    --
    2400

    128
    Chrysene
    218-01-9
    ND
    --
    2400
    Dibenzo[a,h]anthracene
    53-70-3
    ND
    --
    2400
    7,12-Dimethylbenz[a]-
    anthracene
    57-97-6
    ND
    --
    2400
    Fluoranthene
    206-44-0
    ND
    --
    2400
    Indeno(1,2,3-cd)pyrene
    193-39-5
    ND
    --
    2400
    3-Methylcholanthrene
    56-49-5
    ND
    --
    2400
    Naphthalene
    91-20-3
    6200
    19400
    3200
    Toluene
    108-88-3
    69000
    19400
    36000
    Oxygetes:
    Acetophenone
    98-86-2
    ND
    --
    2400
    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
    --
    2400
    Butyl benzyl phthalate
    85-68-7
    ND
    --
    2400
    o-Cresol [2-Methyl
    phenol]
    95-48-7
    ND
    --
    2400
    m-Cresol [3-Methyl
    phenol]
    108-39-4
    ND
    --
    2400
    p-Cresol [4-Methyl
    phenol]
    106-44-5
    ND
    --
    2400
    Di-n-butyl phthalate
    84-74-2
    ND
    --
    2400
    Diethyl phthalate
    84-66-2
    ND
    --
    2400
    2,4-Dimethylphenol
    105-67-9
    ND
    --
    2400
    Dimethyl phthalate
    131-11-3
    ND
    --
    2400
    Di-n-octyl phthalate
    117-84-0
    ND
    --
    2400
    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
    --
    1900
    Methyl ethyl ketone [2-
    Butanone]
    78-93-3
    ND
    --
    39
    Methyl methacrylate
    80-62-6
    ND
    --
    39
    1,4-Naphthoquinone
    130-15-4
    ND
    --
    2400
    Phenol
    108-95-2
    ND
    --
    2400
    Propargyl alcohol [2-
    Propyn-l-ol]
    107-19-7
    ND
    --
    30.
    Safrole
    94-59-7
    ND
    --
    2400

    129
    Sulfonated Organics:
    Carbon disulfide
    75-15-0
    ND
    --
    ND
    39
    Disulfoton
    298-04-4
    ND
    --
    ND
    2400
    Ethyl methanesulfonate
    62-50-0
    ND
    --
    ND
    2400
    Methyl methane-
    sulfonate
    66-27-3
    ND
    --
    ND
    2400
    Phorate
    298-02-2
    ND
    --
    ND
    2400
    1,3-Propane sultone
    1120-71-4
    ND
    --
    ND
    100
    Tetraethyldithiopyro-
    phosphate [Sulfotepp]
    3689-24-5
    ND
    --
    ND
    2400
    Thiophenol [Benzene-
    thiol]
    108-98-5
    ND
    --
    ND
    30
    O,O,O-Triethyl
    phosphorothioate
    126-68-1
    ND
    --
    ND
    2400
    Nitrogenated Organics:
    Acetonitrile [Methyl
    cyanide]
    75-05-8
    ND
    --
    ND
    39
    2-Acetylaminofluorene
    [2-AAF]
    53-96-3
    ND
    --
    ND
    2400
    Acrylonitrile
    107-13-1
    ND
    --
    ND
    39
    4-Aminobiphenyl
    92-67-1
    ND
    --
    ND
    2400
    4-Aminopyridine
    504-24-5
    ND
    --
    ND
    100
    Aniline
    62-53-3
    ND
    --
    ND
    2400
    Benzidine
    92-87-5
    ND
    --
    ND
    2400
    Dibenz[a,j]acridine
    224-42-0
    ND
    --
    ND
    2400
    O,O-Diethyl O-
    pyrazinyl phophoro-
    thioate [Thionazin].
    297-97-2
    ND
    --
    ND
    2400
    Dimethoate
    60-51-5
    ND
    --
    ND
    2400
    p-(Dimethylamino)azo-
    benzene [4-Dimethyl-
    aminoazobenzene].
    60-11-7
    ND
    --
    ND
    2400
    3,3'-Dimethylbenzidine
    119-93-7
    ND
    --
    ND
    2400
    a,a-Dimethylphenethyl-
    amine.
    122-09-8
    ND
    --
    ND
    2400
    3,3'-Dimethoxy-
    benzidine
    119-90-4
    ND
    --
    ND
    100
    1,3-Dinitrobenzene [m-
    Dinitrobenzene]
    99-65-0
    ND
    --
    ND
    2400
    4,6-Dinitro-o-cresol
    534-52-1
    ND
    --
    ND
    2400
    2,4-Dinitrophenol
    51-28-5
    ND
    --
    ND
    2400
    2,4-Dinitrotoluene
    121-14-2
    ND
    --
    ND
    2400
    2,6-Dinitrotoluene
    606-20-2
    ND
    --
    ND
    2400

    130
    Dinoseb [2-sec-Butyl-
    4,6-dinitrophenol]
    88-85-7
    ND
    --
    ND
    2400
    Diphenylamine
    122-39-4
    ND
    --
    ND
    2400
    Ethyl carbamate
    [Urethane]
    51-79-6
    ND
    --
    ND
    100
    Ethylenethiourea (2-
    Imidazolidinethione)
    96-45-7
    ND
    --
    ND
    110
    Famphur
    52-85-7
    ND
    --
    ND
    2400
    Methacrylonitrile
    126-98-7
    ND
    --
    ND
    39
    Methapyrilene
    91-80-5
    ND
    --
    ND
    2400
    Methomyl
    16752-77-5
    ND
    --
    ND
    57
    2-Methyllactonitrile
    [Acetone cyanohydrin].
    75-86-5
    ND
    --
    ND
    100
    Methyl parathion
    298-00-0
    ND
    --
    ND
    2400
    MNNG (N-Metyl-N-
    nitroso-N’-nitro-
    guanidine)
    70-25-7
    ND
    --
    ND
    110
    1-Naphthylamine, [
    α
    -
    Naphthylamine]
    134-32-7
    ND
    --
    ND
    2400
    2-Naphthylamine, [
    β
    -
    Naphthylamine]
    91-59-8
    ND
    --
    ND
    2400
    Nicotine
    54-11-5
    ND
    --
    ND
    100
    4-Nitroaniline, [p-
    Nitroaniline]
    100-01-6
    ND
    --
    ND
    240
    Nitrobenzene
    98-95-3
    ND
    --
    ND
    2400
    p-Nitrophenol, [p-
    Nitrophenol]
    100-02-7
    ND
    --
    ND
    2400
    5-Nitro-o-toluidine
    99-55-8
    ND
    --
    ND
    2400
    N-Nitrosodi-n-butyl-
    amine
    924-16-3
    ND
    --
    ND
    2400
    N-Nitrosodiethylamine
    55-18-5
    ND
    --
    ND
    2400
    N-Nitrosodiphenyl-
    amine, [Diphenylnitros-
    amine]
    86-30-6
    ND
    --
    ND
    2400
    N-Nitroso-N-methyl-
    ethylamine
    10595-95-6
    ND
    --
    ND
    2400
    N-Nitrosomorpholine
    59-89-2
    ND
    --
    ND
    2400
    N-Nitrosopiperidine
    100-75-4
    ND
    --
    ND
    2400
    N-Nitrosopyrrolidine
    930-55-2
    ND
    --
    ND
    2400
    2-Nitropropane
    79-46-9
    ND
    --
    ND
    30
    Parathion
    56-38-2
    ND
    --
    ND
    2400
    Phenacetin
    62-44-2
    ND
    --
    ND
    2400

    131
    1,4-Phenylene diamine,
    [p-Phenylenediamine]
    106-50-3
    ND
    --
    ND
    2400
    N-Phenylthiourea
    103-85-5
    ND
    --
    ND
    57
    2-Picoline [alpha-
    Picoline]
    109-06-8
    ND
    --
    ND
    2400
    Propythioracil [6-
    Propyl-2-thiouracil]
    51-52-5
    ND
    --
    ND
    100
    Pyridine
    110-86-1
    ND
    --
    ND
    2400
    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
    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
    2400
    p-Toluidine
    106-49-0
    ND
    --
    ND
    100
    1,3,5-Trinitrobenzne,
    [sym-Trinitobenzene]
    99-35-4
    ND
    --
    ND
    2400
    Halogenated Organics:
    Allyl chloride
    107-05-1
    ND
    --
    ND
    39
    Aramite
    104-57-8
    ND
    --
    ND
    2400
    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
    2400
    Bromoform [Tribromo-
    methane]
    75-25-2
    ND
    --
    ND
    39
    Bromomethane [Methyl
    bromide]
    74-83-9
    ND
    --
    ND
    39
    4-Bromophenyl phenyl
    ether [p-Bromodiphenyl
    ether]
    101-55-3
    ND
    --
    ND
    2400
    Carbon tetrachloride
    56-23-5
    ND
    --
    ND
    39
    Chlordane
    57-74-9
    ND
    --
    ND
    14
    p-Chloroaniline
    106-47-8
    ND
    --
    ND
    2400
    Chlorobenzene
    108-90-7
    ND
    --
    ND
    39
    Chlorobenzilate
    510-15-6
    ND
    --
    ND
    2400
    p-Chloro-m-cresol
    59-50-7
    ND
    --
    ND
    2400
    2-Chloroethyl vinyl
    ether
    110-75-8
    ND
    --
    ND
    39

    132
    Chloroform
    67-66-3
    ND
    --
    ND
    39
    Chloromethane [Methyl
    chloride]
    74-87-3
    ND
    --
    ND
    39
    2-Chlorophthalene
    [beta-Chlorophthalene]
    91-58-7
    ND
    --
    ND
    2400
    2-Chlorophenol [o-
    Chlorophenol]
    95-57-8
    ND
    --
    ND
    2400
    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
    2400
    1,2-Dibromo-3-chloro-
    propane
    96-12-8
    ND
    --
    ND
    39
    1,2-Dichlorobenzene
    [o-Dichlorobenzene]
    95-50-1
    ND
    --
    ND
    2400
    1,3-Dichlorobenzene
    [m-Dichlorobenzene]
    541-73-1
    ND
    --
    ND
    2400
    1,4-Dichlorobenzene
    [p-Dichlorobenzene]
    106-46-7
    ND
    --
    ND
    2400
    3,3'-Dichlorobenzidine
    91-94-1
    ND
    --
    ND
    2400
    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
    2400
    2,4-Dichlorophenol
    120-83-2
    ND
    --
    ND
    2400
    2,6-Dichlorophenol
    87-65-0
    ND
    --
    ND
    2400
    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

    133
    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
    2400
    Hexachloro-1,3-buta-
    diene [Hexachlorobuta-
    diene]
    87-68-3
    ND
    --
    ND
    2400
    Hexachlorocyclopenta-
    diene
    77-47-4
    ND
    --
    ND
    2400
    Hexachloroethane
    67-72-1
    ND
    --
    ND
    2400
    Hexachlorophene
    70-30-4
    ND
    --
    ND
    59000
    Hexachloropropene
    [Hexachloropropylene]
    1888-71-7
    ND
    --
    ND
    2400
    Isodrin
    465-73-6
    ND
    --
    ND
    2400
    Kepone [Chlordecone]
    143-50-0
    ND
    --
    ND
    4700
    Lindane [gamma-Hexa-
    chlorocyclohexane]
    [gamma-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
    2400
    Pentachloroethane
    76-01-7
    ND
    --
    ND
    39
    Pentachloronitro-
    benzene [PCNB]
    [Quintobenzene]
    [Quintozene]
    82-68-8
    ND
    --
    ND
    2400
    Pentachlorophenol
    87-86-5
    ND
    --
    ND
    2400
    Pronamide
    23950-58-5
    ND
    --
    ND
    2400
    Silvex [2,4,5-Tri-
    chlorophenoxy-
    propionic 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

    134
    1,2,4,5-Tetrachloro-
    benzene
    95-94-3
    ND
    --
    ND
    2400
    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
    2400
    1,2,4-Trichlorobenzene
    120-82-1
    ND
    --
    ND
    2400
    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
    Trichlorofluoromethane
    [Trichloromonofluoro-
    methane]
    75-69-4
    ND
    --
    ND
    39
    2,4,5-Trichlorophenol
    95-95-4
    ND
    --
    ND
    2400
    2,4,6-Trichlorophenol
    88-06-2
    ND
    --
    ND
    2400
    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: Added at 24 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

    135
    SUBPART B: THE MANIFEST
    Section
    722.120
    General Requirements
    722.121
    Acquisition of Manifests
    722.122
    Number of Copies
    722.123
    Use of the Manifest
    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 1000 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

    136
    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
    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, 43 PCB 427, at 5 Ill. Reg. 9781, effective May 17, 1982;
    amended and codified in R81-22, 45 PCB 317, at 6 Ill. Reg. 4828, effective May 17, 1982;
    amended in R82-18, 51 PCB 31, 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. ________, effective
    ______________________; amended in R00-13 at 24 Ill. Reg. ________, effective
    ______________________.
    SUBPART C: PRE-TRANSPORT REQUIREMENTS
    Section 722.134
    Accumulation Time
    a)
    Except as provided in subsection (d), (e), or (f) of this Section, a generator is

    137
    exempt from all the requirements in 35 Ill. Adm. Code 725.Subparts G and H,
    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:
    A)
    In containers, and the generator complies with 35 Ill. Adm. Code
    725.Subparts I, AA, BB, and CC;
    B)
    In tanks, and the generator complies with 35 Ill. Adm. Code
    725.Subparts J, AA, BB, and CC, except 35 Ill. Adm. Code
    725.297(c) and 725.300;
    C)
    On drip pads, and the generator complies with 35 Ill. Adm. Code
    725.Subpart W 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 35 Ill.
    Adm. Code 725.Subpart DD (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 shall 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 respecting 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 “in addition” hanging subsection that appears in

    138
    the Federal rules after 40 CFR 262.34(a)(1)(iv)(B) is 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
    marked clearly with the words “Hazardous Waste”; and
    4)
    The generator complies with the requirements for treatment, storage, and
    disposal facility owners or operators in 35 Ill. Adm. Code 725.Subparts
    C and D and with 35 Ill. Adm. Code 725.116 and 728.107(a)(4)
    728.107(a)(5).
    b)
    A generator that accumulates hazardous waste for more than 90 days 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 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 Section 37 of the Environmental Protection Act 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)
    Complies with 35 Ill. Adm. Code 725.271, 725.272, and
    725.273(a); and
    B)
    Marks the generator’s 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

    139
    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 1000
    kilograms of hazardous waste in a calendar month may accumulate hazardous
    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 6000 kilograms;
    2)
    The generator complies with the requirements of 35 Ill. Adm. Code
    725.Subpart I (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, 35 Ill. Adm. Code 725.Subpart C, 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 shall 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 shall ensure that all employees are thoroughly

    140
    familiar with proper waste handling and emergency procedures,
    relevant to their responsibilities during normal facility operations
    and emergencies.
    D)
    The emergency coordinator or designee shall respond to any
    emergencies that arise. The applicable responses are as follows:
    i)
    In the event of a fire, call the fire department or attempt to
    extinguish it using a fire extinguisher;
    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 shall immediately notify the National
    Response Center (using its 24-hour toll free number 800-
    424-8802). The report must include the following
    information: the name, address, and USEPA identification
    number (Section 722.112 of this Part) of the generator; the
    date, time, and type of incident (e.g., spill or fire); the
    quantity and type of hazardous waste involved in the
    incident; the extent of injuries, if any; and the estimated
    quantity and disposition of recoverable materials, if any.
    e)
    A generator that generates greater than 100 kilograms but less than 1000
    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 1000
    kilograms of hazardous waste in a calendar month and that accumulates
    hazardous waste in quantities exceeding 6000 kg or accumulates hazardous waste
    for more than 180 days (or for more than 270 days if the generator must
    transport 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-

    141
    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 Section 37 of the Environmental Protection Act.
    (Source: Amended at 24 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
    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
    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

    142
    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
    724.212
    Closure Plan; Amendment of Plan
    724.213
    Closure; Time Allowed For Closure
    724.214
    Disposal or Decontamination of Equipment, Structures and Soils

    143
    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’s 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
    Systems
    724.297
    Closure and Post-Closure Care

    144
    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
    724.383
    Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026 and

    145
    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: CORRECTIVE ACTION FOR SOLID WASTE
    MANAGEMENT UNITS
    Section
    724.652
    Corrective Action Management Units
    724.653
    Temporary Units
    724.654
    Staging Piles
    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
    724.673
    Design and operating requirements
    724.674
    Inspections

    146
    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
    724.983
    Waste Determination Procedures

    147
    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
    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, 53 PCB 131, 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

    148
    November 22, 1993; amended in R93-16 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. ________, effective ______________________; amended in
    R00-13 at 24 Ill. Reg. ________, effective ______________________.
    SUBPART A: GENERAL PROVISIONS
    Section 724.101
    Purpose, Scope, and Applicability
    a)
    The purpose of this Part is to establish minimum standards that define the
    acceptable management of hazardous waste.
    b)
    The standards in this Part apply to owners and operators of all facilities that treat,
    store, or dispose of hazardous waste, except as specifically provided otherwise in
    this Part or 35 Ill. Adm. Code 721.
    c)
    The requirements of this Part apply to a person disposing of hazardous waste by
    means of ocean disposal subject to a permit issued under the Marine Protection,
    Research and Sanctuaries Act (16 U.S.C. USC 1431-1434, 33 USC 1401) only
    to the extent they are included in a RCRA permit by rule granted to such a
    person under 35 Ill. Adm. Code 703.141. A “RCRA permit” is a permit
    required by Section 21(f) of the Environmental Protection Act and 35 Ill. Adm.
    Code 703.121.
    BOARD NOTE: This Part does apply to the treatment or storage of hazardous
    waste before it is loaded onto an ocean vessel for incineration or disposal at sea.
    d)
    The requirements of this Part apply to a person disposing of hazardous waste by
    means of underground injection subject to a permit issued by the Agency
    pursuant to Section 12(g) of the Environmental Protection Act only to the extent
    they are required by 35 Ill. Adm. Code 704.Subpart F.
    BOARD NOTE: This Part does apply to the above-ground treatment or storage
    of hazardous waste before it is injected underground.
    e)
    The requirements of this Part apply to the owner or operator of a POTW
    (publicly owned treatment works) that treats, stores, or disposes of hazardous
    waste only to the extent included in a RCRA permit by rule granted to such a

    149
    person under 35 Ill. Adm. Code 703.141.
    f)
    This subsection corresponds with 40 CFR 264.1(f), which provides that the
    federal regulations do not apply to T/S/D activities in authorized states, except
    under limited, enumerated circumstances. This statement maintains structural
    consistency with USEPA rules.
    g)
    The requirements of this Part do not apply to:
    1)
    The owner or operator of a facility permitted by the Agency under
    Section 21 of the Environmental Protection Act 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.
    BOARD NOTE: The owner or operator may be subject to 35 Ill. Adm.
    Code 807 and may have to have a supplemental permit under 35 Ill.
    Adm. Code 807.210.
    2)
    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 35 Ill. Adm.
    Code 726.Subparts C, F, G, or H or 35 Ill. Adm. Code 739).
    3)
    A generator accumulating waste on-site in compliance with 35 Ill. Adm.
    Code 722.134.
    4)
    A farmer disposing of waste pesticides from the farmer’s own use in
    compliance with 35 Ill. Adm. Code 722.170.
    5)
    The owner or operator of a totally enclosed treatment facility, as defined
    in 35 Ill. Adm. Code 720.110.
    6)
    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
    35 Ill. Adm. Code 728.Table T) or reactive (D003) waste to remove the
    characteristic before land disposal, the owner or operator must comply
    with the requirements set out in Section 724.117(b).
    7)
    This subsection corresponds with 40 CFR 264.1(g)(7), reserved by
    USEPA. This statement maintains structural consistency with USEPA
    rules.

    150
    8)
    Immediate response:
    A)
    Except as provided in subsection (g)(8)(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
    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 (g)(8)(A) of this Section
    and 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 shall 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.

    151
    9)
    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.
    10)
    The addition of absorbent materials to waste in a container (as defined in
    35 Ill. Adm. Code 720) or the addition of waste to absorbent material in
    a container, provided these actions occur at the time waste is first placed
    in the container, and Sections 724.117(b), 724.271, and 724.272 are
    complied with.
    11)
    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; and
    D)
    Mercury-containing lampsLamps, as described in 35 Ill. Adm.
    Code 733.107 733.105.
    BOARD NOTE: Subsection (g)(11)(D) of this Section was added
    pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see
    P.A. 90-502, effective August 19, 1997).
    h)
    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.
    i)
    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.
    j)
    The requirements of Subparts B, C, and D of this Part and Section 724.201 do
    not apply to remediation waste management sites. (However, some remediation
    waste management sites may be a part of a facility that is subject to a traditional
    RCRA permit because the facility is also treating, storing, or disposing of
    hazardous wastes that are not remediation wastes. In these cases, Subparts B, C,
    and D of this Part, and Section 724.201 do apply to the facility subject to the
    traditional RCRA permit.) Instead of the requirements of Subparts B, C, and D
    of this Part, owners or operators of remediation waste management sites shall

    152
    comply with the following requirements:
    1)
    The owner or operator shall obtain an EPA identification number by
    applying to USEPA using USEPA Form 8700-12;
    2)
    The owner or operator shall obtain a detailed chemical and physical
    analysis of a representative sample of the hazardous remediation wastes to
    be managed at the site. At a minimum, the analysis must contain all of
    the information that must be known to treat, store, or dispose of the waste
    according to this Part and 35 Ill. Adm. Code 728, and the owner or
    operator shall keep the analysis accurate and up to date;
    3)
    The owner or operator shall prevent people who are unaware of the
    danger from entering the site, and the owner or operator shall minimize
    the possibility for unauthorized people or livestock entering onto the
    active portion of the remediation waste management site, unless the
    owner or operator can demonstrate the following to the Agency:
    A)
    Physical contact with the waste, structures, or equipment within
    the active portion of the remediation waste management site will
    not injure people or livestock who that may enter the active
    portion of the remediation waste management site; and
    B)
    Disturbance of the waste or equipment by people or livestock who
    that enter onto the active portion of the remediation waste
    management site will not cause a violation of the requirements of
    this Part;
    4)
    The owner or operator shall inspect the remediation waste management
    site for malfunctions, deterioration, operator errors, and discharges that
    may be causing or may lead to a release of hazardous waste constituents
    to the environment or a threat to human health. The owner or operator
    shall conduct these inspections often enough to identify problems in time
    to correct them before they harm human health or the environment, and
    the owner or operator shall remedy the problem before it leads to a
    human health or environmental hazard. Where a hazard is imminent or
    has already occurred, the owner or operator shall immediately take
    remedial action;
    5)
    The owner or operator shall provide personnel with classroom or on-the-
    job training on how to perform their duties in a way that ensures the
    remediation waste management site complies with the requirements of this
    Part, and on how to respond effectively to emergencies;
    6)
    The owner or operator shall take precautions to prevent accidental

    153
    ignition or reaction of ignitable or reactive waste, and the owner or
    operator shall prevent threats to human health and the environment from
    ignitable, reactive, and incompatible waste;
    7)
    For remediation waste management sites subject to regulation under
    Subparts I through O and Subpart X of this Part, the owner or operator
    shall design, construct, operate, and maintain a unit within a 100-year
    floodplain to prevent washout of any hazardous waste by a 100-year
    flood, unless the owner or operator can meet the requirements of Section
    724.118(b);
    8)
    The owner or operator shall not place any non-containerized or bulk
    liquid hazardous waste in any salt dome formation, salt bed formation,
    underground mine, or cave;
    9)
    The owner or operator shall develop and maintain a construction quality
    assurance program for all surface impoundments, waste piles, and landfill
    units that are required to comply with Sections 724.321(c) and (d),
    724.351(c) and (d), and 724.401(c) and (d) at the remediation waste
    management site, according to the requirements of Section 724.119;
    10)
    The owner or operator shall develop and maintain procedures to prevent
    accidents and a contingency and emergency plan to control accidents that
    occur. These procedures must address proper design, construction,
    maintenance, and operation of remediation waste management units at the
    site. The goal of the plan must be to minimize the possibility of, and the
    hazards from, a fire, explosion, or any unplanned sudden or non-sudden
    release of hazardous waste or hazardous waste constituents to air, soil, or
    surface water that could threaten human health or the environment. The
    plan must explain specifically how to treat, store, and dispose of the
    hazardous remediation waste in question, and must be implemented
    immediately whenever a fire, explosion, or release of hazardous waste or
    hazardous waste constituents occurs that could threaten human health or
    the environment;
    11)
    The owner or operator shall designate at least one employee, either on
    the facility premises or on call (that is, available to respond to an
    emergency by reaching the facility quickly), to coordinate all emergency
    response measures. This emergency coordinator must be thoroughly
    familiar with all aspects of the facility’s contingency plan, all operations
    and activities at the facility, the location and characteristics of waste
    handled, the location of all records within the facility, and the facility
    layout. In addition, this person must have the authority to commit the
    resources needed to carry out the contingency plan;

    154
    12)
    The owner or operator shall develop, maintain, and implement a plan to
    meet the requirements in subsections (j)(2) through (j)(6) and (j)(9)
    through (j)(10) of this Section; and
    13)
    The owner or operator shall maintain records documenting compliance
    with subsections (j)(1) through (j)(12) of this Section.
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    SUBPART O: INCINERATORS
    Section 724.440
    Applicability
    a)
    The regulations in this Subpart apply to owners and operators of facilities that
    incinerate hazardous waste, except as Section 724.101 provides otherwise. The
    following facility owners and operators are considered to incinerate hazardous
    waste:
    1)
    Owners or operators of hazardous waste incinerators (as defined in 35 Ill.
    Adm. Code 720.110); and
    2)
    Owners or operators who that burn hazardous waste in boilers or in
    industrial furnaces in order to destroy the wastes.
    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 owner or operator demonstrates
    compliance with the maximum achievable control technology (MACT)
    requirements of 40 CFR 63, Subpart EEE, incorporated by reference in
    35 Ill. Adm. Code 720.111, by conducting a comprehensive performance
    test and submitting to the Agency a Notification of Compliance, under 40
    CFR 63.1207(j) and 63.1210(d), documenting compliance with the
    requirements 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 40 CFR 63, Subpart EEE 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.
    BOARD NOTE: Sections 9.1 and 39.5 of the Environmental Protection Act

    155
    [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.
    bc)
    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 except Section 724.441 (Waste
    analysis) and Section 724.451 (Closure):
    1)
    If the Agency finds that the waste to be burned is:
    A)
    Listed as a hazardous waste in 35 Ill. Adm. Code 721.Subpart D
    solely because it is ignitable (Hazard Code I), corrosive (Hazard
    Code C), or both; or
    B)
    Listed as a hazardous waste in 35 Ill. Adm. Code 721.Subpart D
    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; or
    C)
    A hazardous waste solely because it possesses the characteristic of
    ignitability, as determined by the test for characteristics of
    hazardous wastes under 35 Ill. Adm. Code 721.Subpart C; or
    D)
    A hazardous waste solely because it possesses any of the reactivity
    characteristics described by 35 Ill. Adm. Code 721.123(a)(1), (2),
    (3), (6), (7) and (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 35 Ill. Adm. Code 721.Appendix H, which that
    would reasonably be expected to be in the waste.
    cd)
    If the waste to be burned is one which that is described by paragraphs (b)(1)(A),
    (b)(1)(B), (b)(1)(C) or (b)(1)(D) and contains insignificant concentrations of the
    hazardous constituents listed in 35 Ill. Adm. Code 721.Appendix H, then the
    Agency may, in establishing permit conditions, exempt the applicant from all
    requirements of this Subpart, 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.
    de)
    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

    156
    incinerator permits).
    (Source: Amended at 24 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 724.Subparts I through O and AA through CC
    of this Part; and 35 Ill. Adm. Code 702, 703, and 730; and 40 CFR 63, Subpart EEE,
    incorporated by reference in 35 Ill. Adm. Code 720.111, that are appropriate for the
    miscellaneous unit being permitted. Protection of human health and the environment includes,
    but is not limited to:
    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:
    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;

    157
    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:
    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;
    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 casued 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:
    1)
    The volume and physical and chemical characteristics of the waste in the

    158
    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 24 Ill. Reg. ________, effective ______________________)
    SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE
    IMPOUNDMENTS, AND CONTAINERS
    Section 724.983
    Waste Determination Procedures
    a)
    Waste determination procedure for average volatile organic (VO) concentration
    of a hazardous waste at the point of waste origination.
    1)
    An owner or operator shall 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 724.982(c)(1)
    from using air emission controls in accordance with standards specified in
    Section 724.984 through Section 724.987, as applicable to the waste
    management unit.
    A)
    An owner or operator shall 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 724.982(c)(1) from using air emission controls.
    Thereafter, an owner or operator shall make an initial
    determination of the average VO concentration of the waste

    159
    stream for each averaging period that a hazardous waste is
    managed in the unit.
    B)
    An owner or operator shall 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 applicable VO concentration limits specified in Section
    724.982.
    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 in accordance with the
    procedures specified in 35 Ill. Adm. Code 725.984(a)(2) through (a)(4).
    b)
    Waste determination procedures for treated hazardous waste.
    1)
    An owner or operator shall perform the applicable waste determination
    for each treated hazardous waste placed in a waste management unit
    exempted under the provisions of Section 724.982(c)(2)(A) through
    (c)(2)(F) from using air emission controls in accordance with standards
    specified in Sections 724.984 through 724.987, as applicable to the waste
    management unit.
    A)
    An owner or operator shall 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 exempt waste management unit. Thereafter, an owner or
    operator shall 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 shall 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
    724.982(c)(2) are not achieved.
    2)
    The waste determination for a treated hazardous waste must be performed
    in accordance with the procedures specified in 35 Ill. Adm. Code
    725.984(b)(2) through (b)(9), as applicable to the treated hazardous
    waste.
    c)
    Procedure to determine the maximum organic vapor pressure of a hazardous

    160
    waste in a tank.
    1)
    An owner or operator shall 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 724.984(c).
    2)
    The maximum organic vapor pressure of the hazardous waste may be
    determined in accordance with the procedures specified in 35 Ill. Adm.
    Code 725.984(c)(2) through (c)(4).
    d)
    The procedure for determining no detectable organic emissions for the purpose
    of complying with this Subpart must be conducted in accordance with the
    procedures specified in 35 Ill. Adm. Code 725.984(d).
    (Source: Amended at 24 Ill. Reg. 1146, effective January 6, 2000)
    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
    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

    161
    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
    SUBPART G: CLOSURE AND POST-CLOSURE CARE
    Section
    725.210
    Applicability
    725.211
    Closure Performance Standard

    162
    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
    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 Container
    725.273
    Management of Containers
    725.274
    Inspections
    725.276
    Special Requirements for Ignitable or Reactive Waste
    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’s Integrity
    725.292
    Design and Installation of New Tank Systems or Components
    725.293
    Containment and Detection of Releases
    725.294
    General Operating Requirements
    725.295
    Inspections
    725.296
    Response to leaks or spills and disposition of Tank Systems

    163
    725.297
    Closure and Post-Closure Care
    725.298
    Special Requirements for Ignitable or Reactive Waste
    725.299
    Special Requirements for Incompatible Wastes
    725.300
    Waste Analysis and Trial Tests
    725.301
    Generators of 100 to 1000 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 Waste
    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 Waste
    725.357
    Special Requirements for Incompatible Wastes
    725.358
    Closure and Post-closure Care
    725.359
    Response Actions
    725.360
    Monitoring and Inspection
    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
    725.380
    Closure and Post-closure
    725.381
    Special Requirements for Ignitable or Reactive Waste

    164
    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 Inspection
    725.409
    Surveying and Recordkeeping
    725.410
    Closure and Post-closure
    725.412
    Special Requirements for Ignitable or Reactive Waste
    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 Inspection
    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 Waste
    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

    165
    725.505
    Special Requirements for Ignitable or Reactive Waste
    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

    166
    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
    EPA Interim Primary Drinking Water Standards
    725.Appendix D
    Tests for Significance
    725.Appendix E
    Examples of Potentially Incompatible Waste
    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, 43 PCB 427, at 5 Ill. Reg. 9781, effective May 17, 1982;
    amended and codified in R81-22, 45 PCB 317, at 6 Ill. Reg. 4828, effective May 17, 1982;
    amended in R82-18, 51 PCB 831, at 7 Ill. Reg. 2518, effective February 22, 1983; amended in
    R82-19, 53 PCB 131, 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

    167
    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, 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. ________,
    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 that have fully complied with the
    requirements for interim status under Section 3005(e) of the Resource
    Conservation and Recovery Act (RCRA) (42 USC 6901 et seq.) and 35 Ill.
    Adm. Code 703, until either a permit is issued under Section 3005 of the
    Resource Conservation and Recovery Act or Section 21(f) of the Environmental
    Protection Act, 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 or that have failed to file Part A of the
    Permit Application, as required by 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

    168
    disposal of hazardous waste at these facilities after November 19, 1980, except
    as specifically provided otherwise in this Part or 35 Ill. Adm. Code 721.
    BOARD NOTE: As stated in Section 3005(a) of RCRA, 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 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. 35 Ill. Adm. Code
    703.140 et seq. provide that a permit is deemed issued under Section 21(f)(1) of
    the Environmental Protection Act under conditions similar to federal interim
    status.
    c)
    The requirements of this Part do not apply to:
    1)
    A person disposing of hazardous waste by means of ocean disposal
    subject to a permit issued under the Marine Protection, Research and
    Sanctuaries Act (16 USC 1431-1434; 33 USC 1401);
    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 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 35 Ill.
    Adm. Code 704.Subpart F.
    4)
    This subsection 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

    169
    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 35 Ill. Adm.
    Code 726.Subparts C, F, G, or H 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
    35 Ill. Adm. Code 728.Table T) or reactive (D003) waste in order to
    remove the characteristic before land disposal, the owner or operator
    shall comply with the requirements set out 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.

    170
    B)
    An owner or operator of a facility otherwise regulated by this Part
    shall comply with all applicable requirements of 725.Subparts C
    and D of this Part.
    C)
    Any person that is covered by subsection (c)(11)(A) of this
    Section 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 shall 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 and; and

    171
    D)
    Mercury-containing lampsLamps, as described in 35 Ill. Adm.
    Code 733.107 733.105.
    BOARD NOTE: Subsection (c)(14)(D) of this Section was added
    pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see
    P.A. 90-502, effective August 19, 1997).
    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:
    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
    725.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.

    172
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    SUBPART O: INCINERATORS
    Section 725.440
    Applicability
    a)
    The regulations in this Subpart 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 subsection (b)(2) 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 40 CFR 63, Subpart EEE, incorporated by reference in
    35 Ill. Adm. Code 720.111, by conducting a comprehensive performance
    test and submitting to the Agency a Notification of Compliance, under 40
    CFR 63.1207(j) and 63.1210(d), documenting compliance with the
    requirements of 40 CFR 63, Subpart EEE.
    2) The MACT standards of 40 CFR 63, Subpart EEE 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.
    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.
    bc)
    Owners and operators of incinerators burning hazardous waste are exempt from
    all of the requirements of this Subpart, 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 35 Ill. Adm. Code 721.Appendix H and such documentation is retained
    at the facility, if the waste to be burned is:
    1)
    Listed as a hazardous waste in 35 Ill. Adm. Code 721.Subpart D, solely
    because it is ignitable (Hazard Code I), corrosive (Hazard Code C), or
    both; or
    2)
    Listed as a hazardous waste in 35 Ill. Adm. Code 721.Subpart D, solely
    because it is reactive (Hazard Code R) for characteristics other than those
    listed in 35 Ill. Adm. Code 721.123(a)(4) and (5), and will not be burned

    173
    when other hazardous wastes are present in the combustion zone; or
    3)
    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 35 Ill. Adm. Code 721.Subpart
    C; or
    4)
    A hazardous waste solely because it possesses the reactivity
    characteristics described by 35 Ill. Adm. Code 721.123 (a)(1), (2), (3),
    (6), (7) or (8) and will not be burned when other hazardous wastes are
    present in the combustion zone.
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE
    IMPOUNDMENTS, AND CONTAINERS
    Section 725.980
    Applicability
    a)
    The requirements of this Subpart 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 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

    174
    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 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 (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, 61, or 63. 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).
    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 that has received
    a final RCRA permit prior to December 6, 1996, the following requirements
    apply:
    1)
    The requirements of 35 Ill. Adm. Code 724.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.
    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.
    d)
    The requirements of this Subpart, 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

    175
    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
    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 24 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 shall 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 shall 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 shall make an initial
    determination of the average VO concentration of the waste

    176
    stream for each averaging period that a hazardous waste is
    managed in the unit.
    B)
    An owner or operator shall 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 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 shall 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

    177
    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
    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, or in Method 25D in 40 CFR 60, appendix A,
    incorporated by reference in 35 Ill. Adm. Code 720.111.
    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, 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° C (77° F). Each of the

    178
    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, 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, 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, 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 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 adjust these data, the measured concentration of each
    individual chemical constituent contained in the waste is multiplied
    by the constituent-specific adjustment factor (f
    m25D
    ). 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 (f
    m25D
    ) can be
    obtained by contacting the USEPA, Waste and Chemical
    Processes Group, Office of Air Quality Planning and Standards,
    Research Triangle Park, NC 27711.
    i)
    Method 25D in 40 CFR 60, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111.
    ii)
    Method 624 in 40 CFR 136, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111.
    iii)
    Method 625 in 40 CFR 136, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111. 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.

    179
    v)
    Method 1625 in 40 CFR 136, appendix A, incorporated
    by reference in 35 Ill. Adm. Code 720.111.
    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. 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. 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. 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. 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.
    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

    180
    (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).
    Q
    i
    =
    Mass quantity of the hazardous waste
    stream represented by C
    i
    , in kg/hr.
    Q
    T
    =
    Total mass quantity of the hazardous waste
    during the averaging period, in kg/hr.
    C
    i
    =
    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.
    ii)
    For the purpose of determining C
    i
    , for individual waste
    samples analyzed in accordance with subsection (a)(3)(C)
    of this Section, the owner or operator shall 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

    181
    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, 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-
    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.

    182
    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 shall 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, 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. 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
    (f
    m25D
    ).
    D)
    In the event that the Agency and the owner or operator disagree
    on a determination of the average VO concentration for a
    hazardous 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. 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

    183
    Section.
    b)
    Waste determination procedures for treated hazardous waste.
    1)
    An owner or operator shall 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 shall 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 shall 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 shall 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 shall 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 shall identify and record
    the 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.

    184
    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
    720.111, or in Method 25D in 40 CFR 60, appendix A,
    incorporated by reference in 35 Ill. Adm. Code 720.111.
    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

    185
    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.
    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, incorporated by reference in 35 Ill. Adm.
    Code 720.111, 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, 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, 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 by a 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 adjust these data, the measured concentration of each

    186
    individual chemical constituent contained in the waste is multiplied
    by the constituent-specific adjustment factor (f
    m25D
    ). 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 (f
    m25D
    ) can be
    obtained by contacting the USEPA, Waste and Chemical
    Processes Group, Office of Air Quality Planning and Standards,
    Research Triangle Park, NC 27711.
    i)
    Method 25D in 40 CFR 60, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111.
    ii)
    Method 624 in 40 CFR 136, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111.
    iii)
    Method 625 in 40 CFR 136, appendix A, incorporated by
    reference in 35 Ill. Adm. Code 720.111. 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.
    v)
    Method 1625 in 40 CFR 136, appendix A, incorporated
    by reference in 35 Ill. Adm. Code 720.111.
    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. 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. 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

    187
    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. 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. 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.
    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 x C )
    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 1 year).
    Q
    i
    =
    Mass quantity of the hazardous waste stream
    represented by C
    i
    , in kg/hr.
    Q
    T
    =
    Total mass quantity of hazardous waste during the

    188
    averaging period, in kg/hr.
    C
    i
    =
    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
    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 (C
    t
    ) 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 (C
    t
    ) 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 (C
    t
    ) 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
    x C
    ) +
    n
    y = 1
    (Q
    x500ppmw)
    m
    x = 1
    Q
    +
    n
    y = 1
    Q
    Where:
    C
    t
    =
    Exit concentration limit for treated hazardous
    waste, in ppmw.

    189
    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
    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.
    Q
    x
    =
    Annual mass quantity of hazardous waste stream
    “x”, in kg/yr.
    Q
    y
    =
    Annual mass quantity of hazardous waste stream
    “y”, in kg/yr.
    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 shall 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,

    190
    using the following procedures:
    i)
    The mass quantity of each hazardous waste stream entering
    the process (Q
    b
    ) and the mass quantity of each hazardous
    waste stream exiting the process (Q
    a
    ) must be determined.
    ii)
    The average VO concentration at the point of waste
    origination of each hazardous waste stream entering the
    process (C
    b
    ) during the run must be determined in
    accordance with the requirements of subsections subsection
    (a)(3) of this Section. The average VO concentration at
    the point of waste treatment of each hazardous waste
    stream exiting the process (C
    a
    ) 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 (E
    b
    ) and
    the waste volatile organic mass flow exiting the process (E
    a
    ) 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:
    E
    a
    =
    Waste volatile organic mass flow exiting the
    process, in kg/hr.
    E
    b
    =
    Waste volatile organic mass flow entering the
    process, in kg/hr.
    m =
    Total number of runs (at least 3)
    j =
    Individual run “j”.
    Q
    bj
    =
    Mass quantity of hazardous waste entering the
    process during run “j”, in kg/hr.

    191
    Q
    aj
    =
    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.
    bj
    C
    = Average VO concentration of hazardous waste
    entering the process during run “j”, as determined
    in accordance with the requirements of subsection
    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.
    E
    b
    =
    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.
    E
    a
    =
    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 (R
    bio
    ) for a
    treated hazardous waste.
    A)
    The fraction of organics biodegraded (F
    bio
    ) must be determined
    using the procedure specified in 40 CFR 63, Appendix appendix
    C, incorporated by reference in 35 Ill. Adm. Code 720.111.
    B)
    The organic biodegradation efficiency (R
    bio
    ) must be calculated by
    using the following equation:

    192
    bio
    bio
    R
    = F
    x100%
    Where:
    R
    bio
    = Organic biodegradation efficiency, in percent.
    F
    bio
    = Fraction of organic biodegraded, as determined in
    accordance with the requirements of subsection
    (b)(6)(A) of this Section.
    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.

    193
    n =
    Total number of “y” hazardous waste streams
    treated by process.
    V
    y
    =
    Average volumetric flow rate of hazardous waste
    stream “y” at the point of waste origination, in
    m
    3
    /hr.
    k
    y
    =
    Density of hazardous waste stream “y”, in kg/m
    3
    .
    C
    y
    = 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 (E
    b
    ) and
    the waste volatile organic mass flow exiting the process (E
    a
    ) 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.
    E
    b
    =
    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.
    E
    a
    =
    Waste volatile organic mass flow exiting the
    process, as determined in accordance with the

    194
    requirements of subsection (b)(5)(D) of this
    Section, in kg/hr.
    9)
    Procedure to determine the actual organic mass biodegradation rate
    (MR
    bio
    ) for a treated hazardous waste.
    A)
    The actual organic mass biodegradation rate (MR
    bio
    ) 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 organic mass flow entering the process (E
    b
    ) must be
    determined in accordance with the requirements of subsection
    (b)(5)(D) of this Section.
    C)
    The fraction of organic biodegraded (F
    bio
    ) must be determined
    using the procedure specified in 40 CFR 63, Appendix appendix
    C, incorporated by reference in 35 Ill. Adm. Code 720.111.
    D)
    The actual organic mass biodegradation rate (MR
    bio
    ) 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
    x F
    Where:
    MR
    bio
    = Actual organic mass biodegradation rate, in
    kg/hr.
    E
    b
    =
    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.
    F
    bio
    = 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 shall 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).

    195
    2)
    An owner or operator shall 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.
    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, or in Method 25D in 40 CFR 60, appendix A,
    incorporated by reference in 35 Ill. Adm. Code 720.111.
    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 in 40 CFR 60, Appendix appendix A,
    incorporated by reference in 35 Ill. Adm. Code 720.111;
    ii)
    Methods described in American Petroleum Institute
    Publication 2517, incorporated by reference in 35 Ill.
    Adm. Code 720.111;
    iii)
    Methods obtained from standard reference texts;
    iv)
    ASTM Method D 2879-92, incorporated by reference in
    35 Ill. Adm. Code 720.111; or
    v)
    Any other method approved by the Agency.

    196
    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
    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)
    Procedure The procedure for determining no detectable organic emissions for the
    purpose of complying with this Subpart is as follows:
    1)
    The test must be conducted in accordance with the procedures specified
    in Method 21 of 40 CFR 60, appendix A, incorporated by reference in
    35 Ill. Adm. Code 720.111. 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, 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.
    5)
    Calibration gases must be as follows:

    197
    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.
    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.
    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. 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 24 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.

    198
    b)
    General requirements.
    1)
    The owner or operator shall 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 shall 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 shall 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
    shall 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 shall 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

    199
    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
    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 shall 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
    shall 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 shall promptly secure the
    closure devices in the closed position and install covers, as

    200
    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 shall
    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 shall 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

    201
    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.
    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 shall 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 incorporated by reference in
    35 Ill. Adm. Code 722.Appendix A (USEPA Forms 8700-22 and
    8700-22A), as required under Section 725.171. If a defect is
    detected, the owner or operator shall repair the defect in
    accordance with the requirements of subsection (c)(4)(C) of this

    202
    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 shall 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 shall repair the defect in
    accordance with the requirements of subsection (c)(4)(C) of this
    Section.
    C)
    When a defect is detected for in the container, cover, or closure
    devices, the owner or operator shall 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 shall 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.
    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.
    C)
    A container that has been demonstrated within the preceding 12
    months to be vapor-tight by using 40 CFR 60, appendix A,
    Method 27, incorporated by reference in 35 Ill. Adm. Code
    720.111, in accordance with the procedure specified in subsection
    (h) of this Section.

    203
    2)
    Transfer of hazardous waste in 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 shall 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
    shall 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 shall 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

    204
    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 shall
    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 shall 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

    205
    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 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
    shall 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 shall 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 incorporated by reference in
    35 Ill. Adm. Code 722.Appendix A (USEPA Forms 8700-22 and
    8700-22A), as required under Section 725.171. If a defect is
    detected, the owner or operator shall 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 shall 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 shall repair the defect in

    206
    accordance with the requirements of subsection (d)(4)(C) of this
    Section.
    C)
    When a defect is detected for in the container, cover, or closure
    devices, the owner or operator shall 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 which 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 shall 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 40 CFR
    52.741, appendix B, incorporated by reference in 35 Ill. Adm.
    Code 720.111. 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 shall 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

    207
    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 shall 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 shall 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:
    1)
    The container meets the applicable requirements specified in 49 CFR 178,
    “Specifications for Packaging”, or 49 CFR 179, “Specifications for Tank
    Cars”, both incorporated by reference in 35 Ill. Adm. Code 720.111.
    2)
    Hazardous waste is managed in the container in accordance with the
    applicable requirements specified in 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,

    208
    “Continuing Qualification and Maintenance of Packagings”, each
    incorporated by reference in 35 Ill. Adm. Code 720.111.
    3)
    For the purpose of complying with this Subpart, 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 requirements of 49
    CFR 178 for the purpose of complying with this Subpart, an owner or
    operator may comply with the exceptions for combination packagings
    specified in 49 CFR 173.12(b), incorporated by reference in 35 Ill. Adm.
    Code 720.111.
    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:
    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 (0.10 inch) 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

    209
    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 24 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 (Repealed)
    Section
    726.140
    Applicability (Repealed)
    726.141
    Prohibitions (Repealed)
    726.142
    Standards applicable to generators of used oil burned for energy recovery

    210
    (Repealed)
    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
    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

    211
    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
    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].
    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. ________, effective
    ______________________.
    SUBPART H: HAZARDOUS WASTE BURNED IN BOILERS AND
    INDUSTRIAL FURNACES
    Section 726.200
    Applicability
    a)
    The regulations of this Subpart 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), and (f) of this Section. In this Subpart, 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,

    212
    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 40 CFR 63, Subpart EEE, incorporated by reference in
    35 Ill. Adm. Code 720.111, by conducting a comprehensive performance
    test and submitting to the Agency a Notification of Compliance, under 40
    CFR 63.1207(j) and 63.1210(d), documenting compliance with the
    requirements 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:
    A) The closure requirements of Sections 726.202(e)(11) and
    7266.203(l);
    B) The standards for direct transfer of Section 726.211;
    C) The standards for regulation of residues of Section 726.312; and
    D) The applicable requirements of Subparts A through H, BB and
    CC of 35 Ill. Adm. Code 724 and 725.
    bc)
    The following hazardous wastes and facilities are not subject to regulation under
    this Subpart:
    1)
    Used oil burned for energy recovery that is also a hazardous waste solely
    because it exhibits a characteristic of hazardous waste identified in 35 Ill.
    Adm. Code 721.Subpart C. 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
    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

    213
    4)
    Coke ovens, if the only hazardous waste burned is USEPA hazardous
    waste no. K087 decanter tank tar sludge from coking operations.
    cd)
    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,
    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 shall
    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, shall comply with the requirements of
    subsection (c)(3) (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 40 CFR 63, Subpart X shall 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 (c)(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;
    B)
    Sample and analyze the hazardous waste and other feedstocks as
    necessary to comply with the requirements of this subsection
    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

    214
    determination, the owner or operator shall use the best available
    method; and
    C)
    Maintain at the facility for at least three years records to document
    compliance with the provisions of this subsection 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 35 Ill. Adm. Code 721.Appendix H
    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 (c)(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 (c)(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 40 CFR
    63, Subpart X, or a metal recovery furnace that burns baghouse bags
    used to capture metallic dusts emitted by steel manufacturing shall 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 waste under this subsection or subsection (c)(1) of this
    Section. The owner or operator shall comply with the requirements of
    subsection (c)(1) of this Section for those wastes claimed to be exempt
    under that subsection and with the following requirements for those
    wastes claimed to be exempt under this subsection:

    215
    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 (c)(1) of this Section, provided that:
    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 35 Ill. Adm. Code 261.Appendix H 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
    toxicity characteristic of 35 Ill. Adm. Code 721.124 for an
    organic constituent;
    iii)
    The waste is not a hazardous waste listed in 35 Ill. Adm.
    Code 721.Subpart D because it is listed for an organic
    constituent, as identified in 35 Ill. Adm. Code
    721.Appendix G; and
    iv)
    The owner or operator certifies in the one-time notice that
    hazardous waste is burned under the provisions of
    subsection (c)(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 (c)(1)(B) of this Section,
    and records to document compliance with subsection (c)(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 35 Ill.
    Adm. Code 721.Appendix H may pose a hazard to human health
    and the environment when burned in a metal recovery furnace
    exempt from the requirements of this Subpart. Under these
    circumstances, after adequate notice and opportunity for comment,
    the metal recovery furnace will become subject to the
    requirements of this Subpart when burning that material. In

    216
    making the hazard determination, the Agency shall 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.
    de)
    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.
    ef)
    The management standards for residues under Section 726.212 apply to any BIF
    burning hazardous waste.
    fg)
    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, except for Section
    726.212. To be exempt from Sections 726.202 through 726.211, an owner or
    operator shall:
    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
    precious metal, using procedures specified by Test Methods for
    Evaluating Solid Waste, Physical/Chemical Methods, SW-846,

    217
    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 shall 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 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 shall 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 35 Ill. Adm.
    Code 721.Appendix H 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.
    gi)
    Abbreviations and definitions. The following definitions and abbreviations are
    used in this Subpart:
    “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”.

    218
    “Feed rates” are measured as specified in Section 726.202(e)(6).
    “Good engineering practice stack height” is as defined by 40 CFR
    51.100(ii), incorporated by reference in 35 Ill. Adm. Code 720.111.
    “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 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.

    219
    “RSD” means risk-specific dose, the acceptable ambient level for the
    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 or D 2161-87, incorporated by reference in 35 Ill.
    Adm. Code 720.111.
    “TCLP test” means the toxicity characteristic leaching procedure 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 “Procedures for Estimating the Toxicity Equivalence of Chlorinated
    Dibenzo-p-Dioxin and Dibenzofuran Congeners” incorporated by
    reference in Appendix I of this Part.
    “mg” means microgram.
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 726.201
    Management prior to Burning
    a)
    Generators. Generators of hazardous waste that is burned in a BIF are subject to
    35 Ill. Adm. Code 722.
    b)
    Transporters. Transporters of hazardous waste that is burned in a BIF are
    subject to 35 Ill. Adm. Code 723.
    c)
    Storage and treatment facilities.
    1)
    Owners and operators of facilities An owner or operator of a facility that
    store stores or treats hazardous waste that is burned in a BIF are is
    subject to the applicable provisions of 35 Ill. Adm. Code 724.Subparts A
    through L, 35 Ill. Adm. Code 725.Subparts A through L 724 and 725
    and 35 Ill. Adm. Code 702 and 703, except as provided by subsection
    (c)(2), below of this Section. These standards apply to storage and

    220
    treatment by the burner as well as to any storage or treatment facilities
    facility operated by intermediaries an intermediary (processors, blenders,
    distributorsa processor, blender, distributor, etc.) between the generator
    and the burner.
    2)
    Owners and operators of facilities An owner or operator of a facility that
    burn burns, in an on-site BIF exempt from regulation under the small
    quantity burner provisions of Section 726.208, hazardous waste that they
    generate are it generates is exempt from regulation under 35 Ill. Adm.
    Code 724.Subparts A through L, 35 Ill. Adm. Code 725.Subparts A
    through L 724 and 725 and 35 Ill. Adm. Code 702 and 703 applicable to
    storage units for those storage units that store mixtures of hazardous
    waste and the primary fuel to the BIF in tanks that feed the fuel mixture
    directly to the burner. Storage of hazardous waste prior to mixing with
    the primary fuel is subject to regulation as prescribed in subsection (c)(1),
    above of this Section.
    (Source: Amended at 24 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 cu m (0.08 grains/dry standard cubic foot) after correction to a stack
    gas concentration of 7% oxygen, using procedures prescribed in 40 CFR 60,
    Appendix A, methods 1 through 5, (incorporated by reference in 35 Ill. Adm.
    Code 720.111), and incorporated by reference in Appendix I (“eye”) of this
    Part.
    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 formula:
    (
    )
    P
    P
    14
    E - Y
    c
    m
    =
    ×
    Where:
    P
    c
    is the corrected concentration of the pollutant in the stack
    gas,
    P
    m
    is the measured concentration of the pollutant in the stack
    gas,

    221
    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 must be
    based on correcting to seven percent oxygen using this procedure.
    cd)
    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 24 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% 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% by weight normal,
    nonhazardous raw materials;
    3)
    Cement kilns. Cement kilns must process at least 50% by weight 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:

    222
    1)
    Comparison of waste-derived residue with normal residue. The waste-
    derived residue must not contain 35 Ill. Adm. Code 721.Appendix H
    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 35 Ill. Adm. Code 721.Appendix H that may
    be PICs. Sampling and analyses must be in conformance with
    procedures prescribed in “Test Methods for Evaluating Solid Waste,
    Physical/Chemical Methods”, U.S. EPA USEPA Publication SW-846,
    incorporated by reference in 35 Ill. Adm. Code 720.111(a). For
    polychlorinated dibenzo-p-dioxins and polychlorinated dibenzo-furans
    (D/F), 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% confidence with a
    95% proportion of the sample distribution) of the concentration in
    the normal residue shall 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 shall use statistical
    procedures prescribed in “Statistical Methodology for Bevill
    Residue Determinations” incorporated by reference in Section
    726.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)

    223
    above 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 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) above of this
    Section) in the waste-derived residue must not exceed the health-
    based level specified in Section 726.Appendix G of this Part, or
    the level of detection (using analytical procedures prescribed in
    “Test Methods for Evaluating Solid Waste, Physical/Chemical
    Methods”, U.S. EPA 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
    Section 726.Appendix G of this Part, then a limit of 0.002 mg/kg
    or the level of detection (using analytical procedures prescribed in
    “Test Methods for Evaluating Solid Waste, Physical/Chemical
    Methods”, U.S. EPA USEPA Publication SW-846, incorporated
    by reference in 35 Ill. Adm. Code 720.111), whichever is higher,
    must be used. The levels specified in Section 726.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 Section
    726.Appendix G of this Part) are administratively stayed under the
    condition, for those constituents specified in subsection (b)(1)
    above 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 728.Table B 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 U.S. EPA USEPA guidance and standards, the owner
    or operator is deemed to be in compliance for that constituent.
    Until U.S. EPA USEPA develops new guidance or standards, the
    owner or operator may demonstrate such good-faith efforts by

    224
    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 728.Table B for F039
    nonwastewaters 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
    pentachlorodibenzofurans, total tetrachlorodibenzo-p-dioxins, and
    total tetrachlorodibenzofurans;. The stay will remain in effect
    until further rulemaking action is taken; and
    BOARD NOTE: In a note to corresponding 40 CFR
    266.112(b)(2)(i) (1999), as amended at 64 Fed. Reg. 53076 (Sept.
    30, 1999), 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 Section 726.Appendix G; and
    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

    225
    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 35 Ill. Adm. Code 721.Appendix H that are
    present in waste-derived residues;
    2)
    If the waste-derived residue is compared with normal residue under
    subsection (b)(1) above of this Section:
    A)
    The levels of constituents in 35 Ill. Adm. Code 721.Appendix H
    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 24 Ill. Reg. ________, effective ______________________)
    Section 726.Appendix H
    Potential PICs for Determination of Exclusion of Waste-Derived
    Residues
    PICs Found in Stack Effluents
    Volatiles
    Semivolatiles
    Benzene
    Bis(2-ethylhexyl)phthalate
    Toluene
    Naphthalene
    Carbon tetrachloride
    Phenol
    Chloroform
    Diethyl phthalate
    Methylene chloride
    Butyl benzyl phthalate
    Trichloroethylene
    2,4-Dimethylphenol
    Tetrachloroethylene
    o-Dichlorobenzene
    1,1,1-Trichloroethane
    m-Dichlorobenzene
    Chlorobenzene
    p-Dichlorobenzene
    cis-1,4-Dichloro-2-butene
    Hexachlorobenzene
    Bromochloromethane
    2,4,6-Trichlorophenol

    226
    Bromodichloromethane
    Fluoranthene
    Bromoform
    o-Nitrophenol
    Bromomethane
    1,2,4-Trichlorobenzene
    Methylene bromide
    o-Chlorophenol
    Methyl ethyl ketone
    Pentachlorophenol
    Pyrene
    Dimethyl phthalate
    Mononitrobenzene
    Polycholorinate dibenzo-p-dioxins
    1
    Polycholorinate dibenzo-furans
    1
    1
    Analyses for polychlorinated dibenzo-p-dioxins and polychlorinated dibenzo-furans are
    required only for residues collected from areas downstream of the combustion chamber (e.g.,
    ductwork, boiler tubes, heat exchange surfaces, air pollution control devices, etc.).
    BOARD NOTE: Analysis is not required for those compounds that do not have an established
    F039 nonwastewater concentration limit.
    (Source: Amended at 24 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)

    227
    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
    728.130
    Waste Specific Prohibitions -- Wood Preserving Wastes
    728.131
    Waste Specific Prohibitions -- Dioxin-Containing Wastes
    728.132
    Waste Specific Prohibitions -- California List Wastes (Repealed)
    728.133
    Waste-Specific Prohibitions -- Organobromine Wastes
    728.134
    Waste-Specific Prohibitions -- Toxicity Characteristic Metal Wastes
    728.135
    Waste Specific Prohibitions -- Petroleum Refining Wastes
    728.136
    Waste Specific Prohibitions -- Newly Listed Wastes (Repealed)
    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 (Repealed)
    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

    228
    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
    728.Table F
    Alternative Treatment Standards for Hazardous Debris
    728.Table G
    Alternative Treatment Standards Based on HMTR
    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 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, 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.
    ________, effective ______________________.

    229
    SUBPART A: GENERAL
    Section 728.101
    Purpose, Scope, and Applicability
    a)
    This Part identifies hazardous wastes that are restricted from land disposal and
    defines those limited circumstances under which an otherwise prohibited waste
    may continue to be land disposed.
    b)
    Except as specifically provided otherwise in this Part or 35 Ill. Adm. Code 721,
    the requirements of this Part apply to persons that generate or transport
    hazardous waste and to owners and operators of hazardous waste treatment,
    storage, and disposal facilities.
    c)
    Restricted wastes may continue to be land disposed as follows:
    1)
    Where persons have been granted an extension to the effective date of a
    prohibition under Subpart C or pursuant to Section 728.105, with respect
    to those wastes covered by the extension;
    2)
    Where persons have 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)
    A waste that is hazardous only because it exhibits a characteristic of
    hazardous waste and that is otherwise prohibited under this Part is not
    prohibited if the waste:
    A)
    Is disposed into a nonhazardous or hazardous waste injection well,
    as defined in 35 Ill. Adm. Code 704.106(a); and
    B)
    Does not exhibit any prohibited characteristic of hazardous waste
    identified in 35 Ill. Adm. Code 721.Subpart C at the point of
    injection.
    4)
    A waste that is hazardous only because it exhibits a characteristic of
    hazardous waste and which is otherwise prohibited under this Part is not
    prohibited if the waste meets any of the following criteria, unless the
    waste is subject to a specified method of treatment other than DEACT in
    Section 728.140 or is D003 reactive cyanide:
    A)
    Any of the following is true of either treatment or management of
    the waste:
    i)
    The waste is managed in a treatment system which
    subsequently discharges to waters of the U.S. United

    230
    States pursuant to a permit issued under 35 Ill. Adm. Code
    309;
    ii)
    The waste is treated for purposes of the pretreatment
    requirements of 35 Ill. Adm. Code 307 and 310; or
    iii)
    The waste is managed in a zero discharge system engaged
    in Clean Water Act (CWA)-equivalent treatment, as
    defined in Section 728.137(a); and
    B)
    The waste no longer exhibits a prohibited characteristic of
    hazardous waste at the point of land disposal (i.e., placement in a
    surface impoundment).
    d)
    This Part does not affect the availability of a waiver under Section 121(d)(4) of
    the Comprehensive Environmental Response, Compensation, and Liability Act of
    1980 (CERCLA) (42 U.S.C. USC §§ 9601 et seq.).
    e)
    The following hazardous wastes are not subject to any provision of this Part:
    1)
    Waste generated by small quantity generators of less than 100 kg of non-
    acute hazardous waste or less than 1 kg of acute hazardous waste per
    month, as defined in 35 Ill. Adm. Code 721.105;
    2)
    Waste pesticide that a farmer disposes of pursuant to 35 Ill. Adm. Code
    722.170;
    3)
    Waste identified or listed as hazardous after November 8, 1984, for
    which USEPA has not promulgated a land disposal prohibition or
    treatment standard; or
    4)
    De minimis losses of waste that exhibits a characteristic of hazardous
    waste to wastewaters are not considered to be prohibited waste and are
    defined as losses 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);
    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; rinsate from empty containers or
    from containers that are rendered empty by that rinsing; and laboratory
    waste that does not exceed one percent of the total flow of wastewater
    into the facility’s headworks on an annual basis, or with a combined
    annualized average concentration not exceeding one part per million
    (ppm) in the headworks of the facility’s wastewater treatment or

    231
    pretreatment facility.; or
    5)
    Land disposal prohibitions for hazardous characteristic wastes do not
    apply to laboratory wastes displaying the characteristic of ignitability
    (D001), corrosivity (D002), or organic toxicity (D012 through D043) that
    are mixed with other plant wastewaters at facilities whose ultimate
    discharge is subject to regulation under the CWA (including wastewaters
    at facilities that have eliminated the discharge of wastewater), provided
    that the annualized flow of laboratory wastewater into the facility’s
    headworks does not exceed one percent or that the laboratory wastes’
    combined annualized average concentration does not exceed one part per
    million in the facility’s headworks.
    f)
    A universal waste handler or universal waste transporter (as defined in 35 Ill.
    Adm. Code 720.110) is exempt from Sections 728.107 and 728.150 for the
    hazardous wastes listed below. Such a handler or transporter is subject to
    regulation under 35 Ill. Adm. Code 733.
    1)
    Batteries, as described in 35 Ill. Adm. Code 733.102;
    2)
    Pesticides, as described in 35 Ill. Adm. Code 733.103;
    3)
    Thermostats, as described in 35 Ill. Adm. Code 733.104; and
    4)
    Mercury-containing lampsLamps, as described in 35 Ill. Adm. Code
    733.107 733.105.
    BOARD NOTE: Subsection (f)(4) of this Section was added pursuant to
    Section 22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502,
    effective August 19, 1997).
    g)
    This Part is cumulative with the land disposal restrictions of 35 Ill. Adm. Code
    729. The Environmental Protection Agency (Agency) shall not issue a
    wastestream authorization pursuant to 35 Ill. Adm. Code 709 or Section 22.6 or
    39(h) of the Environmental Protection Act [415 ILCS 5/22.6 or 39(h)] unless the
    waste meets the requirements of this Part as well as 35 Ill. Adm. Code 729.
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    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.

    232
    “Agency” means the Illinois Environmental Protection Agency.
    “Board” means the Illinois Pollution Control Board.
    “CERCLA” means the Comprehensive Environmental Response, Compensation,
    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 35 Ill.
    Adm. Code 721.Appendix H.
    “Hazardous debris” means debris that contains a hazardous waste listed in 35 Ill.
    Adm. Code 721.Subpart D or that exhibits a characteristic of hazardous waste
    identified in 35 Ill. Adm. Code 721.Subpart C. 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

    233
    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 40 CFR 761.3, incorporated by reference in 35 Ill.
    Adm. Code 720.111.
    “ppm” means parts per million.
    “RCRA corrective action” means corrective action taken under 35 Ill. Adm.
    Code 724.200 or 725.193, 40 CFR 264.100 or 265.93 (1996), or similar
    regulations in other States states with RCRA programs authorized by USEPA
    pursuant to 40 CFR 271 (1996).
    “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 U.S. 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 1 percent by weight total organic
    carbon (TOC) and less than 1 percent by weight total suspended solids (TSS).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)

    234
    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 shall 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
    Characteristic Leaching Procedure), incorporated by reference in 35 Ill.
    Adm. Code 720.111, 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 shall 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 shall 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 shall 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)

    235
    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:
    A)
    With the initial shipment of waste to each treatment, storage, or
    disposal facility, the generator shall 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 35 Ill. Adm. Code 728.Subpart D. 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 shall 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

    236
    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 shall
    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 shall 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
    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 shall 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, and all waste analysis data must be retained on-site
    in the generator’s files.

    237
    7)
    If a generator determines that it is managing a prohibited waste which 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 shall 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.
    8)
    A generator shall 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 shall fulfill the following conditions:
    A)
    With the initial shipment of waste to a treatment facility, the
    generator shall 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 35 Ill. Adm. Code 728.Appendix D and that this lab
    pack will be sent to a combustion facility in compliance
    with the alternative treatment standards for lab packs at 35

    238
    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 shall also comply with the requirements in
    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) shall 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 shall
    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 shall 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 shall
    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, 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 shall 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

    239
    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 requirements indicated in the
    following table:
    Treatment Facility Paperwork Requirements Table
    Required information
    Section
    728.107(b)
    1. USEPA hazardous waste number and
    manifest number of first shipment.
    ü
    2. The waste is subject to the LDRs. The
    constituents of 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.
    ü
    3. The notice must include the applicable
    wastewater/ nonwastewater category (see
    Section Section 728.102(d) and (f)) and sub-
    divisions made within a waste code based on
    waste-specific criteria (such as D003 reactive
    cyanide).
    ü
    4. Waste analysis data (when available).
    ü
    5. 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).
    ü
    6. A certification is needed (see applicable
    section for exact wording).
    ü

    240
    4)
    The owner or operator of a treatment facility shall 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:
    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 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

    241
    must be signed by an authorized representative and must state the
    following:
    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 35 Ill.
    Adm. Code 728.Table C. 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
    and which contain underlying hazardous constituents as defined in
    35 Ill. Adm. Code 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 the following:
    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 the following:
    I certify under penalty of law that the waste has been
    treated in accordance with the requirements of 35 Ill.

    242
    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 universal treatment standards. 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 sending 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
    facility shall 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 shall 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:
    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), 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.

    243
    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 shall
    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:
    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 shall 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

    244
    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 the following:
    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 generators and
    treaters that first determine that a contaminated soil subject to LDRs, as provided
    in Section 728.149(a), no longer exhibits a characteristic of hazardous waste
    shall 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 24 Ill. Reg. ________, effective ______________________)
    Section 728.109
    Special Rules for Characteristic Wastes
    a)
    The initial generator of a solid waste shall determine each USEPA hazardous
    waste number (waste code) applicable to the waste in order to determine the
    applicable treatment standards under Subpart D of this Part. For purposes of this
    Part, the waste must carry the waste code for any applicable listing under 35 Ill.
    Adm. Code 721.Subpart D. In addition, the waste must carry one or more of
    the waste codes under 35 Ill. Adm. Code 721.Subpart C where the waste
    exhibits a characteristic, except in the case when the treatment standard for the
    listed waste operates in lieu of the treatment standard for the characteristic waste,
    as specified in subsection (b) of this Section. If the generator determines that its
    waste displays a characteristic of hazardous waste (and the waste is not D001

    245
    nonwastewaters treated by CMBST, RORGS, or POLYM of Section 728.Table
    C), the generator shall determine the underlying hazardous constituents (as
    defined at Section 728.102(i)) in the characteristic waste.
    b)
    Where a prohibited waste is both listed under 35 Ill. Adm. Code 721.Subpart D
    and exhibits a characteristic under 35 Ill. Adm. Code 721.Subpart C, the
    treatment standard for the waste code listed in 35 Ill. Adm. Code 721.Subpart D
    will operate in lieu of the standard for the waste code under 35 Ill. Adm. Code
    721.Subpart C, provided that the treatment standard for the listed waste includes
    a treatment standard for the constituent that causes the waste to exhibit the
    characteristic. Otherwise, the waste must meet the treatment standards for all
    applicable listed and characteristic waste codes.
    c)
    In addition to any applicable standards determined from the initial point of
    generation, no prohibited waste that exhibits a characteristic under 35 Ill. Adm.
    Code 721.Subpart C shall be land disposed unless the waste complies with the
    treatment standards under Subpart D of this Part.
    d)
    A waste that exhibits a characteristic is also subject to Section 728.107
    requirements, except that once the waste is no longer hazardous, a one-time
    notification and certification must be placed in the generator’s or treater’s files
    and sent to the Agency, except for those facilities described in subsection (f) of
    this Section. 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 (municipal solid waste landfill) facility
    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 year, but no later
    than December 31.
    1)
    The notification must include the following information:
    A)
    The name and address of the RCRA Subtitle D (municipal solid
    waste landfill) facility receiving the waste shipment; and
    B)
    A description of the waste as initially generated, including the
    applicable USEPA hazardous waste numbers, the treatability
    group(s) group(s), and the underlying hazardous constituents (as
    defined in Section 728.102(i)), unless the waste will be treated and
    monitored for all underlying hazardous constituents. If all
    underlying hazardous constituents will be treated and monitored,
    there is no requirement to list any of the underlying hazardous
    constituents on the notice.
    2)
    The certification must be signed by an authorized representative and must

    246
    state the language found in Section 728.107(b)(4). If treatment removes
    the characteristic but does not meet standards applicable to underlying
    hazardous constituents, then the certification found in Section
    728.107(b)(4)(D) applies.
    3)
    For a characteristic waste whose ultimate disposal will be into a Class I
    nonhazardous waste injection well, and for which compliance with the
    treatment standards set forth in Sections 728.148 and 728.Table U for
    underlying hazardous constituents is achieved through pollution
    prevention that meets the criteria set forth at 35 Ill. Adm. Code
    738.101(d), the following information must also be included:
    A)
    A description of the pollution prevention mechanism and when it
    was implemented, if already complete;
    B)
    The mass of each underlying hazardous constituent before
    pollution prevention;
    C)
    The mass of each underlying hazardous constituent that must be
    removed, adjusted to reflect variations in mass due to normal
    operating conditions; and
    D)
    The mass reduction of each underlying hazardous constituent that
    is achieved.
    e)
    For a decharacterized waste managed on-site in a wastewater treatment system
    subject to the federal Clean Water Act (CWA) or zero-dischargers engaged in
    CWA-equivalent treatment, compliance with the treatment standards set forth in
    Sections 728.148 and 728.Table D must be monitored quarterly, unless the
    treatment is aggressive biological treatment, in which case compliance must be
    monitored annually. Monitoring results must be kept in on-site files for 5 years.
    f)
    For a decharacterized waste managed on-site in a wastewater treatment system
    subject to the federal Clean Water Act (CWA) for which all underlying
    hazardous constituents (as defined in Section 728.102) are addressed by a CWA
    permit, this compliance must be documented and this documentation must be kept
    in on-site files.
    g)
    For a characteristic waste whose ultimate disposal will be into a Class I
    nonhazardous waste injection well that qualifies for the de minimis exclusion
    described in Section 728.101, information supporting that qualification must be
    kept in on-site files.
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)

    247
    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 SW-846, incorporated by reference in Section 35 Ill. Adm.
    Code 720.111, 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 1310, the Extraction Procedure Toxicity Test, found in “Test
    Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA
    Publication SW-846, incorporated by reference in Section 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,

    248
    treatment and disposal facilities may demonstrate (and certify pursuant to 35 Ill.
    Adm. Code 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 35 Ill. Adm. Code 724.Subpart O, 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 SW-846, incorporated by reference in Section 35 Ill. Adm. Code
    720.111. 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 corresponds with 40 CFR 268.40(g), added at 61 Fed. Reg.
    43927 (Aug. 26, 1996), which has expired. This statement maintains structural
    consistency with the federal rules.

    249
    h)
    Prohibited USEPA hazardous waste numbers D004 through D011, mixed
    radioactive wastes, and mixed radioactive listed wastes containing metal
    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)
    Zinc micronutrient fertilizers that are produced for the use of the general public
    and which are produced from or contain recycled characteristic hazardous wastes
    (D004 through D011) are subject to the applicable treatment standards set forth
    in 40 CFR 268.41 (1990) (1999), incorporated by reference in 35 Ill. Adm.
    Code 720.111(b).
    BOARD NOTE: USEPA added 40 CFR 268.40(i) at 63 Fed. Reg. 46331
    (Aug. 31, 1998) to stay the Phase IV land disposal restrictions (LDRs) as they
    apply to zinc-containing fertilizers while it develops a more comprehensive set of
    regulations applicable to use of hazardous waste in making fertilizers. To effect
    the stay, USEPA applied the 1990 LDR standards to the affected materials.
    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,; 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.
    BOARD NOTE: USEPA added a second 40 CFR 268.40(i) at 63 Fed. Reg.
    46415 (Sep. 4, 1998) to indefinitely extend the alternative treatment standards for
    seven carbamate wastes. The Board has incorporated this later-adopted duplicate
    subsection (i) as subsection (j).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 728.149
    Alternative LDR Treatment Standards for Contaminated Soil
    a)
    Applicability. An owner or operator shall comply with LDRs prior to placing
    soil that exhibits a characteristic of hazardous waste or which exhibited a
    characteristic of hazardous waste at the time it was generated into a land disposal
    unit. The following chart describes whether an owner or operator must comply
    with LDRs prior to placing soil contaminated by listed hazardous waste into a
    land disposal unit:

    250
    If the LDRs
    And if the LDRs
    And if
    Then the owner
    or operator
    Applied to the
    listed waste when
    it contaminated
    the soil*.
    Apply to the listed
    waste now.
    Must comply with
    LDRs.
    Did not apply to
    the listed waste
    when it contamin-
    ated the soil*.
    Apply to the listed
    waste now.
    The soil is deter-
    mined to contain
    the listed waste
    when the soil is
    first generated.
    Must comply with
    LDRs.
    Did not apply to
    the listed waste
    when it contamin-
    ated the soil*.
    Apply to the listed
    waste now.
    The soil is deter-
    mined to contain
    the listed waste
    when the soil is
    first generated.
    Needs not comply
    with LDRs.
    Did not apply to
    the listed waste
    when it contamin-
    ated the soil*.
    Do not apply to
    the listed waste
    now.
    Needs not comply
    with LDRs.
    * For dates of LDR applicability, see Appendix G of this Part. To determine the
    date any given listed hazardous waste contaminated any given volume of soil,
    use the last date any given listed hazardous waste was placed into any given
    land disposal unit or, in the case of an accidental spill, the date of the spill.
    b)
    Prior to land disposal, contaminated soil identified by subsection (a) of this
    Section as needing to comply with LDRs must be treated according to the
    applicable treatment standards specified in subsection (c) of this Section or
    according to the universal treatment standards specified in Section 728.148 and
    Table U of this Part applicable to the contaminating listed hazardous waste or the
    applicable characteristic of hazardous waste if the soil is characteristic. The
    treatment standards specified in subsection (c) of this Section and the universal
    treatment standards may be modified through a treatment variance approved in
    accordance with Section 728.144.
    c)
    Treatment standards for contaminated soils. Prior to land disposal, contaminated
    soil identified by subsection (a) of this Section as needing to comply with LDRs
    must be treated according to all the standards specified in this subsection or
    according to the universal treatment standards specified in Section 728.148 and
    Table U of this Part.
    1)
    All soils. Prior to land disposal, all constituents subject to treatment must
    be treated as follows:

    251
    A)
    For non-metals except carbon disulfide, cyclohexanone, and
    methanol, treatment must achieve 90 percent reduction in total
    constituent concentrations, except as provided by subsection
    (c)(1)(C) of this Section.
    B)
    For metals and carbon disulfide, cyclohexanone, and methanol,
    treatment must achieve 90 percent reduction in constituent
    concentrations as measured in leachate from the treated 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 (c)(1)(C) of
    this Section.
    C)
    When treatment of any constituent subject to treatment 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. The universal
    treatment standards are identified in Table U of this Part.
    2)
    Soils that exhibit the characteristic of ignitability, corrosivity or
    reactivity. In addition to the treatment required by subsection (c)(1) of
    this Section, prior to land disposal, soils that exhibit the characteristic of
    ignitability, corrosivity, or reactivity must be treated to eliminate these
    characteristics.
    3)
    Soils that contain nonanalyzable constituents. In addition to the treatment
    requirements of subsections (c)(1) and (c)(2) of this Section, prior to land
    disposal, the following treatment is required for soils that contain
    nonanalyzable constituents:
    A)
    For soil that contains only analyzable and nonanalyzable organic
    constituents, treatment of the analyzable organic constituents to the
    levels specified in subsections (c)(1) and (c)(2) of this Section; or
    B)
    For soil that contains only nonanalyzable constituents, treatment
    by the methods specified in Section 728.142 for the waste
    contained in the soil.
    d)
    Constituents subject to treatment. When applying the soil treatment standards in
    subsection (c) of this Section, constituents subject to treatment are any
    constituents listed in Table U of this Part universal treatment standards that are
    reasonably expected to be present in any given volume of contaminated soil,
    except fluoride, selenium, sulfides, vanadium and zinc, and are present at
    concentrations greater than ten times the universal treatment standard.

    252
    e)
    Management of treatment residuals. Treatment residuals from treating
    contaminated soil identified by subsection (a) of this Section as needing to comply
    with LDRs must be managed as follows:
    1)
    Soil residuals are subject to the treatment standards of this Section;
    2)
    Non-soil residuals are subject to the following requirements:
    A)
    For soils contaminated by listed hazardous waste, the RCRA
    Subtitle C standards applicable to the listed hazardous waste; and
    B)
    For soils that exhibit a characteristic of hazardous waste, if the
    non-soil residual also exhibits a characteristic of hazardous waste,
    the treatment standards applicable to the characteristic hazardous
    waste.
    (Source: Amended at 24 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/l
    3
    ; or Techno-
    logy Code
    4
    Concentration in
    mg/kg
    5
    unless
    noted as “mg/l
    TCLP”; or Tech-
    nology 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
    ;
    8
    or
    RORGS; or
    CMBST
    DEACT and meet
    Section 728.148
    standards
    8
    ;
    8
    or
    RORGS; or
    CMBST
    D001
    9
    High TOC Ignitable Characteristic Liquids Subcategory based on 35 Ill. Adm. Code

    253
    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
    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

    254
    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
    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 (TCLP) in SW-846 Method 1311.
    Arsenic
    7440-38-2
    1.4 and meet
    Section 728.148
    standards
    8
    5.0 mg/l 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 (TCLP) in SW-846 Method 1311.
    Barium
    7440-39-3
    1.2 and meet
    Section 728.148
    standards
    8
    21 mg/l 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 (TCLP) in SW-846 Method 1311.
    Cadmium
    7440-43-9
    0.69 and meet
    Section 728.148
    standards
    8
    0.11 mg/l 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
    D007
    9
    Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for chromium based
    on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
    Chromium (Total)
    7440-47-3
    2.77 and meet
    Section 728.148
    standards
    8
    0.60 mg/l TCLP
    and meet Section
    728.148 standards
    8

    255
    D008
    9
    Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for lead based on
    the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
    Lead
    7439-92-1
    0.69 and meet
    Section 728.148
    standards
    8
    0.75 mg/l 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
    D009
    9
    Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for
    mercury based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method
    1311; 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 (TCLP) in SW-846 Method
    1311; 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

    256
    D009
    9
    Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for
    mercury based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method
    1311; and contain less than 260 mg/kg total mercury. (Low Mercury Subcategory)
    Mercury
    7439-97-6
    NA
    0.20 mg/l 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 (TCLP) in SW-846 Method
    1311; 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/l TCLP
    and meet Section
    728.148 standards
    8
    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
    D010
    9
    Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for selenium based
    on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
    Selenium
    7782-49-2
    0.82
    5.7 mg/l TCLP
    and meet Section
    728.148 standards
    8

    257
    D011
    9
    Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for silver based on
    the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
    Silver
    7440-22-4
    0.43
    0.14 mg/l TCLP
    and meet Section
    728.148 standards
    8
    D012
    9
    Wastes that are TC for Endrin based on the toxicity characteristic leaching procedure (TCLP) in
    SW-846 Method 1311.
    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 based on the toxicity characteristic leaching procedure (TCLP)
    in SW-846 Method 1311.
    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
    χ
    -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
    (TCLP) in SW-846 Method 1311.
    Methoxychlor
    72-43-5
    WETOX or
    CMBST
    0.18 and meet
    Section 728.148
    standards
    8

    258
    D015
    9
    Wastes that are TC for Toxaphene based on the toxicity characteristic leaching procedure
    (TCLP) in SW-846 Method 1311.
    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 acid) based on the toxicity
    characteristic leaching procedure (TCLP) in SW-846 Method 1311.
    2,4-D (2,4-Dichlorophenoxy-
    acetic 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
    (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching procedure (TCLP)
    in SW-846 Method 1311.
    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 tetrachloride based on the toxicity characteristic leaching
    procedure (TCLP) in SW-846 Method 1311.
    Carbon tetrachloride
    56-23-5
    0.057 and meet
    Section 728.148
    standards
    8
    6.0 and meet
    Section 728.148
    standards
    8
    D020
    9
    Wastes that are TC for Chlordane based on the toxicity characteristic leaching procedure
    (TCLP) in SW-846 Method 1311.
    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

    259
    D021
    9
    Wastes that are TC for Chlorobenzene based on the toxicity characteristic leaching procedure
    (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching procedure
    (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching procedure (TCLP)
    in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching procedure (TCLP)
    in SW-846 Method 1311.
    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
    D025
    9
    Wastes that are TC for p-Cresol based on the toxicity characteristic leaching procedure (TCLP)
    in SW-846 Method 1311.
    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) based on the toxicity characteristic leaching procedure
    (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching

    260
    procedure (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching
    procedure (TCLP) in SW-846 Method 1311.
    1,2-Dichloroethane
    107-06-2
    0.21 and meet
    Section 728.148
    standards
    8
    6.0 and meet
    Section 728.148
    standards
    8
    D029
    9
    Wastes that are TC for 1,1-Dichloroethylene based on the toxicity characteristic leaching
    procedure (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching
    procedure (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching procedure
    (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching
    procedure (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching

    261
    procedure (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching procedure
    (TCLP) in SW-846 Method 1311.
    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 ethyl ketone based on the toxicity characteristic leaching
    procedure (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching procedure
    (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching
    procedure (TCLP) in SW-846 Method 1311.
    Pentachlorophenol
    87-86-5
    0.089 and meet
    Section 728.148
    standards
    8
    7.4 and meet
    Section 728.148
    standards
    8
    D038
    9
    Wastes that are TC for Pyridine based on the toxicity characteristic leaching procedure (TCLP)
    in SW-846 Method 1311.
    Pyridine
    110-86-1
    0.014 and meet
    Section 728.148
    standards
    8
    16 and meet
    Section 728.148
    standards
    8

    262
    D039
    9
    Wastes that are TC for Tetrachloroethylene based on the toxicity characteristic leaching
    procedure (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching procedure
    (TCLP) in SW-846 Method 1311.
    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 based on the toxicity characteristic leaching
    procedure (TCLP) in SW-846 Method 1311.
    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
    D042
    9
    Wastes that are TC for 2,4,6-Trichlorophenol based on the toxicity characteristic leaching
    procedure (TCLP) in SW-846 Method 1311.
    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 chloride based on the toxicity characteristic leaching procedure
    (TCLP) in SW-846 Method 1311.
    Vinyl chloride
    75-01-4
    0.27 and meet
    Section 728.148
    standards
    8
    6.0 and meet
    Section 728.148
    standards
    8

    263
    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
    tetrachloride, chlorinated fluorocarbons, chlorobenzene, o-cresol, m-cresol, p-cresol, cyclo-
    hexanone, 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, trichloromono-
    fluoromethane, 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
    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

    264
    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/l TCLP
    Cyclohexanone
    108-94-1
    0.36
    0.75 mg/l TCLP
    Methanol
    67-56-1
    5.6
    0.75 mg/l 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
    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/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l 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/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l TCLP
    Silver
    7440-22-4
    NA
    0.14 mg/l TCLP
    F007
    Spent cyanide plating bath solutions from electroplating operations.
    Cadmium
    7440-43-9
    NA
    0.11 mg/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Cyanides (Total)
    7
    57-12-5
    1.2
    590

    265
    Cyanides (Amenable)
    7
    57-12-5
    0.86
    30
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l TCLP
    Silver
    7440-22-4
    NA
    0.14 mg/l 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/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l 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/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l TCLP
    Silver
    7440-22-4
    NA
    0.14 mg/l 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/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l 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/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l TCLP
    Silver
    7440-22-4
    NA
    0.14 mg/l 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/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l 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/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l TCLP
    Silver
    7440-22-4
    NA
    0.14 mg/l TCLP
    F012
    Quenching wastewater treatment sludges from metal heat treating operations where cyanides are

    266
    used in the process.
    Cadmium
    7440-43-9
    NA
    0.11 mg/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l 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/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l TCLP
    Silver
    7440-22-4
    NA
    0.14 mg/l 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/l 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)
    NA
    0.000063
    0.001
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    NA
    0.000063
    0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    NA
    0.000035
    0.001
    Pentachlorophenol
    87-86-5
    0.089
    7.4
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    NA
    0.000063
    0.001
    TCDFs (All Tetrachloro-
    dibenzofurans)
    NA
    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

    267
    2,3,4,6-Tetrachlorophenol
    58-90-2
    0.030
    7.4
    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
    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/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l 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

    268
    Hexachlorobenzene
    118-74-1
    0.055
    10
    Hexachlorobutadiene
    87-68-3
    0.055
    5.6
    Hexachloroethane
    67-72-1
    0.055
    30
    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)
    NA
    0.000063
    0.001
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    NA
    0.000063
    0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    NA
    0.000035
    0.001
    Pentachlorophenol
    87-86-5
    0.089
    7.4
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    NA
    0.000063
    0.001
    TCDFs (All Tetrachloro-
    dibenzofurans)
    NA
    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)
    NA
    0.000063
    0.001
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    NA
    0.000063
    0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    NA
    0.000035
    0.001
    Pentachlorophenol
    87-86-5
    0.089
    7.4
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    NA
    0.000063
    0.001

    269
    TCDFs (All Tetrachloro-
    dibenzofurans)
    NA
    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
    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

    270
    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
    Arsenic
    7440-38-2
    1.4
    5.0 mg/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l 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/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l 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/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP

    271
    F037
    Petroleum refinery primary oil/water/solids separation sludge--Any sludge generated from the
    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/l TCLP
    Cyanides (Total)
    7
    57-12-5
    1.2
    590
    Lead
    7439-92-1
    0.69
    NA
    Nickel
    7440-02-0
    NA
    11 mg/l 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

    272
    been treated in aggressive biological units) and F037, K048, and K051 are not included in this
    listing.
    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
    108-88-3
    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/l TCLP
    Cyanides (Total)
    7
    57-12-5
    1.2
    590
    Lead
    7439-92-1
    0.69
    NA
    Nickel
    7440-02-0
    NA
    11 mg/l 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
    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
    χ
    -BHC
    58-89-9
    0.0017
    0.066

    273
    Benzene
    71-43-2
    0.14
    10
    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(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
    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

    274
    Cyclohexanone
    108-94-1
    0.36
    NA
    1,2-Dibromo-3-chloropropane
    96-12-8
    0.11
    15
    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
    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

    275
    Diphenylnitrosamine (difficult to
    distinguish from diphenylamine)
    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
    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)
    NA
    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
    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

    276
    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
    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)
    NA
    0.000063
    0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    NA
    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
    Phorate
    298-02-2
    0.021
    4.6
    Phthalic anhydride
    85-44-9
    0.055
    NA
    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)
    NA
    0.000063
    0.001
    TCDFs (All Tetrachloro-
    dibenzofurans)
    NA
    0.000063
    0.001
    1,1,1,2-Tetrachloroethane
    630-20-6
    0.057
    6.0

    277
    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/l TCLP
    Arsenic
    7440-38-2
    1.4
    5.0 mg/l TCLP
    Barium
    7440-39-3
    1.2
    21 mg/l TCLP
    Beryllium
    7440-41-7
    0.82
    NA
    Cadmium
    7440-43-9
    0.69
    0.11 mg/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Cyanides (Total)
    7
    57-12-5
    1.2
    590
    Cyanides (Amenable)
    7
    57-12-5
    0.86
    NA
    Fluoride
    16964-48-8
    35
    NA
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP
    Mercury
    7439-97-6
    0.15
    0.025 mg/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l TCLP
    Selenium
    7782-49-2
    0.82
    5.7 mg/l TCLP
    Silver
    7440-22-4
    0.43
    0.14 mg/l 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

    278
    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/l TCLP
    K002
    Wastewater treatment sludge from the production of chrome yellow and orange pigments.
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP
    K003
    Wastewater treatment sludge from the production of molybdate orange pigments.
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP
    K004
    Wastewater treatment sludge from the production of zinc yellow pigments.
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP
    K005
    Wastewater treatment sludge from the production of chrome green pigments.
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Lead
    7439-92-1
    0.69
    0.75 mg/l 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/l TCLP
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP
    K006
    Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated).
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l 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/l TCLP
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP
    Cyanides (Total)
    7
    57-12-5
    1.2
    590

    279
    K008
    Oven residue from the production of chrome oxide green pigments.
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Lead
    7439-92-1
    0.69
    0.75 mg/l 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
    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

    280
    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/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l 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
    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

    281
    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
    Chloroform
    67-66-3
    0.046
    6.0
    Antimony
    7440-36-0
    1.9
    1.15 mg/l 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 diphenylamine)
    86-30-6
    0.92
    13
    Phenol
    108-95-2
    0.039
    6.2
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l 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

    282
    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
    K027
    Centrifuge and distillation residues from the 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/l TCLP
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l 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

    283
    K030
    Column bodies or heavy ends from the combined production of trichloroethylene and
    perchloroethylene.
    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
    K031
    By-product salts generated in the production of MSMA and cacodylic acid.
    Arsenic
    7440-38-2
    1.4
    5.0 mg/l TCLP
    K032
    Wastewater treatment sludge from the production of chlordane.
    Hexachlorocyclopentadiene
    77-47-4
    0.057
    2.4
    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
    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

    284
    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
    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

    285
    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
    HxCDFs (All Hexachloro-
    dibenzofurans)
    NA
    0.000063
    0.001
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    NA
    0.000063
    0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    NA
    0.000035
    0.001
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    NA
    0.000063
    0.001
    TCDFs (All Tetrachloro-
    dibenzofurans)
    NA
    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/l 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

    286
    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
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Cyanides (Total)
    7
    57-12-5
    1.2
    590
    Lead
    7439-92-1
    0.69
    NA
    Nickel
    7440-02-0
    NA
    11 mg/l 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/l TCLP
    Lead
    7439-92-1
    0.69
    NA
    Nickel
    7440-02-0
    NA
    11 mg/l 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

    287
    Cyanides (Total)
    7
    57-12-5
    1.2
    590
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Lead
    7439-92-1
    0.69
    NA
    Nickel
    7440-02-0
    NA
    11 mg/l 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
    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/l TCLP
    Lead
    7439-92-1
    0.69
    NA
    Nickel
    7440-02-0
    NA
    11 mg/l 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

    288
    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/l TCLP
    Cyanides (Total)
    7
    57-12-5
    1.2
    590
    Lead
    7439-92-1
    0.69
    NA
    Nickel
    7440-02-0
    NA
    11 mg/l TCLP
    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/l TCLP
    Arsenic
    7440-38-2
    NA
    5.0 mg/l TCLP
    Barium
    7440-39-3
    NA
    21 mg/l TCLP
    Beryllium
    7440-41-7
    NA
    1.22 mg/l TCLP
    Cadmium
    7440-43-9
    0.69
    0.11 mg/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP
    Mercury
    7439-97-6
    NA
    0.025 mg/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l TCLP
    Selenium
    7782-49-2
    NA
    5.7 mg/l TCLP
    Silver
    7440-22-4
    NA
    0.14 mg/l TCLP
    Thallium
    7440-28-0
    NA
    0.20 mg/l TCLP
    Zinc
    7440-66-6
    NA
    4.3 mg/l 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/l TCLP
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP
    Nickel
    7440-02-0
    3.98
    NA
    K069
    Emission control dust or sludge from secondary lead smelting. - Calcium sulfate (Low Lead)
    Subcategory
    Cadmium
    7440-43-9
    0.69
    0.11 mg/l TCLP

    289
    Lead
    7439-92-1
    0.69
    0.75 mg/l 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/l 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/l 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
    Diphenylnitrosamine (difficult to
    distinguish from diphenylamine)
    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/l TCLP

    290
    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/l 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
    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

    291
    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/l TCLP
    Cyanides (Total)
    7
    57-12-5
    1.2
    590
    Lead
    7439-92-1
    0.69
    0.75 mg/l 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/l 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
    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/l TCLP
    Arsenic
    7440-38-2
    1.4
    26.1 mg/l TCLP
    Barium
    7440-39-3
    1.2
    21 mg/l TCLP
    Beryllium
    7440-41-7
    0.82
    1.22 mg/l TCLP
    Cadmium
    7440-43-9
    0.69
    0.11 mg/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP

    292
    Mercury
    7439-97-6
    0.15
    0.025 mg/l TCLP
    Nickel
    7440-02-0
    3.98
    11 mg/l TCLP
    Selenium
    7782-49-2
    0.82
    5.7 mg/l TCLP
    Silver
    7440-22-4
    0.43
    0.14 mg/l TCLP
    Cyanide (Total)
    7
    57-12-5
    1.2
    590
    Cyanide (Amenable)
    7
    57-12-5
    0.86
    30
    Fluoride
    16984-48-8
    35
    48 mg/l TCLPNA
    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
    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

    293
    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)
    NA
    0.000063
    0.001
    PeCDDs (All Pentachloro-
    dibenzo-p-dioxins)
    NA
    0.000063
    0.001
    PeCDFs (All Pentachloro-
    dibenzofurans)
    NA
    0.000035
    0.001
    TCDDs (All Tetrachloro-
    dibenzo-p-dioxins)
    NA
    0.000063
    0.001
    TCDFs (All Tetrachloro-
    dibenzofurans)
    NA
    0.000063
    0.001
    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/l TCLP
    Chromium (Total)
    7440-47-3
    2.77
    0.60 mg/l TCLP
    Lead
    7439-92-1
    0.69
    0.75 mg/l 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/l TCLP
    Cadmium
    7440-43-9
    0.69
    NA
    Lead
    7439-92-1
    0.69
    NA
    Mercury
    7439-97-6
    0.15
    NA

    294
    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/l 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
    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)

    295
    nonwastewaters that contain less than 260 mg/kg total mercury that are residues from RMERC.
    Mercury
    7439-97-6
    NA
    0.20 mg/l 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/l 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
    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

    296
    K110
    Condensed column overheads from intermediate 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
    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
    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/l TCLP
    NA
    NA
    CARBN; or
    CMBST
    CMBST

    297
    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
    K124
    Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.
    NA
    NA
    CMBST; or
    CHOXD fb
    (BIODG or
    CARBN)
    CMBST

    298
    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
    K140
    Floor sweepings, off-specification product, and spent filter media from the production of 2,4,6-
    tribromophenol.
    2,4,6-Tribromophenol
    118-79-6
    0.035
    7.4

    299
    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.
    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
    Ideno(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

    300
    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
    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

    301
    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
    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

    302
    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
    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

    303
    Pyridine
    110-86-1
    0.014
    16
    Triethylamine
    121-44-8
    0.081
    1.5
    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

    304
    Pyrene
    129-00-0
    0.067
    8.2
    Toluene (Methyl Benzene)
    108-88-3
    0.080
    10
    Xylene(s) Xylenes (Total)
    1330-20-7
    0.32
    30
    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
    Xylene(s) 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
    Xylene(s) Xylenes (Total)
    1330-20-7
    0.32
    30
    Arsenic
    7740-38-2
    1.4
    5 mg/L TCLP
    Nickel
    7440-02-0
    3.98
    11.0 mg/L TCLP
    Vanadium
    7440-62-2
    4.3
    1.6 mg/L 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
    Xylene(s) Xylenes (Total)
    1330-20-7
    0.32
    30
    Antimony
    7740-36-0
    1.9
    1.15 mg/L TCLP

    305
    Arsenic
    7740-38-2
    1.4
    5 mg/L TCLP
    Nickel
    7440-02-0
    3.98
    11.0 mg/L TCLP
    Vanadium
    7440-62-2
    4.3
    1.6 mg/L TCLP
    Reactive Sulfides
    NA
    DEACT
    DEACT
    P001
    Warfarin, & salts, when present at concentrations greater than 0.3 percent
    Warfarin
    81-81-2
    (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
    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

    306
    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
    P010
    Arsenic acid
    Arsenic
    7440-38-2
    1.4
    5.0 mg/l TCLP
    P011
    Arsenic pentoxide
    Arsenic
    7440-38-2
    1.4
    5.0 mg/l TCLP
    P012
    Arsenic trioxide
    Arsenic
    7440-38-2
    1.4
    5.0 mg/l TCLP
    P013
    Barium cyanide
    Barium
    7440-39-3
    NA
    21 mg/l 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

    307
    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
    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/l TCLP

    308
    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
    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

    309
    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
    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/l TCLP
    P037
    Dieldrin
    Dieldrin
    60-57-1
    0.017
    0.13
    P038
    Diethylarsine
    Arsenic
    7440-38-2
    1.4
    5.0 mg/l 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

    310
    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
    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

    311
    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
    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

    312
    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
    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/l 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/l TCLP

    313
    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
    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

    314
    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/l TCLP
    P074
    Nickel cyanide
    Cyanides (Total)
    7
    57-12-5
    1.2
    590
    Cyanides (Amenable)
    7
    57-12-5
    0.86
    30
    Nickel
    7440-02-0
    3.98
    11 mg/l 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

    315
    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
    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

    316
    than 260 mg/kg total mercury.
    Mercury
    7439-97-6
    NA
    0.20 mg/l 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/l TCLP
    P092
    All P092 (phenyl mercuric acetate) wastewaters.
    Mercury
    7439-97-6
    0.15
    NA
    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

    317
    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/l TCLP
    P101
    Ethyl cyanide (Propanenitrile)
    Ethyl cyanide (Propanenitrile)
    107-12-0
    0.24
    360
    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/l 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/l 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

    318
    P109
    Tetraethyldithiopyrophosphate
    Tetraethyldithiopyrophosphate
    3689-24-5
    CARBN; or
    CMBST
    CMBST
    P110
    Tetraethyl lead
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP
    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/l 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

    319
    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
    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 Zn
    3
    P
    2
    , 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

    320
    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
    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

    321
    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
    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

    322
    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
    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

    323
    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
    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

    324
    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
    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

    325
    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/l TCLP
    U033
    Carbon oxyfluoride
    Carbon oxyfluoride
    353-50-4
    (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST
    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

    326
    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
    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

    327
    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
    Lead
    7439-92-1
    0.69
    0.75 mg/l 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

    328
    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/l TCLP
    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

    329
    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
    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

    330
    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
    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

    331
    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
    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

    332
    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
    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

    333
    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
    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

    334
    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
    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

    335
    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
    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

    336
    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
    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

    337
    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
    χ
    -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
    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

    338
    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/l 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
    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/l TCLP
    U145
    Lead phosphate
    Lead
    7439-92-1
    0.69
    0.75 mg/l TCLP

    339
    U146
    Lead subacetate
    Lead
    7439-92-1
    0.69
    0.75 mg/l 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
    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/l 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/l TCLP

    340
    U151
    All U151 (mercury) wastewater.
    Mercury
    7439-97-6
    0.15
    NA
    U151
    Element 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
    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/l 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

    341
    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
    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

    342
    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
    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

    343
    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
    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

    344
    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
    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

    345
    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
    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

    346
    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/l TCLP
    U205
    Selenium sulfide
    Selenium
    7782-49-2
    0.82
    5.7 mg/l TCLP
    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

    347
    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
    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

    348
    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
    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

    349
    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
    U238
    Urethane (Ethyl carbamate)
    Urethane (Ethyl carbamate)
    51-79-6
    (WETOX or
    CHOXD) fb
    CARBN; or
    CMBST
    CMBST

    350
    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
    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

    351
    U249
    Zinc phosphide, Zn
    3
    P
    2
    , 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

    352
    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

    353
    U408
    2,4,6-Tribromophenol
    2,4,6-Tribromophenol
    118-79-6
    0.035
    7.4
    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/l 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. “;” 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 upon on incineration in units operated in accordance with the technical
    requirements of 35 Ill. Adm. Code 724.Subpart O or 35 Ill. Adm. Code 725.Subpart O
    or based upon 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 35 Ill. Adm. Code 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

    354
    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
    using Method 9010 or 9012, found in “Test Methods for Evaluating Solid Waste,
    Physical or Chemical Methods”, USEPA Publication SW-846, incorporated by
    reference in 35 Ill. Adm. Code 720.111, 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 35 Ill. Adm. Code 724.Subpart O, or (3) combustion units operating under 35 Ill.
    Adm. Code 725.Subpart O.
    BOARD NOTE: Derived from table to 40 CFR 268.40 (1998) (1999), as amended at 63 64
    Fed. Reg. 47415 (Sep. 4, 1998) 56471 (October 20, 1999) and 63 Fed. Reg. 51264 (Sep. 24,
    1998).
    NA
    means not applicable.
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    TITLE 35: ENVIRONMENTAL PROTECTION
    SUBTITLE G: WASTE DISPOSAL
    CHAPTER I: POLLUTION CONTROL BOARD
    SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS

    355
    PART 733
    STANDARDS FOR UNIVERSAL WASTE MANAGEMENT
    SUBPART A: GENERAL
    Section
    733.101
    Scope
    733.102
    Applicability--Batteries
    733.103
    Applicability--Pesticides
    733.104
    Applicability--Mercury Thermostats
    733.105 Applicability--Lamps.
    733.105 Applicability--Household and Conditionally Exempt Small Quantity Generator
    Waste
    733.106 Definitions
    733.107
    Applicability--Mercury-Containing Lamps (Repealed)
    733.108 Applicability--Household and Conditionally Exempt Small Quantity Generator
    Waste
    733.109 Definitions
    SUBPART B: STANDARDS FOR SMALL QUANTITY HANDLERS
    Section
    733.110
    Applicability
    733.111
    Prohibitions
    733.112
    Notification
    733.113
    Waste Management
    733.114
    Labeling and Marking
    733.115
    Accumulation Time Limits
    733.116
    Employee Training
    733.117
    Response to Releases
    733.118
    Off-Site Shipments
    733.119
    Tracking Universal Waste Shipments
    733.120
    Exports
    SUBPART C: STANDARDS FOR LARGE QUANTITY HANDLERS
    Section
    733.130
    Applicability
    733.131
    Prohibitions
    733.132
    Notification
    733.133
    Waste Management
    733.134
    Labeling and Marking
    733.135
    Accumulation Time Limits
    733.136
    Employee Training
    733.137
    Response to Releases
    733.138
    Off-Site Shipments
    733.139
    Tracking Universal Waste Shipments

    356
    733.140
    Exports
    SUBPART D: STANDARDS FOR UNIVERSAL WASTE
    TRANSPORTERS
    Section
    733.150
    Applicability
    733.151
    Prohibitions
    733.152
    Waste Management
    733.153
    Accumulation Time Limits
    733.154
    Response to Releases
    733.155
    Off-site Shipments
    733.156
    Exports
    SUBPART E: STANDARDS FOR DESTINATION FACILITIES
    Section
    733.160
    Applicability
    733.161
    Off-Site Shipments
    733.162
    Tracking Universal Waste Shipments
    SUBPART F: IMPORT REQUIREMENTS
    Section
    733.170
    Imports
    SUBPART G: PETITIONS TO INCLUDE OTHER WASTES
    Section
    733.180
    General
    733.181
    Factors for Petitions to Include Other Wastes
    AUTHORITY: Implementing Sections 7.2, 22.4 and 22.23a and authorized by Section 27 of
    the Environmental Protection Act [415 ILCS 5/7.2, 22.4, 22.23a, and 27].
    SOURCE: Adopted in R95-20 at 20 Ill. Reg. 11291, effective August 1, 1996; amended in
    R96-10/R97-3/R97-5 at 22 Ill. Reg. 944, effective December 16, 1997; amended in R98-12 at
    22 Ill. Reg. 7650, effective April 15, 1998; amended in R99-15 at 23 Ill. Reg. 9502, effective
    July 26, 1999; amended in R00-13 at 24 Ill. Reg. ________, effective
    ______________________.
    SUBPART A: GENERAL
    Section 733.101
    Scope
    a)
    This Part establishes requirements for managing the following:
    1)
    Batteries, as described in Section 733.102;

    357
    2)
    Pesticides, as described in Section 733.103;
    3)
    Thermostats, as described in Section 733.104; and
    4)
    Mercury-containing lampsLamps, as described in Section 733.107
    733.105.
    BOARD NOTE: Subsection (a)(4) of this Section was added pursuant to
    Section 22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502,
    effective August 19, 1997).
    b)
    This Part provides an alternative set of management standards in lieu of
    regulation under 35 Ill. Adm. Code 702 through 705, 720 through 726, and
    728.
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 733.102
    Applicability--Batteries
    a)
    Batteries covered under this Part.
    1)
    The requirements of this Part apply to persons managing batteries, as
    described in Section 733.106 733.109, except those listed in subsection
    (b) below of this Section.
    2)
    Spent lead-acid batteries that are not managed under 35 Ill. Adm. Code
    726.Subpart G, are subject to management under this Part.
    b)
    Batteries not covered under this Part. The requirements of this Part do not apply
    to persons managing the following batteries:
    1)
    Spent lead-acid batteries that are managed under 35 Ill. Adm. Code
    726.Subpart G.
    2)
    Batteries, as described in Section 733.106 733.109, that are not yet
    wastes under 35 Ill. Adm. Code 721, including those that do not meet the
    criteria for waste generation in subsection (c) below of this Section.
    3)
    Batteries, as described in Section 733.106 733.109, that are not
    hazardous waste. A battery is a hazardous waste if it exhibits one or
    more of the characteristics identified in 35 Ill. Adm. Code 721.Subpart
    C.
    c)
    Generation of waste batteries.

    358
    1)
    A used battery becomes a waste on the date it is discarded (e.g., when
    sent for reclamation).
    2)
    An unused battery becomes a waste on the date the handler decides to
    discard it.
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 733.103
    Applicability--Pesticides
    a)
    Pesticides covered under this Part. The requirements of this Part apply to
    persons managing pesticides, as described in Section 733.106 733.109, that meet
    the following conditions, except those listed in subsection (b) below of this
    Section:
    1)
    Recalled pesticides:
    A)
    Stocks of a suspended and canceled pesticide that are part of a
    voluntary or mandatory recall under Section 19(b) of the Federal
    Insecticide, Fungicide and Rodenticide Act (FIFRA; 7 U.S.C.
    USC § 136q), including, but not limited to those owned by the
    registrant responsible for conducting the recall; or
    B)
    Stocks of a suspended or cancelled pesticide, or a pesticide that is
    not in compliance with FIFRA, that are part of a voluntary recall
    by the registrant.
    2)
    Stocks of other unused pesticide products that are collected and managed
    as part of a waste pesticide collection program.
    b)
    Pesticides not covered under this Part. The requirements of this Part do not
    apply to persons managing the following pesticides:
    1)
    Recalled pesticides described in subsection (a)(1) above of this Section,
    and unused pesticide products described in subsection (a)(2) above of this
    Section, that are managed by farmers in compliance with 35 Ill. Adm.
    Code 722.170. (35 Ill. Adm. Code 722.170 addresses pesticides
    disposed of on the farmer’s own farm in a manner consistent with the
    disposal instructions on the pesticide label, providing the container is
    triple rinsed in accordance with 35 Ill. Adm. Code 721.107(b)(3).);
    2)
    Pesticides not meeting the conditions set forth in subsection (a) above of
    this Section must be managed in compliance with the hazardous waste
    regulations in 35 Ill. Adm. Code 702 through 705, 720 through 726, and
    728;

    359
    3)
    Pesticides that are not wastes under 35 Ill. Adm. Code 721, including
    those that do not meet the criteria for waste generation in subsection (c)
    below of this Section or those that are not wastes as described in
    subsection (d) below of this Section; and
    4)
    Pesticides that are not hazardous waste. A pesticide is a hazardous waste
    if it is a waste (see subsection (b)(3) above of this Section) and either it is
    listed in 35 Ill. Adm. Code 721.Subpart D or it exhibits one or more of
    the characteristics identified in 35 Ill. Adm. Code 721.Subpart C.
    c)
    When a pesticide becomes a waste.
    1)
    A recalled pesticide described in subsection (a)(1) above of this Section
    becomes a waste on the first date on which both of the following
    conditions apply:
    A)
    The generator of the recalled pesticide agrees to participate in the
    recall; and
    B)
    The person conducting the recall decides to discard (e.g., burn the
    pesticide for energy recovery).
    2)
    An unused pesticide product described in subsection (a)(2) above of this
    Section becomes a waste on the date the generator decides to discard it.
    d)
    Pesticides that are not wastes. The following pesticides are not wastes:
    1)
    Recalled pesticides described in subsection (a)(1) above of this Section,
    provided that:
    A)
    The person conducting the recall has not made a decision to
    discard the pesticide (e.g., burn it for energy recovery). Until
    such a decision is made, the pesticide does not meet the definition
    of “solid waste” under 35 Ill. Adm. Code 721.102; thus the
    pesticide is not a hazardous waste and is not subject to hazardous
    waste requirements, including those of this Part. This pesticide
    remains subject to the requirements of FIFRA; or
    B)
    The person conducting the recall has made a decision to use a
    management option that, under 35 Ill. Adm. Code 721.102, does
    not cause the pesticide to be a solid waste (i.e., the selected option
    is use (other than use constituting disposal) or reuse (other than
    burning for energy recovery) or reclamation). Such a pesticide is
    not a solid waste and therefore is not a hazardous waste, and is

    360
    not subject to the hazardous waste requirements including this
    Part. This pesticide, including a recalled pesticide that is exported
    to a foreign destination for use or reuse, remains subject to the
    requirements of FIFRA.
    2)
    Unused pesticide products described in subsection (a)(2) above of this
    Section, if the generator of the unused pesticide product has not decided
    to discard them (e.g., burn for energy recovery). These pesticides
    remain subject to the requirements of FIFRA.
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 733.104
    Applicability--Mercury Thermostats
    a)
    Thermostats covered under this Part. The requirements of this Part apply to
    persons managing thermostats, as described in Section 733.106 733.109, except
    those listed in subsection (b) below of this Section.
    b)
    Thermostats not covered under this Part. The requirements of this Part do not
    apply to persons managing the following thermostats:
    1)
    Thermostats that are not yet wastes under 35 Ill. Adm. Code 721.
    Subsection (c) below of this Section describes when thermostats become
    wastes.
    2)
    Thermostats that are not hazardous waste. A thermostat is a hazardous
    waste if it is a waste (see subsection (b)(1) above of this Section) and it
    exhibits one or more of the characteristics identified in 35 Ill. Adm. Code
    721.Subpart C.
    c)
    Generation of waste thermostats.
    1)
    A used thermostat becomes a waste on the date it is discarded (e.g., sent
    for reclamation).
    2)
    An unused thermostat becomes a waste on the date the handler decides to
    discard it.
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 733.105 Applicability--Lamps.
    a) Lamps covered under this Part. The requirements of this Part apply to persons
    that manage lamps, as described in Section 733.109, except those listed in
    subsection (b) of this Section.

    361
    b) Lamps not covered under this Part. The requirements of this Part do not apply
    to persons that manage the following lamps:
    1) Lamps that are not yet wastes under 35 Ill. Adm. Code 721, as provided
    in subsection (c) of this Section.
    2) Lamps that are not hazardous waste. A lamp is a hazardous waste if it
    exhibits one or more of the characteristics identified in 35 Ill. Adm. Code
    721.Subpart C.
    c) Generation of waste lamps.
    1) A used lamp becomes a waste on the date it is discarded.
    2) An unused lamp becomes a waste on the date the handler decides to
    discard it.
    (Source: Former Section 733.105 renumbered to Section 733.108 and amended and new
    Section 733.105 added at 24 Ill. Reg. ________, effective ______________________)
    Section 733.107
    Applicability--Mercury-Containing Lamps (Repealed)
    a) Mercury-containing lamps covered under this Part. The requirements of this
    Part apply to persons managing mercury-containing lamps, except those listed in
    subsection (b) of this Section.
    b) Mercury-containing lamps not covered under this Part. The requirements of this
    Part do not apply to persons managing the following mercury-containing lamps:
    1) Mercury-containing lamps that are not yet wastes under 35 Ill. Adm.
    Code 721, including those that do not meet the criteria for waste
    generation in subsection (c) of this Section.
    2) Mercury-containing lamps that are not hazardous waste. A mercury-
    containing lamp is not a hazardous waste if it does not exhibit one or
    more of the characteristics identified in 35 Ill. Adm. Code 721.Subpart
    C.
    c) Generation of waste mercury-containing lamps.
    1) A used mercury-containing lamp becomes a waste on the date the handler
    permanently removes it from its fixture.
    2) An unused mercury-containing lamp becomes a waste on the date the

    362
    handler decides to discard it.
    BOARD NOTE: Section 733.107 was added pursuant to Section 22.23a of the Act
    [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19, 1997).
    (Source: Repealed at 22 Ill. Reg. ________, effective ______________________)
    Section 733.105 Applicability--Household and Conditionally Exempt Small Quantity
    Generator Waste
    Section 733.108 Applicability--Household and Conditionally Exempt Small Quantity
    Generator Waste
    a)
    Persons managing A person that manages any of the wastes listed below may, at
    their its option, manage them the waste under the requirements of this Part:
    1)
    Household wastes that are exempt under 35 Ill. Adm. Code
    721.104(b)(1) and which are also of the same type as the universal wastes
    defined at Section 733.106 733.109; or
    2)
    Conditionally exempt small quantity generator wastes that are exempt
    under 35 Ill. Adm. Code 721.105 and are also of the same type as the
    universal wastes defined at Section 733.106.
    b)
    Persons A person that commingle commingles the wastes described in
    subsections (a)(1) and (a)(2) above of this Section together with universal waste
    regulated under this Part shall manage the commingled waste under the
    requirements of this Part.
    (Source: Renumbered from Section 733.105 and amended at 24 Ill. Reg. ________, effective
    ______________________)
    Section 733.106 Definitions
    Section 733.109 Definitions
    “Battery” means a device consisting 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.
    “Destination facility” means a facility that treats, disposes of, or recycles a
    particular category of universal waste, except those management activities
    described in Sections 733.113 (a) and (c) and 733.133 (a) and (c). A facility at

    363
    which a particular category of universal waste is only accumulated is not a
    destination facility for purposes of managing that category of universal waste.
    “Electric lamp” means the bulb or tube portion of a lighting device specifically
    designed to produce radiant energy, most often in the ultraviolet, visible, and
    infrared regions of the electromagnetic spectrum.
    BOARD NOTE: The definition of “electric lamp” was added pursuant to
    Section 22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective
    August 19, 1997).
    “FIFRA” means the Federal Insecticide, Fungicide, and Rodenticide Act (7 USC
    136 through 136y).
    “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.
    “Lamp” or “universal waste lamp” is defined as 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 infra-red regions of the
    electromagnetic spectrum. Common examples of universal waste electric lamps
    include, but are not limited to, fluorescent, high intensity discharge, neon,
    mercury vapor, high pressure sodium, and metal halide lamps.
    “Large quantity handler of universal waste” means a universal waste handler (as
    defined in this Section) that accumulates 5,000 kilograms or more total of
    universal waste (batteries, pesticides, thermostats, or mercury-containing lamps,
    calculated collectively) at any time. This designation as a large quantity handler
    of universal waste is retained through the end of the calendar year in which
    5,000 kilograms or more total of universal waste is accumulated.
    BOARD NOTE: Mercury-containing lamps were added pursuant to Section
    22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
    1997).
    “Mercury-containing lamp” means an electric lamp into which mercury is
    purposely introduced by the manufacturer for the operation of the lamp.
    Mercury-containing lamps include, but are not limited to, fluorescent lamps and
    high-intensity discharge lamps.
    BOARD NOTE: The definition of “mercury-containing lamp” was added
    pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502,
    effective August 19, 1997).
    “On-site” means the same or geographically contiguous property that may be
    divided by public or private right-of-way, provided that the entrance and exit
    between the properties is at a cross-roads intersection, and access is by crossing

    364
    as opposed to going along the right of way. Non-contiguous properties, owned
    by the same person but connected by a right-of-way that that person controls and
    to which the public does not have access, are also considered on-site property.
    “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 35 Ill. Adm. Code 720.111,;
    It is an animal drug that has been determined by regulation of the federal
    Secretary of Health and Human Services pursuant to FFDCA Section
    360b(j), incorporated by reference in Section 35 Ill. Adm. Code 720.111,
    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 35 Ill. Adm. Code 720.111, 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 273.6
    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 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.
    “Small quantity handler of universal waste” means a universal waste handler (as
    defined in this Section) that does not accumulate 5,000 kilograms or more total of
    universal waste (batteries, pesticides, thermostats, or mercury-containing lamps,
    calculated collectively) at any time.
    BOARD NOTE: Mercury-containing lamps were added pursuant to Section
    22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
    1997).
    “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 Section 733.113(c)(2) or

    365
    733.133(c)(2).
    “Universal waste” means any of the following hazardous wastes that are subject
    to the universal waste requirements of this Part:
    Batteries, as described in Section 733.102;
    Pesticides, as described in Section 733.103;
    Thermostats, as described in Section 733.104; and
    Mercury-containing lampsLamps, as described in Section 733.107
    733.105.
    BOARD NOTE: Mercury-containing lamps were added as universal
    waste pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see
    P.A. 90-502, effective August 19, 1997).
    “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 universal waste, and sends universal waste to another
    universal waste handler, to a destination facility, or to a foreign
    destination.
    “Universal waste handler” does not mean:
    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 transfer facility” means any transportation-related facility
    including loading docks, parking areas, storage areas, and other similar areas
    where shipments of universal waste are held during the normal course of
    transportation for ten days or less.
    “Universal waste transporter” means a person engaged in the off-site
    transportation of universal waste by air, rail, highway, or water.

    366
    (Source: Renumbered from Section 733.106 and amended at 24 Ill. Reg. ________, effective
    ______________________)
    SUBPART B: STANDARDS FOR SMALL QUANTITY HANDLERS
    Section 733.110
    Applicability
    This Subpart applies to small quantity handlers of universal waste (as defined in Section
    733.106 733.109).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 733.113
    Waste Management
    a)
    Universal waste batteries. A small quantity handler of universal waste shall
    manage universal waste batteries in a way manner that prevents releases of any
    universal waste or component of a universal waste to the environment, as
    follows:
    1)
    A small quantity handler of universal waste shall contain any universal
    waste battery that shows evidence of leakage, spillage, or damage that
    could cause leakage under reasonably foreseeable conditions in a
    container. The container must be closed, structurally sound, compatible
    with the contents of the battery, and must lack evidence of leakage,
    spillage, or damage that could cause leakage under reasonably foreseeable
    conditions.
    2)
    A small quantity handler of universal waste may conduct the following
    activities, as long as the casing of each individual battery cell is not
    breached and remains intact and closed (except that cells may be opened
    to remove electrolyte but must be immediately closed after removal):
    A)
    Sorting batteries by type;
    B)
    Mixing battery types in one container;
    C)
    Discharging batteries so as to remove the electric charge;
    D)
    Regenerating used batteries;
    E)
    Disassembling batteries or battery packs into individual batteries
    or cells;
    F)
    Removing batteries from consumer products; or

    367
    G)
    Removing electrolyte from batteries.
    3)
    A small quantity handler of universal waste that removes electrolyte from
    batteries, or that generates other solid waste (e.g., battery pack materials,
    discarded consumer products) as a result of the activities listed above,
    shall determine whether the electrolyte or other solid waste exhibits a
    characteristic of hazardous waste identified in 35 Ill. Adm. Code
    721.Subpart C.
    A)
    If the electrolyte or other solid waste exhibits a characteristic of
    hazardous waste, it is subject to all applicable requirements of 35
    Ill. Adm. Code 702 through 705, 720 through 726, and 728. The
    handler is considered the generator of the hazardous electrolyte or
    other waste and is subject to 35 Ill. Adm. Code 722.
    B)
    If the electrolyte or other solid waste is not hazardous, the handler
    may manage the waste in any way that is in compliance with
    applicable federal, state State, or local solid (nonhazardous) waste
    regulations.
    BOARD NOTE: See generally the Act and 35 Ill. Adm. Code
    807 through 817 to determine whether additional facility siting,
    special waste, or nonhazardous waste regulations apply to the
    waste. Consult the ordinances of relevant units of local
    government to determine whether local requirements apply.
    b)
    Universal waste pesticides. A small quantity handler of universal waste shall
    manage universal waste pesticides in a way that prevents releases of any
    universal waste or component of a universal waste to the environment. The
    universal waste pesticides must be contained in one or more of the following:
    1)
    A container that remains closed, structurally sound, compatible with the
    pesticide, and that lacks evidence of leakage, spillage, or damage that
    could cause leakage under reasonably foreseeable conditions;
    2)
    A container that does not meet the requirements of subsection (b)(1)
    above of this Section, provided that the unacceptable container is
    overpacked in a container that does meet the requirements of subsection
    (b)(1);
    3)
    A tank that meets the requirements of 35 Ill. Adm. Code 725.Subpart J,
    except for 35 Ill. Adm. Code 725.297(c), 265.300, and 265.301; or
    4)
    A transport vehicle or vessel that is closed, structurally sound, compatible

    368
    with the pesticide, and that lacks evidence of leakage, spillage, or damage
    that could cause leakage under reasonably foreseeable conditions.
    c)
    Universal waste thermostats. A small quantity handler of universal waste shall
    manage universal waste thermostats in a way that prevents releases of any
    universal waste or component of a universal waste to the environment, as
    follows:
    1)
    A small quantity handler of universal waste shall contain any universal
    waste thermostat that shows evidence of leakage, spillage, or damage that
    could cause leakage under reasonably foreseeable conditions in a
    container. The container must be closed, structurally sound, compatible
    with the contents of the thermostat, and must lack evidence of leakage,
    spillage, or damage that could cause leakage under reasonably foreseeable
    conditions.
    2)
    A small quantity handler of universal waste may remove mercury-
    containing ampules from universal waste thermostats provided the handler
    follows each of the following procedures:
    A)
    It removes the ampules in a manner designed to prevent breakage
    of the ampules;
    B)
    It removes ampules only over or in a containment device (e.g.,
    tray or pan sufficient to collect and contain any mercury released
    from an ampule in case of breakage);
    C)
    It ensures that a mercury clean-up system is readily available to
    immediately transfer any mercury resulting from spills or leaks
    from broken ampules, from the containment device to a container
    that meets the requirements of 35 Ill. Adm. Code 722.134;
    D)
    It immediately transfers any mercury resulting from spills or leaks
    from broken ampules from the containment device to a container
    that meets the requirements of 35 Ill. Adm. Code 722.134;
    E)
    It ensures that the area in which ampules are removed is well
    ventilated and monitored to ensure compliance with applicable
    OSHA exposure levels for mercury;
    F)
    It ensures that employees removing ampules are thoroughly
    familiar with proper waste mercury handling and emergency
    procedures, including transfer of mercury from containment
    devices to appropriate containers;

    369
    G)
    It stores removed ampules in closed, non-leaking containers that
    are in good condition; and
    H)
    It packs removed ampules in the container with packing materials
    adequate to prevent breakage during storage, handling, and
    transportation.
    3)
    Required hazardous waste determination and further waste management.
    A)
    A small quantity handler of universal waste that removes mercury-
    containing ampules from thermostats shall determine whether the
    following exhibit a characteristic of hazardous waste identified in
    35 Ill. Adm. Code 721.Subpart C:
    i)
    Mercury or clean-up residues resulting from spills or
    leaks; or
    ii)
    Other solid waste generated as a result of the removal of
    mercury-containing ampules (e.g., remaining thermostat
    units).
    B)
    If the mercury, residues, or other solid waste exhibits a
    characteristic of hazardous waste, it must be managed in
    compliance with all applicable requirements of 35 Ill. Adm. Code
    702 through 705, 720 through 726, and 728. The handler is
    considered the generator of the mercury, residues, or other waste
    and shall manage it is subject to 35 Ill. Adm. Code 722.
    C)
    If the mercury, residues, or other solid waste is not hazardous, the
    handler may manage the waste in any way that is in compliance
    with applicable federal, state, or local solid (nonhazardous) waste
    regulations.
    BOARD NOTE: See generally the Act and 35 Ill. Adm. Code
    807 through 817 to determine whether additional facility siting,
    special waste, or nonhazardous waste regulations apply to the
    waste. Consult the ordinances of relevant units of local
    government to determine whether local requirements apply.
    d)
    Universal waste mercury-containing lampsLamps. A small quantity handler of
    universal waste shall manage universal waste mercury-containing lamps in a
    manner that prevents releases of any universal waste or component of a universal
    waste to the environment, as follows:
    1)
    A small quantity handler of universal waste mercury-containing lamps

    370
    shall, at all times: contain all lamps in containers or packages that are
    structurally sound, adequate to prevent breakage, and compatible with the
    contents of the lamps. Such containers and packages must remain closed
    and must lack evidence of leakage, spillage, or damage that could cause
    leakage under reasonably foreseeable conditions.
    A) Contain unbroken lamps in packaging that will minimize breakage
    during normal handling conditions; and
    B) Contain broken lamps in packaging that will prevent releases of
    lamp fragments and residues.
    2)
    A small quantity handler of universal waste mercury-containing lamps
    shall, at all times, manage waste lamps in a manner designed to minimize
    lamp breakage immediately clean up and place in a container any lamp
    that is broken, and the small quantity handler shall place in a container
    any lamp that shows evidence of breakage, leakage, or damage that could
    cause the release of mercury or other hazardous constituents to the
    environment. Any container used must be closed, structurally sound,
    compatible with the contents of the lamps, and must lack evidence of
    leakage, spillage, or damage that could cause leakage or releases of
    mercury or other hazardous constituents to the environment under
    reasonably foreseeable conditions.
    3) A small quantity handler of universal waste mercury-containing lamps
    shall immediately contain all releases of lamp fragments and residues from
    broken lamps.
    4) A small quantity handler of universal wastes shall undertake hazardous
    waste determination and further waste management as follows:
    A) A small quantity handler of universal waste mercury-containing
    lamps shall determine whether the following exhibit a
    characteristic of hazardous waste identified in 35 Ill. Adm. Code
    721.Subpart C:
    i) Any materials resulting from a release;
    ii) Clean-up residues from spills or breakage; or
    iii) Other solid waste generated as a result of handling waste
    lamps.
    B) If the material, residue, or other solid waste exhibits a
    characteristic of hazardous waste, it shall be managed in

    371
    compliance with all applicable requirements of 35 Ill. Adm. Code
    702 through 705, 720 through 726, and 728. The handler is
    considered to be the generator of the material, residue, or other
    hazardous waste and shall manage it in accordance with 35 Ill.
    Adm. Code 722.
    C) If the material, residue, or other solid waste is not hazardous, the
    handler may manage the waste in any manner that is in
    compliance with applicable federal, State, or local solid
    (nonhazardous) waste regulations.
    5) Small quantity handlers of mercury containing universal waste lamps may
    treat mercury containing lamps for volume reduction at the site where
    they were generated under the following conditions:
    A) The lamps must be crushed in a closed system designed and
    operated in such a manner that any emission of mercury from the
    crushing system shall not exceed 0.1 mg/m
    3
    when measured on
    the basis of time weighted average over an 8-hour period;
    B) The handler must provide notification of crushing activity to the
    Agency quarterly, in a form as provided by the Agency. Such
    notification must include the following information:
    i) Name and address of the handler;
    ii) Estimated monthly amount of lamps crushed; and
    iii) The technology employed for crushing, including any
    certification or testing data provided by the manufacturer
    of the crushing unit verifying that the crushing device
    achieves the emission controls required in subsection
    (d)(5)(A) of this Section;
    C) The handler immediately transfers any material recovered from a
    spill or leak to a container that meets the requirements of 40 CFR
    262.34, and has available equipment necessary to comply with this
    requirement;
    D) The handler ensures that the area in which the lamps are crushed
    is well-ventilated and monitored to ensure compliance with
    applicable OSHA exposure levels for mercury;
    E) The handler ensures that employees crushing lamps are
    thoroughly familiar with proper waste mercury handling and
    emergency procedures, including transfer of mercury from

    372
    containment devices to appropriate containers; and
    F) The crushed lamps are stored in closed, non-leaking containers
    that are in good condition (e.g., no severe rusting, apparent
    structural defects or deterioration), suitable to prevent releases
    during storage, handling and transportation.
    BOARD NOTE: Subsection (d) of this Section was added pursuant to Section
    22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
    1997).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 733.114
    Labeling and Marking
    A small quantity handler of universal waste shall label or mark the universal waste to identify
    the type of universal waste as follows:
    a)
    Universal waste batteries (i.e., each battery) or a container in which the batteries
    are contained must be labeled or marked clearly with any one of the following
    phrases: “Universal Waste-Battery(ies)Batteries”, “Waste Battery(ies) Batteries”,
    or “Used Battery(ies) Batteries”;
    b)
    A container (or multiple container package unit), tank, transport vehicle, or
    vessel in which recalled universal waste pesticides, as described in Section
    733.103(a)(1), are contained must be labeled or marked clearly as follows:
    1)
    The label that was on or accompanied the product as sold or distributed;
    and
    2)
    The words “Universal Waste-Pesticide(s)Pesticides” or “Waste-
    Pesticide(s)Pesticides”;
    c)
    A container, tank, or transport vehicle, or vessel in which unused pesticide
    products, as described in Section 733.103(a)(2), are contained must be labeled or
    marked clearly as follows:
    1)
    Pesticide labeling:
    A)
    The label that was on the product when purchased, if still legible;
    B)
    If using the labels described in subsection (c)(1)(A) above of this
    Section is not feasible, the appropriate label as required under
    USDOT regulation 49 CFR 172; or

    373
    C)
    If using the labels described in subsections (c)(1)(A) and (c)(1)(B)
    above of this Section is not feasible, another label prescribed or
    designated by the waste pesticide collection program administered
    or recognized by a state; and
    2)
    The words “Universal Waste-Pesticide(s)Pesticides” or “Waste-
    Pesticide(s)Pesticides”;
    d)
    Universal waste thermostats (i.e., each thermostat) or a container in which the
    thermostats are contained must be labeled or marked clearly with any one of the
    following phrases: “Universal Waste-Mercury Thermostat(s) Thermostat(s)”, or
    “Waste Mercury Thermostat(s) Thermostat(s)”, or “Used Mercury Thermostat(s)
    Thermostat(s)”; and
    e)
    Universal waste mercury-containing lamps Each lamp or a container or package
    in which the such lamps are contained shall must be labeled or clearly marked
    with any one of the following phrases: “Universal Waste--Mercury-Containing
    Lamp(s)Lamp(s)”, “Waste Mercury-Containing Lamp(s)Lamp(s)” or “Used
    Mercury-Containing Lamp(s)Lamp(s)”.
    BOARD NOTE: Subsection (e) of this Section was added pursuant to Section
    22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
    1997).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    SUBPART C: STANDARDS FOR LARGE QUANTITY HANDLERS
    Section 733.130
    Applicability
    This subpart applies to large quantity handlers of universal waste (as defined in Section 733.106
    733.109).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 733.132
    Notification
    a)
    Written notification of universal waste management.
    1)
    Except as provided in subsections (a)(2) and (a)(3) below of this Section,
    a large quantity handler of universal waste shall have sent written
    notification of universal waste management to the Agency, and received a
    USEPA Identification Number, before meeting or exceeding the 5,000
    kilogram storage limit.

    374
    2)
    A large quantity handler of universal waste that has already notified
    USEPA or the Agency of its hazardous waste management activities and
    has received a USEPA Identification Number is not required to renotify
    under this Section.
    3)
    A large quantity handler of universal waste that manages recalled
    universal waste pesticides, as described in Section 733.103(a)(1), and that
    has sent notification to USEPA or the Agency, as required by 40 CFR
    165, is not required to notify for those recalled universal waste pesticides
    under this Section.
    b)
    This notification must include:
    1)
    The universal waste handler’s name and mailing address;
    2)
    The name and business telephone number of the person at the universal
    waste handler’s site who should be contacted regarding universal waste
    management activities;
    3)
    The address or physical location of the universal waste management
    activities;
    4)
    A list of all of the types of universal waste managed by the handler (e.g,
    batteries, pesticides, thermostats, and or mercury-containing lamps); and
    5)
    A statement indicating that the handler is accumulating more than 5,000
    kilograms of universal waste at one time and the types of universal waste
    (e.g, batteries, pesticides, thermostats, or mercury-containing lamps) the
    handler is accumulating above this quantity.
    BOARD NOTE: At 60 Fed. Reg. 25520-21 (May 11, 1995), USEPA
    explained the generator or consolidation point may use USEPA Form 8700-12
    for notification. (To obtain USEPA Form 8700-12 call the Agency at 217-782-
    6761.) USEPA further explained that it is not necessary for the handler to
    aggregate the amounts of waste at multiple non-contiguous sites for the purposes
    of the 5,000 kilogram determination. Mercury-containing lamps were added as
    universal waste pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see
    P.A. 90-502, effective August 19, 1997).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 733.133
    Waste Management
    a)
    Universal waste batteries. A large quantity handler of universal waste shall

    375
    manage universal waste batteries in a way manner that prevents releases of any
    universal waste or component of a universal waste to the environment, as
    follows:
    1)
    A large quantity handler of universal waste shall contain any universal
    waste battery that shows evidence of leakage, spillage, or damage that
    could cause leakage under reasonably foreseeable conditions in a
    container. The container must be closed, structurally sound, compatible
    with the contents of the battery, and must lack evidence of leakage,
    spillage, or damage that could cause leakage under reasonably foreseeable
    conditions.
    2)
    A large quantity handler of universal waste may conduct the following
    activities, as long as the casing of each individual battery cell is not
    breached and remains intact and closed (except that cells may be opened
    to remove electrolyte but must be immediately closed after removal):
    A)
    Sorting batteries by type;
    B)
    Mixing battery types in one container;
    C)
    Discharging batteries so as to remove the electric charge;
    D)
    Regenerating used batteries;
    E)
    Disassembling batteries or battery packs into individual batteries
    or cells;
    F)
    Removing batteries from consumer products; or
    G)
    Removing electrolyte from batteries.
    3)
    A large quantity handler of universal waste that removes electrolyte from
    batteries or that generates other solid waste (e.g., battery pack materials,
    discarded consumer products) as a result of the activities listed above shall
    determine whether the electrolyte or other solid waste exhibits a
    characteristic of hazardous waste identified in 35 Ill. Adm. Code
    721.Subpart C.
    A)
    If the electrolyte or other solid waste exhibits a characteristic of
    hazardous waste, it must be managed in compliance with all
    applicable requirements of 35 Ill. Adm. Code 702 through 705,
    720 through 726, and 728. The handler is considered the
    generator of the hazardous electrolyte or other waste and is
    subject to 35 Ill. Adm. Code 722.

    376
    B)
    If the electrolyte or other solid waste is not hazardous, the handler
    may manage the waste in any way that is in compliance with
    applicable federal, state State, or local solid (nonhazardous) waste
    regulations.
    BOARD NOTE: See generally the Act and 35 Ill. Adm. Code
    807 through 817 to determine whether additional facility siting,
    special waste, or nonhazardous waste regulations apply to the
    waste. Consult the ordinances of relevant units of local
    government to determine whether local requirements apply.
    b)
    Universal waste pesticides. A large quantity handler of universal waste shall
    manage universal waste pesticides in a way manner that prevents releases of any
    universal waste or component of a universal waste to the environment. The
    universal waste pesticides must be contained in one or more of the following:
    1)
    A container that remains closed, structurally sound, compatible with the
    pesticide, and that lacks evidence of leakage, spillage, or damage that
    could cause leakage under reasonably foreseeable conditions;
    2)
    A container that does not meet the requirements of subsection (b)(1)
    above of this Section, provided that the unacceptable container is
    overpacked in a container that does meet the requirements of subsection
    (b)(1);
    3)
    A tank that meets the requirements of 35 Ill. Adm. Code 725.Subpart J,
    except for 35 Ill. Adm. Code 725.297(c), 725.300, and 725.301; or
    4)
    A transport vehicle or vessel that is closed, structurally sound, compatible
    with the pesticide, and that lacks evidence of leakage, spillage, or damage
    that could cause leakage under reasonably foreseeable conditions.
    c)
    Universal waste thermostats. A large quantity handler of universal waste shall
    manage universal waste thermostats in a way manner that prevents releases of
    any universal waste or component of a universal waste to the environment, as
    follows:
    1)
    A large quantity handler of universal waste shall contain any universal
    waste thermostat that shows evidence of leakage, spillage, or damage that
    could cause leakage under reasonably foreseeable conditions in a
    container. The container must be closed, structurally sound, compatible
    with the contents of the thermostat, and must lack evidence of leakage,
    spillage, or damage that could cause leakage under reasonably foreseeable
    conditions.

    377
    2)
    A large quantity handler of universal waste may remove mercury-
    containing ampules from universal waste thermostats provided the handler
    follows each of the following procedures:
    A)
    It removes the ampules in a manner designed to prevent breakage
    of the ampules;
    B)
    It removes ampules only over or in a containment device (e.g.,
    tray or pan sufficient to collect and contain any mercury released
    from an ampule in case of breakage);
    C)
    It ensures that a mercury clean-up system is readily available to
    immediately transfer any mercury resulting from spills or leaks
    from broken ampules, from the containment device to a container
    that meets the requirements of 35 Ill. Adm. Code 722.134;
    D)
    It immediately transfers any mercury resulting from spills or leaks
    from broken ampules from the containment device to a container
    that meets the requirements of 35 Ill. Adm. Code 722.134;
    E)
    It ensures that the area in which ampules are removed is well
    ventilated and monitored to ensure compliance with applicable
    OSHA exposure levels for mercury;
    F)
    It ensures that employees removing ampules are thoroughly
    familiar with proper waste mercury handling and emergency
    procedures, including transfer of mercury from containment
    devices to appropriate containers;
    G)
    It stores removed ampules in closed, non-leaking containers that
    are in good condition; and
    H)
    It packs removed ampules in the container with packing materials
    adequate to prevent breakage during storage, handling, and
    transportation.
    3)
    Required hazardous waste determination and further waste management.
    A)
    A large quantity handler of universal waste that removes mercury-
    containing ampules from thermostats shall determine whether the
    following exhibit a characteristic of hazardous waste identified in
    35 Ill. Adm. Code 721.Subpart C:
    i)
    Mercury or clean-up residues resulting from spills or

    378
    leaks; or
    ii)
    Other solid waste generated as a result of the removal of
    mercury-containing ampules (e.g., remaining thermostat
    units).
    B)
    If the mercury, residues, or other solid waste exhibits a
    characteristic of hazardous waste, it must be managed in
    compliance with all applicable requirements of 35 Ill. Adm. Code
    702 through 705, 720 through 726, and 728. The handler is
    considered the generator of the mercury, residues, or other waste
    and is subject to 35 Ill. Adm. Code 722.
    C)
    If the mercury, residues, or other solid waste is not hazardous, the
    handler may manage the waste in any way that is in compliance
    with applicable federal, state State, or local solid (nonhazardous)
    waste regulations.
    BOARD NOTE: See generally the Act and 35 Ill. Adm. Code
    807 through 817 to determine whether additional facility siting,
    special waste, or nonhazardous waste regulations apply to the
    waste. Consult the ordinances of relevant units of local
    government to determine whether local requirements apply.
    d)
    Universal waste mercury-containing lamps. Lamps. A large quantity handler of
    universal waste shall manage universal waste mercury-containing lamps in a
    manner that prevents releases of any universal waste or component of a universal
    waste to the environment, as follows:
    1)
    A large quantity handler of universal waste mercury-containing lamps
    shall, at all times: contain all lamps in containers or packages that are
    structurally sound, adequate to prevent breakage, and compatible with the
    contents of the lamps. Such containers and packages must remain closed
    and must lack evidence of leakage, spillage, or damage that could cause
    leakage under reasonably foreseeable conditions.
    A) Contain unbroken lamps in packaging that will minimize breakage
    during normal handling conditions; and
    B) Contain broken lamps in packaging that will prevent releases of
    lamp fragments and residues.
    2)
    A large quantity handler of universal waste mercury-containing lamps
    shall, at all times, manage waste lamps in a manner designed to minimize
    lamp breakage immediately clean up and place in a container any lamp

    379
    that is broken, and the large quantity handler shall place in a container
    any lamp that shows evidence of breakage, leakage, or damage that could
    cause the release of mercury or other hazardous constituents to the
    environment. Any container used must be closed, structurally sound,
    compatible with the contents of the lamps, and must lack evidence of
    leakage, spillage, or damage that could cause leakage or releases of
    mercury or other hazardous constituents to the environment under
    reasonably foreseeable conditions.
    3) A large quantity handler of universal waste mercury-containing lamps
    shall immediately contain all releases of lamp fragments and residues from
    broken lamps.
    4) A large quantity handler of universal waste shall undertake a hazardous
    waste determination and further waste management as follows:
    A) A large quantity handler of universal waste mercury-containing
    lamps shall determine whether the following exhibit a
    characteristic of hazardous waste identified in 35 Ill. Adm. Code
    721.Subpart C:
    i) Any materials resulting from a release;
    ii) Clean-up residues from spills or breakage; or
    iii) Other solid waste generated as a result of handling waste
    lamps.
    B) If the material, residue, or other solid waste exhibits a
    characteristic of hazardous waste, it shall be managed in
    compliance with all applicable requirements of 35 Ill. Adm. Code
    702 through 705, 720 through 726, and 728. The handler is
    considered to be the generator of the material, residue, or other
    hazardous waste and shall manage it in accordance with 35 Ill.
    Adm. Code 722.
    C) If the material, residue, or other solid waste is not hazardous, the
    handler may manage the waste in any manner that is in
    compliance with applicable federal, State, or local solid
    (nonhazardous) waste regulations.
    5) Large quantity handlers of mercury containing universal waste lamps may
    treat mercury containing lamps for volume reduction at the site where
    they were generated under the following conditions:

    380
    A) The lamps must be crushed in a closed system designed and
    operated in such a manner that any emission of mercury from the
    crushing system shall not exceed 0.1 mg/m
    3
    when measured on
    the basis of time weighted average over an 8-hour period;
    B) The handler must provide notification of crushing activity to the
    Agency quarterly, in a form as provided by the Agency. Such
    notification must include the following information:
    i) Name and address of the handler;
    ii) Estimated monthly amount of lamps crushed; and
    iii) The technology employed for crushing, including any
    certification or testing data provided by the manufacturer
    of the crushing unit verifying that the crushing device
    achieves the emission controls required in subsection
    (d)(5)(A) of this Section;
    C) The handler immediately transfers any material recovered from a
    spill or leak to a container that meets the requirements of 40 CFR
    262.34, and has available equipment necessary to comply with this
    requirement;
    D) The handler ensures that the area in which the lamps are crushed
    is well-ventilated and monitored to ensure compliance with
    applicable OSHA exposure levels for mercury;
    E) The handler ensures that employees crushing lamps are
    thoroughly familiar with proper waste mercury handling and
    emergency procedures, including transfer of mercury from
    containment devices to appropriate containers; and
    F) The crushed lamps are stored in closed, non-leaking containers
    that are in good condition (e.g., no severe rusting, apparent
    structural defects or deterioration), suitable to prevent releases
    during storage, handling and transportation.
    BOARD NOTE: Subsection (d) of this Section was added pursuant to Section
    22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
    1997).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    Section 733.134
    Labeling and Marking

    381
    A large quantity handler of universal waste shall label or mark the universal waste to identify
    the type of universal waste as follows:
    a)
    Universal waste batteries (i.e., each battery), or a container or tank in which the
    batteries are contained, must be labeled or marked clearly with any one of the
    following phrases: “Universal Waste-Battery(ies)Batteries”; or “Waste
    Battery(ies)Batteries”; or “Used Battery(ies)Batteries”;
    b)
    A container (or multiple container package unit), tank, transport vehicle or vessel
    in which recalled universal waste pesticides as described in Section 733.103(a)(1)
    are contained must be labeled or marked clearly as follows:
    1)
    The label that was on or accompanied the product as sold or distributed;
    and
    2)
    The words “Universal Waste-Pesticide(s)Pesticides” or “Waste-
    Pesticide(s)Pesticides”;
    c)
    A container, tank, or transport vehicle or vessel in which unused pesticide
    products, as described in Section 733.103(a)(2), are contained must be labeled or
    marked clearly as follows:
    1)
    Pesticide labeling:
    A)
    The label that was on the product when purchased, if still legible;
    B)
    If using the labels described in subsection (c)(1)(A) above of this
    Section is not feasible, the appropriate label as required under the
    USDOT regulation 49 CFR 172; or
    C)
    If using the labels described in subsections (c)(1)(A) and (c)(1)(B)
    above of this Section is not feasible, another label prescribed or
    designated by the pesticide collection program; and
    2)
    The words “Universal Waste-Pesticide(s)Pesticides” or “Waste-
    Pesticide(s)Pesticides”;
    d)
    Universal waste thermostats (i.e., each thermostat) or a container or tank in
    which the thermostats are contained must be labeled or marked clearly with any
    one of the following phrases: “Universal Waste-Mercury Thermostat(s)
    Thermostat(s)”, or “Waste Mercury Thermostat(s) Thermostat(s)”, or “Used
    Mercury Thermostat(s) Thermostat(s)”; and
    e)
    Universal waste mercury-containing lamps Each lamp or a container or package

    382
    in which the such lamps are contained shall must be labeled or clearly marked
    with any one of the following phrases: “Universal Waste-Mercury-Containing
    Lamp(s)Lamps”, “Waste Mercury-Containing Lamp(s)Lamps” or “Used
    Mercury-Containing Lamp(s)Lamps”.
    BOARD NOTE: Subsection (e) of this Section was added pursuant to Section
    22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
    1997).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    SUBPART D: STANDARDS FOR UNIVERSAL WASTE
    TRANSPORTERS
    Section 733.150
    Applicability
    This Subpart applies to universal waste transporters (as defined in Section 733.106 733.109).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    SUBPART E: STANDARDS FOR DESTINATION FACILITIES
    Section 733.160
    Applicability
    a)
    The owner or operator of a destination facility (as defined in Section 733.106
    733.109) is subject to all applicable requirements of 35 Ill. Adm. Code 702
    through 705, 720 724 through 726, and 728, and the notification requirement
    under section 3010 of RCRA.
    b)
    The owner or operator of a destination facility that recycles a particular universal
    waste without storing that universal waste before it is recycled shall comply with
    35 Ill. Adm. Code 721.106(c)(2).
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)
    SUBPART G: PETITIONS TO INCLUDE OTHER WASTES
    Section 733.181
    Factors for Petitions to Include Other Wastes
    a)
    Hazardous waste listing or characteristics. The waste or category of waste, as
    generated by a wide variety of generators, is listed in 35 Ill. Adm. Code
    721.Subpart D, or (if not listed) a proportion of the waste stream exhibits one or
    more characteristics of hazardous waste identified in 35 Ill. Adm. Code

    383
    721.Subpart C. (When a characteristic waste is added to the universal waste
    regulations of this Part by using a generic name to identify the waste category
    (e.g., batteries), the definition of universal waste in 35 Ill. Adm. Code 720.110
    and Section 733.106 733.109 will be amended to include only the hazardous
    waste portion of the waste category (e.g., hazardous waste batteries).) Thus,
    only the portion of the waste stream that does exhibit one or more characteristics
    (i.e., is hazardous waste) is subject to the universal waste regulations of this Part;
    b)
    Generation by a wide variety of types of facilities. The waste or category of
    waste is not exclusive to a specific industry or group of industries, is commonly
    generated by a wide variety of types of establishments (including, for example,
    households, retail and commercial businesses, office complexes, conditionally
    exempt small quantity generators, small businesses, or government organizations,
    as well as large industrial facilities);
    c)
    Generation by a large number of generators. The waste or category of waste is
    generated by a large number of generators (e.g., more than 1,000 nationally) and
    is frequently generated in relatively small quantities by each generator;
    d)
    Collection systems to ensure close stewardship. Systems to be used for
    collecting the waste or category of waste (including packaging, marking, and
    labeling practices) would ensure close stewardship of the waste;
    e)
    Waste management standards and risk to human health and the environment.
    The risk posed by the waste or category of waste during accumulation and
    transport is relatively low compared to other hazardous wastes, and specific
    management standards proposed or referenced by the petitioner (e.g., waste
    management requirements appropriate to be added to Sections 733.113, 733.133,
    and 733.152; or applicable USDOT requirements) would be protective of human
    health and the environment during accumulation and transport;
    f)
    Increased likelihood of diversion of waste from non-hazardous waste
    management systems. Regulation of the waste or category of waste under this
    Part will increase the likelihood that the waste will be diverted from non-
    hazardous waste management systems (e.g., the municipal waste stream, non-
    hazardous industrial or commercial waste stream, municipal sewer or stormwater
    systems) to recycling, treatment, or disposal in compliance with Subtitle C of
    RCRA;
    g)
    Improved implementation of the hazardous waste program. Regulation of the
    waste or category of waste under this Part will improve implementation of and
    compliance with the hazardous waste regulatory program; or
    h)
    Such other factors as may be appropriate.

    384
    (Source: Amended at 24 Ill. Reg. ________, effective ______________________)

    Back to top