ILLINOIS POLLUTION CONTROL BOARD

    April 18, 2002

     

       
    IN THE MATTER OF: )
    ) R02-1
    RCRA SUBTITLE C UPDATE, USEPA )(Identical-in-Substance
    AMENDMENTS (January 1, 2001 through )  Rulemaking - Land)
    June 30, 2001) )
    ________________________________________
    RCRA SUBTITLE C UPDATE, USEPA )R02-12
    AMENDMENTS (July 1, 2001 through )(Identical-in-Substance
    December 31, 2001, January 22, 2002, )  Rulemaking - Land)
    March 13, 2002, and April 9, 2002) )
    ________________________________________
    UIC UPDATE, USEPA AMENDMENTS )R02-17
    (July 1, 2001 through December 31, 2001) )  (Identical-in-Substance
    ) Rulemaking - Land)
    ) (Consolidated)

    Adopted Rule. Final Order.

     

    ORDER OF THE BOARD (by S.T. Lawton, Jr.):

     

    The Board adopts amendments to the Illinois regulations that are “identical in substance” to cover rules adopted by the United States Environmental Protection Agency (USEPA) in two programs:

     

      
    1. 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. (2000)) are adopted by the Board under Sections 7.2 and 22.4(a) of the Environmental Protection Act (Act) (415 ILCS 5/7.2 and 22.4(a) (2000)). Today’s RCRA Subtitle C amendments adopted by USEPA during the periods January 1, 2001 through June 30, 2001 and July 1, 2001 through December 31, 2001, and amendments that occurred on January 22, 2002, March 13, 2002, and April 9, 2002.
    2. Underground injection control (UIC) regulations that USEPA adopted to implement Section 1421 of the federal Safe Drinking Water Act (SDWA) (42 U.S.C. § 300h (2000))are adopted by the Board under Sections 7.2 and 13(c) of the Act (415 ILCS 5/7.2 and 13(c) (2000)). Today’s UIC amendments cover rules adopted by USEPA during the period July 1, 2001 through December 31, 2001.

    This order is supported by an opinion that the Board also adopts today.

     

    IT IS SO ORDERED.

     

     

    I, Dorothy M. Gunn, Clerk of the Illinois Pollution Control Board, certify that the Board adopted the above oorder on April 18, 2002, by a vote of 6-0.

    Dorothy M. Gunn, Clerk

    Illinois Pollution Control Board


    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
    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

     
    703.220 Emergency Permits
    703.221 Alternative Compliance with the Federal NESHAPS
    703.222 Incinerator Conditions Prior to Trial Burn
    703.223 Incinerator Conditions During Trial Burn
    703.224 Incinerator Conditions After Trial Burn
    703.225 Trial Burns for Existing Incinerators
    703.230 Land Treatment Demonstration
    703.231 Research, Development and Demonstration Permits
    703.232 Permits for Boilers and Industrial Furnaces Burning Hazardous Waste
    703.234 Remedial Action Plans

    SUBPART F: PERMIT CONDITIONS OR DENIAL

    Section

     
    703.240 Permit Denial
    703.241 Establishing Permit Conditions
    703.242 Noncompliance Pursuant to Emergency Permit
    703.243 Monitoring
    703.244 Notice of Planned Changes (Repealed)
    703.245 Twenty-four Hour Reporting
    703.246 Reporting Requirements
    703.247 Anticipated Noncompliance
    703.248 Information Repository

    SUBPART G: CHANGES TO PERMITS

    Section

     
    703.260 Transfer
    703.270 Modification
    703.271 Causes for Modification
    703.272 Causes for Modification or Reissuance
    703.273 Facility Siting
    703.280 Permit Modification at the Request of the Permittee
    703.281 Class 1 Modifications
    703.282 Class 2 Modifications
    703.283 Class 3 Modifications

    SUBPART H: REMEDIAL ACTION PLANS

    Section

     
    703.300 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 Sections 7.2 and 22.4 and authorized by Section 27 of the Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].

     

    SOURCE: Adopted in R82-19 at 7 Ill. Reg. 14289, effective October 12, 1983; amended in R83-24 at 8 Ill. Reg. 206, effective December 27, 1983; amended in R84-9 at 9 Ill. Reg. 11899, effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 1110, effective January 2, 1986; amended in R85-23 at 10 Ill. Reg. 13284, effective July 28, 1986; amended in R86-1 at 10 Ill. Reg. 14093, effective August 12, 1986; amended in R86-19 at 10 Ill. Reg. 20702, effective December 2, 1986; amended in R86-28 at 11 Ill. Reg. 6121, effective March 24, 1987; amended in R86-46 at 11 Ill. Reg. 13543, effective August 4, 1987; amended in R87-5 at 11 Ill. Reg. 19383, effective November 12, 1987; amended in R87-26 at 12 Ill. Reg. 2584, effective January 15, 1988; amended in R87-39 at 12 Ill. Reg. 13069, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 447, effective December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18477, effective November 13, 1989; amended in R89-9 at 14 Ill. Reg. 6278, effective April 16, 1990; amended in R90-2 at 14 Ill. Reg. 14492, effective August 22, 1990; amended in R90-11 at 15 Ill. Reg. 9616, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14554, effective September 30, 1991; amended in R91-13 at 16 Ill. Reg. 9767, effective June 9, 1992; amended in R92-10 at 17 Ill. Reg. 5774, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20794, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6898, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12392, effective July 29, 1994; amended in R94-5 at 18 Ill. Reg. 18316, effective December 20, 1994; amended in R95-6 at 19 Ill. Reg. 9920, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 11225, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 553, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7632, effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17930, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 2153, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9381, effective July 26, 1999; amended in R00-13 at 24 Ill. Reg. 9765, effective June 20, 2000; amended in R01-21/R01-23 at 25 Ill. Reg. 9313, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. ________, effective ______________________.

     

     

    SUBPART G: CHANGES TO PERMITS

     

     
    Section 703.280 Permit Modification at the Request of the Permittee
        
    a) Class 1 modifications. See Section 703.281.
    b) Class 2 modifications. See Section 703.282.
    c) Class 3 modifications. See Section 703.283.
    d) Other modifications.
      
    1) In the case of modifications not explicitly listed in Appendix A, the permittee may submit a Class 3 modification request to the Agency, or the permittee may request a determination by the Agency that the modification be reviewed and approved as a Class 1 or Class 2 modification. If the permittee requests that the modification be classified as a Class 1 or 2 modification, the permittee must provide the Agency with the necessary information to support the requested classification.
    2) The Agency must make the determination described in subsection (d)(1) of this Section as promptly as practicable. In determining the appropriate class for a specific modification, the Agency must consider the similarity of the modification to other modifications codified in Appendix A and the following criteria:
      
    A) Class 1 modifications apply to minor changes that keep the permit current with routine changes to the facility or its operation. These changes do not substantially alter the permit conditions or reduce the capacity of the facility to protect human health or the environment. In the case of Class 1 modifications, the Agency may require prior approval.
    B) Class 2 modifications apply to changes that are necessary to enable a permittee to respond, in a timely manner, to any of the following:
       
    i) Common variations in the types and quantities of the wastes managed under the facility permit;
    ii) Technological advances; and
    iii) Changes necessary to comply with new regulations, where these changes can be implemented without substantially changing design specifications or management practices in the permit.
     
    C) Class 3 modifications substantially alter the facility or its operation.
     
    e) Temporary authorizations.
      
    1) Upon request of the permittee, the Agency shall must, without prior public notice and comment, grant the permittee a temporary authorization in accordance with this subsection. Temporary authorizations have a term of not more than 180 days.
    2) Procedures.
     
    A) The permittee may request a temporary authorization for the following:
      
    i) Any Class 2 modification meeting the criteria in subsection (e)(3)(B) of this Section; and
    ii) Any Class 3 modification that meets the criteria in subsection (e)(3)(B)(i) or that meets the criteria in subsections (e)(3)(B)(iii) through (v) and provides improved management or treatment of a hazardous waste already listed in the facility permit.
     
    B) The temporary authorization request must include the following:
       
    i) A description of the activities to be conducted under the temporary authorization;
    ii) An explanation of why the temporary authorization is necessary; and
    iii) Sufficient information to ensure compliance with 35 Ill. Adm. Code 724 standards.
     
    C) The permittee must send a notice about the temporary authorization request to all persons on the facility mailing list maintained by the Agency and to appropriate units of State and local governments as specified in 35 Ill. Adm. Code 705.163(a)(5). This notification must be made within seven days after submission of the authorization request.
     
    3) The Agency must approve or deny the temporary authorization as quickly as practical. To issue a temporary authorization, the Agency must find as follows:
      
    A) That the authorized activities are in compliance with the standards of 35 Ill. Adm. Code 724.
    B) That the temporary authorization is necessary to achieve one of the following objectives before action is likely to be taken on a modification request:
         
    i) To facilitate timely implementation of closure or corrective action activities;
    ii) To allow treatment or storage in tanks, containers or in containment buildings in accordance with 35 Ill. Adm. Code 728;
    iii) To prevent disruption of ongoing waste management activities;
    iv) To enable the permittee to respond to sudden changes in the types or quantities of the wastes managed under the facility permit; or
    v) To facilitate other changes to protect human health and the environment.
     
    4) A temporary authorization must be reissued for one additional term of up to 180 days, provided that the permittee has requested a Class 2 or 3 permit modification for the activity covered in the temporary authorization and either of the following is true:
      
    A) The reissued temporary authorization constitutes the Agency’s decision on a Class 2 permit modification in accordance with Section 703.282(f)(1)(D) or (f)(2)(D); or
    B) The Agency determines that the reissued temporary authorization involving a Class 3 permit modification request is warranted to allow the authorized activities to continue while the modification procedures of 35 Ill. Adm. Code 703.283 are conducted.
     
    f) Public notice and appeals of permit modification decisions.
       
    1) The Agency must notify persons on the facility mailing list and appropriate units of State and local government within 10 days after any decision to grant or deny a Class 2 or 3 permit modification request. The Agency must also notify such persons within 10 days after an automatic authorization for a Class 2 modification goes into effect under Section 703.282(f)(3) or (f)(5).
    2) The Agency’s decision to grant or deny a Class 2 or 3 permit modification request may be appealed under the permit appeal procedures of 35 Ill. Adm. Code 705.212.
    3) An automatic authorization that goes into effect under Section 703.282(f)(3) or (f)(5) may be appealed under the permit appeal procedures of 35 Ill. Adm. Code 705.212; however, the permittee may continue to conduct the activities pursuant to the automatic authorization until the Board enters a final order on the appeal notwithstanding the provisions of 35 Ill. Adm. Code 705.204.
     
    g) Newly regulated wastes and units.
     
    1) The permittee is authorized to continue to manage wastes listed or identified as hazardous under 35 Ill. Adm. Code 721, or to continue to manage hazardous waste in units newly regulated as hazardous waste management units, if each of the following is true:
         
    A) The unit was in existence as a hazardous waste facility with respect to the newly listed or characterized waste or newly regulated waste management unit on the effective date of the final rule listing or identifying the waste, or regulating the unit;
    B) The permittee submits a Class 1 modification request on or before the date on which the waste becomes subject to the new requirements;
    C) The permittee is in compliance with the applicable standards of 35 Ill. Adm. Code 725 and 726;
    D) The permittee also submits a complete class 2 or 3 modification request within 180 days after the effective date of the rule listing or identifying the waste, or subjecting the unit to management standards under 35 Ill. Adm. Code 724, 725 or 726; and
    E) In the case of land disposal units, the permittee certifies that such unit is in compliance with all applicable requirements of 35 Ill. Adm. Code 725 for groundwater monitoring and financial responsibility requirements on the date 12 months after the effective date of the rule identifying or listing the waste as hazardous, or regulating the unit as a hazardous waste management unit. If the owner or operator fails to certify compliance with all these requirements, the owner or operator loses authority to operate under this Section.
     
    2) New wastes or units added to a facility’s permit under this subsection do not constitute expansions for the purpose of the 25 percent capacity expansion limit for Class 2 modifications.
     
    h) Military hazardous waste munitions treatment and disposal. The permittee is authorized to continue to accept waste military munitions notwithstanding any permit conditions barring the permittee from accepting off-site wastes, if each of the following is true:
       
    1) The facility was in existence as a hazardous waste facility and the facility was already permitted to handle the waste military munitions on the date when the waste military munitions became subject to hazardous waste regulatory requirements;
    2) On or before the date when the waste military munitions become subject to hazardous waste regulatory requirements, the permittee submits a Class 1 modification request to remove or amend the permit provision restricting the receipt of off-site waste munitions; and
    3) The permittee submits a complete Class 2 modification request within 180 days after the date when the waste military munitions became subject to hazardous waste regulatory requirements.
      
    i) Permit modification list. The Agency must maintain a list of all approved permit modifications and must publish a notice once a year in a State-wide newspaper that an updated list is available for review.
    j) Combustion facility changes to meet federal 40 CFR 63 MACT standards. The following procedures apply to hazardous waste combustion facility permit modifications requested under Section 703.Appendix A, paragraph L(9).
      
    1) Facility owners or operators must comply have complied with the federal notification of intent to comply (NIC) requirements of 40 CFR 63.1210(b) and (c) before 63.1210 that was in effect prior to May 14, 2001, (see 40 CFR 63 (2000)) in order to request a permit modification can be requested under this Section.
    2) If the Agency does not act to either approve or deny the request within 90 days of receiving it, the request must be deemed approved. The Agency may, at its discretion, extend this 90-day deadline one time for up to 30 days by notifying the facility owner or operator in writing before the 90 days has expired.

    BOARD NOTE: Derived from 40 CFR 270.42(d) through (j) (2000), as amended at 65 Fed. Reg. 42302 (July 10, 2000).

     

    (Source: Amended at 26 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 AND REFERENCES

    Section

     
    720.110 Definitions
    720.111 References

    SUBPART C: RULEMAKING PETITIONS AND OTHER PROCEDURES

    Section

     
    720.120 Rulemaking
    720.121 Alternative Equivalent Testing Methods
    720.122 Waste Delisting
    720.123 Petitions for Regulation as Universal Waste
    720.130 Procedures for Solid Waste Determinations
    720.131 Solid Waste Determinations
    720.132 Boiler Determinations
    720.133 Procedures for Determinations
    720.140 Additional regulation of certain hazardous waste Recycling Activities on a case-by-case Basis
    720.141 Procedures for case-by-case regulation of hazardous waste Recycling Activities
     
    720.Appendix A Overview of 40 CFR, 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 at 5 Ill. Reg. 9781, effective May 17, 1982; amended and codified in R81-22 at 6 Ill. Reg. 4828, effective May 17, 1982; amended in R82-19 at 7 Ill. Reg. 14015, effective October 12, 1983; amended in R84-9 at 9 Ill. Reg. 11819, effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 968, effective January 2, 1986; amended in R86-1 at 10 Ill. Reg. 13998, effective August 12, 1986; amended in R86-19 at 10 Ill. Reg. 20630, effective December 2, 1986; amended in R86-28 at 11 Ill. Reg. 6017, effective March 24, 1987; amended in R86-46 at 11 Ill. Reg. 13435, effective August 4, 1987; amended in R87-5 at 11 Ill. Reg. 19280, effective November 12, 1987; amended in R87-26 at 12 Ill. Reg. 2450, effective January 15, 1988; amended in R87-39 at 12 Ill. Reg. 12999, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 362, effective December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18278, effective November 13, 1989; amended in R89-2 at 14 Ill. Reg. 3075, effective February 20, 1990; amended in R89-9 at 14 Ill. Reg. 6225, effective April 16, 1990; amended in R90-10 at 14 Ill. Reg. 16450, effective September 25, 1990; amended in R90-17 at 15 Ill. Reg. 7934, effective May 9, 1991; amended in R90-11 at 15 Ill. Reg. 9323, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14446, effective September 30, 1991; amended in R91-13 at 16 Ill. Reg. 9489, effective June 9, 1992; amended in R92-1 at 16 Ill. Reg. 17636, effective November 6, 1992; amended in R92-10 at 17 Ill. Reg. 5625, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20545, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6720, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12160, effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17480, effective November 23, 1994; amended in R95-6 at 19 Ill. Reg. 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, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9094, effective July 26, 1999; amended in R00-5 at 24 Ill. Reg. 1063, effective January 6, 2000; amended in R00-13 at 24 Ill. Reg. 9443, effective June 20, 2000; amended in R01-3 at 25 Ill. Reg. 1266, effective January 11, 2001; amended in R01-21/R01-23 at 25 Ill. Reg. 9168, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. ________, effective ______________________.

     

     

    SUBPART B: DEFINITIONS AND REFERENCES

     

     
    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 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 United States Environmental Protection Agency or the Administrator’s designee.

     

    “Agency” means the Illinois Environmental Protection Agency.

     

    “Ancillary equipment” means any device, including, but not limited to, such devices as piping, fittings, flanges, valves, and pumps, that is used to distribute, meter, or control the flow of hazardous waste from its point of generation to storage or treatment tanks, between hazardous waste storage and treatment tanks to a point of disposal onsite, or to a point of shipment for disposal off-site.

     

    “Aquifer” means a geologic formation, group of formations, or part of a formation capable of yielding a significant amount of groundwater to wells or springs.

     

    “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:

     

    Boiler physical characteristics.

     

    The unit must have physical provisions for recovering and exporting thermal energy in the form of steam, heated fluids, or heated gases; and the unit’s combustion chamber and primary energy recovery sections must be of integral design. To be of integral design, the combustion chamber and the primary energy recovery sections (such as waterwalls and superheaters) must be physically formed into one manufactured or assembled unit. A unit in which the combustion chamber and the primary energy recovery sections are joined only by ducts or connections carrying flue gas is not integrally designed; however, secondary energy recovery equipment (such as economizers or air preheaters) need not be physically formed into the same unit as the combustion chamber and the primary energy recovery section. The following units are not precluded from being boilers solely because they are not of integral design: process heaters (units that transfer energy directly to a process stream) and fluidized bed combustion units; and

     

    While in operation, the unit must maintain a thermal energy recovery efficiency of at least 60 percent, calculated in terms of the recovered energy compared with the thermal value of the fuel; and

     

    The unit must export and utilize at least 75 percent of the recovered energy, calculated on an annual basis. In this calculation, no credit shall may be given for recovered heat used internally in the same unit. (Examples of internal use are the preheating of fuel or combustion air, and the driving of induced or forced draft fans or feedwater pumps.); or

     

    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 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 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 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,

     

    Of which any of the following is true:

     

    The facility has received a RCRA permit (or interim status) pursuant to 35 Ill. Adm. Code 702, 703 and 705;

     

    The facility has received a RCRA permit from USEPA pursuant to 40 CFR 124 and 270 (1999);

     

    The facility has received a RCRA permit from a state authorized by USEPA pursuant to 40 CFR 271 (1999); or

     

    The facility is regulated under 35 Ill. Adm. Code 721.106(c)(2) or 266.Subpart F; and

     

    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 that has been authorized by USEPA pursuant to 40 CFR 271, but which has not yet obtained authorization to regulate that waste as hazardous, then the designated facility must be a facility allowed by the receiving state to accept such waste.

     

    “Destination facility” means a facility that treats, disposes of, or recycles a particular category of universal waste, except those management activities described in 35 Ill. Adm. Code 733.113(a) and (c) and 733.133(a) and (c). A facility at which a particular category of universal waste is only accumulated is not a destination facility for the purposes of managing that category of universal waste.

     

    “Dike” means an embankment or ridge of either natural or manmade materials used to prevent the movement of liquids, sludges, solids, or other materials.

     

    “Dioxins and furans” or “D/F” means tetra, penta, hexa, hepta, and octa-chlorinated dibenzo dioxins and furans.

     

    “Director” means the Director of the Illinois Environmental Protection Agency.

     

    “Discharge” or “hazardous waste discharge” means the accidental or intentional spilling, leaking, pumping, pouring, emitting, emptying, or dumping of hazardous waste into or on any land or water.

     

    “Disposal” means the discharge, deposit, injection, dumping, spilling, leaking, or placing of any solid waste or hazardous waste into or on any land or water so that such solid waste or hazardous waste or any constituent thereof may enter the environment or be emitted into the air or discharged into any waters, including groundwaters.

     

    “Disposal facility” means a facility or part of a facility at which hazardous waste is intentionally placed into or on any land or water and at which waste will remain after closure. The term disposal facility does not include a corrective action management unit (CAMU) into which remediation wastes are placed.

     

    “Drip pad” means an engineered structure consisting of a curbed, free-draining base, constructed of non-earthen materials and designed to convey preservative kick-back or drippage from treated wood, precipitation and surface water runon to an associated collection system at wood preserving plants.

     

    “Elementary neutralization unit” means a device 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.

     

    “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 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

     

    The owner or operator had entered into contractual obligations that could not be canceled or modified without substantial loss for physical construction of the facility to be completed within a reasonable time.

     

    “Existing portion” means that land surface area of an existing waste management unit, included in the original Part A permit application, on which wastes have been placed prior to the issuance of a permit.

     

    “Existing tank system” or “existing component” means a tank system or component that is used for the storage or treatment of hazardous waste and which was in operation or for which installation was commenced on or prior to July 14, 1986. Installation will be considered to have commenced if the owner or operator has obtained all federal, State, and local approvals or permits necessary to begin physical construction of the site or installation of the tank system and if either of the following is true:

     

    A continuous on-site physical construction or installation program has begun; or

     

    The owner or operator has entered into contractual obligations that cannot be canceled or modified without substantial loss for physical construction of the site or installation of the tank system to be completed within a reasonable time.

     

    “Explosives or munitions emergency” means a situation involving the suspected or detected presence of unexploded ordnance (UXO), damaged or deteriorated explosives or munitions, an improvised explosive device (IED), other potentially explosive material or device, or other potentially harmful military chemical munitions or device, that creates an actual or potential imminent threat to human health, including safety, or the environment, including property, as determined by an explosives or munitions emergency response specialist. Such situations may require immediate and expeditious action by an explosives or munitions emergency response specialist to control, mitigate, or eliminate the threat.

     

    “Explosives or munitions emergency response” means all immediate response activities by an explosives and munitions emergency response specialist to control, mitigate, or eliminate the actual or potential threat encountered during an explosives or munitions emergency. An explosives or munitions emergency response may include in-place render-safe procedures, treatment, or destruction of the explosives or munitions or transporting those items to another location to be rendered safe, treated, or destroyed. Any reasonable delay in the completion of an explosives or munitions emergency response caused by a necessary, unforeseen, or uncontrollable circumstance will not terminate the explosives or munitions emergency. Explosives and munitions emergency responses can occur on either public or private lands and are not limited to responses at RCRA facilities.

     

    “Explosives or munitions emergency response specialist” means an individual trained in chemical or conventional munitions or explosives handling, transportation, render-safe procedures, or destruction techniques. Explosives or munitions emergency response specialists include United States Department of Defense (USDOD) emergency explosive ordnance disposal (EOD), technical escort unit (TEU), and USDOD-certified civilian or contractor personnel and other federal, State, or local government or civilian personnel who are similarly trained in explosives or munitions emergency responses.

     

    “Facility” means:

     

    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 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 produces hazardous waste identified or listed in 35 Ill. Adm. Code 721 or whose act first causes a hazardous waste to become subject to regulation.

     

    “Groundwater” means water below the land surface in a zone of saturation.

     

    “Hazardous waste” means a hazardous waste as defined in 35 Ill. Adm. Code 721.103.

     

    “Hazardous waste constituent” means a constituent that caused the hazardous waste 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 of which the following is true:

     

    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

     

    The facility meets the definition of infrared incinerator or plasma arc incinerator.

     

    “Incompatible waste” means a hazardous waste 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;

     

    Halogen acid furnaces (HAFs) for the production of acid from halogenated hazardous waste generated by chemical production facilities where the furnace is located on the site of a chemical production facility, the acid product has a halogen acid content of at least three percent, the acid product is used in a manufacturing process, and, except for hazardous waste burned as fuel, hazardous waste fed to the furnace has a minimum halogen content of 20 percent, as generated; and

     

    Any other such device as the Agency determines to be an industrial furnace on the basis of one or more of the following factors:

     

    The design and use of the device primarily to accomplish recovery of material products;

     

    The use of the device to burn or reduce raw materials to make a material product;

     

    The use of the device to burn or reduce secondary materials as effective substitutes for raw materials, in processes using raw materials as principal feedstocks;

     

    The use of the device to burn or reduce secondary materials as ingredients in an industrial process to make a material product;

     

    The use of the device in common industrial practice to produce a material product; and

     

    Other relevant factors.

     

    “Individual generation site” means the contiguous site at or on which one or more hazardous wastes are generated. An individual generation site, such as a large manufacturing plant, may have one or more sources of hazardous waste but is considered a single or individual generation site if the site or property is contiguous.

     

    “Infrared incinerator” means any enclosed device that uses electric powered resistance heaters as a source of radiant heat followed by an afterburner using controlled flame combustion and which is not listed as an industrial furnace.

     

    “Inground tank” means a device meeting the definition of tank whereby a portion of the tank wall is situated to any degree within the ground, thereby preventing visual inspection of that external surface area of the tank that is in the ground.

     

    “In operation” refers to a facility that is treating, storing, or disposing of hazardous waste.

     

    “Injection well” means a well into which fluids are being injected. (See also “underground injection”.)

     

    “Inner liner” means a continuous layer of material placed inside a tank or container that protects the construction materials of the tank or container from the contained waste or reagents used to treat the waste.

     

    “Installation inspector” means a person who, by reason of knowledge of the physical sciences and the principles of engineering, acquired by a professional education and related practical experience, is qualified to supervise the installation of tank systems.

     

    “International shipment” means the transportation of hazardous waste into or out of the jurisdiction of the United States.

     

    “Lamp” or “universal waste lamp” means the bulb or tube portion of an electric lighting device. A lamp is specifically designed to produce radiant energy, most often in the ultraviolet, visible, or 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 that uses a liner to provide isolation of wastes from adjacent cells or wastes. Examples of landfill cells are trenches and pits.

     

    “LDS” means leak detection system.

     

    “Leachate” means any liquid, including any suspended components in the liquid, that has percolated through or drained from hazardous waste.

     

    “Liner” means a continuous layer of natural or manmade materials beneath or on the sides of a surface impoundment, landfill, or landfill cell that restricts the downward or lateral escape of hazardous waste, hazardous waste constituents, or leachate.

     

    “Leak-detection system” means a system capable of detecting the failure of either the primary or secondary containment structure or the presence of a release of hazardous waste or accumulated liquid in the secondary containment structure. Such a system must employ operational controls (e.g., daily visual inspections for releases into the secondary containment system of aboveground tanks) or consist of an interstitial monitoring device designed to detect continuously and automatically the failure of the primary or secondary containment structure or the presence of a release of hazardous waste into the secondary containment structure.

     

    “Management” or “hazardous waste management” means the systematic control of the collection, source separation, storage, transportation, processing, treatment, recovery, and disposal of hazardous waste.

     

    “Manifest” means the shipping document originated and signed by the generator 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.

     

    “Military munitions” means all ammunition products and components produced or used by or for the United States Department of Defense or the United States Armed Services for national defense and security, including military munitions under the control of the United States Department of Defense, the United States Coast Guard, the United States Department of Energy (USDOE), and National Guard personnel. The term military munitions includes: confined gaseous, liquid, and solid propellants, explosives, pyrotechnics, chemical and riot control agents, smokes, and incendiaries used by USDOD components, including bulk explosives and chemical warfare agents, chemical munitions, rockets, guided and ballistic missiles, bombs, warheads, mortar rounds, artillery ammunition, small arms ammunition, grenades, mines, torpedoes, depth charges, cluster munitions and dispensers, demolition charges, and devices and components of these items and devices. Military munitions do not include wholly inert items, improvised explosive devices, and nuclear weapons, nuclear devices, and nuclear components of these items and devices. However, the term does include non-nuclear components of nuclear devices, managed under USDOE’s nuclear weapons program after all sanitization operations required under the Atomic 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 hazardous waste that is transported to a facility in an individual vehicle.

     

    “New hazardous waste management facility” or “new facility” means a facility that began operation, or for which construction commenced after November 19, 1980. (See also “Existing hazardous waste management facility”.)

     

    “New tank system” or “new tank component” means a tank system or component that will be used for the storage or treatment of hazardous waste and for which installation commenced after July 14, 1986; except, however, for purposes of 35 Ill. Adm. Code 724.293(g)(2) and 725.293(g)(2), a new tank system is one for which construction commenced after July 14, 1986. (See also “existing tank system”.)

     

    “Onground tank” means a device meeting the definition of tank that is situated in such a way that the bottom of the tank is on the same level as the adjacent surrounding surfaces so that the external tank bottom cannot be visually inspected.

     

    “On-site” means the same or geographically contiguous property 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 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 that contains other active hazardous waste management units. For example, partial closure may include the closure of a tank (including its associated piping and underlying containment systems), landfill cell, surface impoundment, waste pile, or other hazardous waste management unit, while other units of the same facility continue to operate.

     

    “Person” means an individual, trust, firm, joint stock company, federal agency, corporation (including a government corporation), partnership, association, state, municipality, commission, political subdivision of a state, or any interstate body.

     

    “Personnel” or “facility personnel” means all persons who work at or oversee the operations of a hazardous waste facility and whose actions or failure to act may result in noncompliance with the requirements of 35 Ill. Adm. Code 724 or 725.

     

    “Pesticide” means any substance or mixture of substances intended for preventing, destroying, repelling, or mitigating any pest or intended for use as a plant regulator, defoliant, or desiccant, other than any article that fulfills one of the following descriptions:

     

    It is a new animal drug under section 201(v) of the Federal Food, Drug and Cosmetic Act (FFDCA; 21 USC 321(v)), incorporated by reference in Section 720.111;

     

    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 paragraphs of this definition.

    BOARD NOTE: The second exception of corresponding 40 CFR 260.10 reads as follows: “Is an animal drug that has been determined by regulation of the Secretary of Health and Human Services not to be a new animal drug”. This is very similar to the language of section 2(u) of the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA; 7 USC 136(u)). The three exceptions, taken together, appear intended not to include as pesticide any material within the scope of federal Food and Drug Administration regulation. The Board codified this provision with the intent of retaining the same meaning as its federal counterpart while adding the definiteness required under Illinois law.

     

    “Pile” means any noncontainerized accumulation of solid, non-flowing hazardous waste that is used for treatment or storage, and that is not a containment building.

     

    “Plasma arc incinerator” means any enclosed device that uses a high intensity electrical discharge or arc as a source of heat followed by an afterburner using controlled flame combustion and which is not listed as an industrial furnace.

     

    “Point source” means any discernible, confined, and discrete conveyance, including, but not limited to, any pipe, ditch, channel, tunnel, conduit, well, discrete fissure, container, rolling stock, concentrated animal feeding operation, or vessel or other floating craft from which pollutants are or may be discharged. This term does not include return flows from irrigated agriculture.

     

    “Publicly owned treatment works” or “POTW” is as defined in 35 Ill. Adm. Code 310.110.

     

    “Qualified groundwater scientist” means a scientist or engineer who has received a baccalaureate or postgraduate degree in the natural sciences or engineering, and has sufficient training and experience in groundwater hydrology and related fields, as demonstrated by state registration, professional certifications, or completion of accredited university courses that enable the individual to make sound professional judgments regarding groundwater monitoring and contaminant rate and transport.

    BOARD NOTE: State registration includes, but is not limited to, registration as a professional engineer with the Department of Professional Regulation, pursuant to 225 ILCS 325 and 68 Ill. Adm. Code 1380. Professional certification includes, but is not limited to, certification under the certified groundwater professional program of the National Ground Water Association.

     

    “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 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) 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 Classification Code as defined in Standard Industrial 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 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 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 that is a natural topographic depression, manmade excavation, or diked area formed primarily of earthen materials (although it may be lined with 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-tetrachlorodibenzo-p-dioxin.

     

    “Thermal treatment” means the treatment of hazardous waste in a device that uses elevated temperatures as the primary means to change the chemical, physical, or biological character or composition of the hazardous waste. Examples of thermal treatment processes are incineration, molten salt, pyrolysis, calcination, wet air oxidation, and microwave discharge. (See also “incinerator” and “open burning”.)

     

    “Thermostat” means a temperature control device that contains metallic mercury in an ampule attached to a bimetal sensing element and mercury-containing ampules that have been removed from such a temperature control device in compliance with the requirements of 35 Ill. Adm. Code 733.113(c)(2) or 733.133(c)(2).

     

    “Totally enclosed treatment facility” means a facility for the treatment of hazardous waste that is directly connected to an industrial production process and which is constructed and operated in a manner 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.

     

    “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 the waste, recover energy or material resources from the waste, or render the waste non-hazardous or less hazardous; safer to transport, store, or dispose of; or amenable for recovery, amenable for storage, or reduced in volume.

     

    “Treatment zone” means a soil area of the unsaturated zone of a land treatment unit within which hazardous constituents are degraded, transformed, or immobilized.

     

    “Underground injection” means the subsurface emplacement of fluids through a bored, drilled, or driven well or through a dug well, where the depth of the dug well is greater than the largest surface dimension. (See also “injection well”.)

     

    “Underground tank” means a device meeting the definition of tank whose entire surface area is totally below the surface of and covered by the ground.

     

    “Unfit-for-use tank system” means a tank system that has been determined, through an integrity assessment or other inspection, to be no longer capable of storing or treating hazardous waste without posing a threat of release of hazardous waste to the environment.

     

    “United States” means the 50 states, the District of Columbia, the Commonwealth of Puerto Rico, the U.S. Virgin Islands, Guam, American Samoa, and the Commonwealth of the Northern Mariana Islands.

     

    “Universal waste” means any of the following hazardous wastes that are managed under the universal waste requirements of 35 Ill. Adm. Code 733:

     

    Batteries, as described in 35 Ill. Adm. Code 733.102;

     

    Pesticides, as described in 35 Ill. Adm. Code 733.103;

     

    Thermostats, as described in 35 Ill. Adm. Code 733.104; and

     

    Lamps, as described in 35 Ill. Adm. Code 733.105.

     

    “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.

     

    “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:

     

    It is part of a wastewater treatment facility that has an NPDES permit pursuant to 35 Ill. Adm. Code 309 or a pretreatment permit or authorization to discharge pursuant to 35 Ill. Adm. Code 310; and

     

    It receives and treats or stores an influent wastewater that is a hazardous waste as defined in 35 Ill. Adm. Code 721.103, or generates and accumulates a wastewater treatment sludge 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

     

    It meets the definition of tank or tank system in this Section.

     

    “Water (bulk shipment)” means the bulk transportation of hazardous waste that is loaded or carried on board a vessel without containers or labels.

     

    “Well” means any shaft or pit dug or bored into the earth, generally of a cylindrical form, and often walled with bricks or tubing to prevent the earth from caving in.

     

    “Well injection” (See “underground injection”.)

     

    “Zone of engineering control” means an area under the control of the owner or operator that, upon detection of a hazardous waste release, can be readily cleaned up prior to the release of hazardous waste or hazardous constituents to groundwater or surface water.

     

    (Source: Amended at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 720.111 References

    The following documents are incorporated by reference for the purposes of this Part and 35 Ill. Adm. Code 703 through 705, 721 through 726, 728, 730, 733, 738, and 739:

     

     
    a) Non-Regulatory Government Publications and Publications of Recognized Organizations and Associations:

    ACI. Available from the American Concrete Institute, Box 19150, Redford Station, Detroit, Michigan 48219:

     

    ACI 318-83: “Building Code Requirements for Reinforced Concrete”, adopted September 1983.

     

    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.

     

    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 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 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, PB80-208895, December 1981.

     

    “Generic Quality Assurance Project Plan for Land Disposal Restrictions Program”, EPA/530-SW-87-011, March 15, 1987 (document number PB88-170766).

     

    “Guideline on Air Quality Models”, Revised 1986 (document number PB86-245-248 (Guideline) and PB88-150-958 (Supplement), also set forth at 40 CFR 51, Appendix W).

     

    “Method 164, 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 number PB99-121949).

     

    “Methods for Chemical Analysis of Water and Wastes”, Third Edition, March 1983 (document number PB84-128677).

     

    “Methods Manual for Compliance with BIF Regulations”, December 1990 (document number PB91-120-006).

     

    “Petitions to Delist Hazardous Wastes — A Guidance Manual, Second Edition”, EPA/530-R-93-007, March 1993 (document number PB93-169 365).

     

    “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 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 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: “CO2 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).

     

    USDOD. Available from the United States Department of Defense:

     

    “DOD Ammunition and Explosives Safety Standards” (DOD 6055.9-STD), as in effect in July 1999.

     

    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 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 22202 (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).

     

    USGSA. Available from the United States Government Services Administration:

     

    Government Bill of Lading (GBL) (GSA Standard Form 1109), as in effect on November 8, 1995.

     

     
    b) Code of Federal Regulations. Available from the Superintendent of Documents, U.S. Government Printing Office, Washington, D.C. 20401, 202-783-3238:

    10 CFR 20.2006 (2001)

     

    10 CFR 20, Appendix B (2000) (2001)

     

    10 CFR 71 (2001)

     

    40 CFR 51.100(ii) (2000) (2001)

     

    40 CFR 51, Appendix W (2000) (2001)

     

    40 CFR 52.741, Appendix B (2000) (2001)

     

    40 CFR 60 (2000), as amended at 65 Fed. Reg. 42297 (July 10, 2000) (2001)

     

    40 CFR 61, Subpart V (2000) (2001)

     

    40 CFR 63 (2000) (2001), as amended at 65 Fed. Reg. 42296 (July 10, 2000) 66 Fed. Reg. 35087 (July 3, 2001), and 66 Fed. Reg. 52361 (October 15, 2001)

     

    40 CFR 136 (2000), as amended at 65 Fed. Reg. 81295 (December 22, 2000) (2001)

     

    40 CFR 142 (2000) (2001)

     

    40 CFR 220 (2000) (2001)

     

    40 CFR 232.2 (2000) (2001)

     

    40 CFR 260.20 (2000) (2001)

     

    40 CFR 264 (2000) (2001)

     

    40 CFR 268.41 (1990)

     

    40 CFR 268, Appendix IX (2000) (2001)

     

    40 CFR 270.5 (2000) (2001)

     

    40 CFR 302.4, 302.5, and 302.6 (2000) (2001)

     

    40 CFR 761 (2000) (2001)

     

    49 CFR 107 (2001)

     

    49 CFR 171 (2000) (2001)

     

    49 CFR 172 (2001)

     

    49 CFR 173 (2000) (2001)

     

    49 CFR 178 (2000) (2001)

     

    49 CFR 179 (2001)

     

     
    c) Federal Statutes

    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 26 Ill. Reg. ________, effective ______________________)

     

     

    TITLE 35: ENVIRONMENTAL PROTECTION

    SUBTITLE G: WASTE DISPOSAL

    CHAPTER I: POLLUTION CONTROL BOARD

    SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS

     

    PART 721

    IDENTIFICATION AND LISTING OF HAZARDOUS WASTE

     

    SUBPART A: GENERAL PROVISIONS

    Section

     
    721.101 Purpose and Scope
    721.102 Definition of Solid Waste
    721.103 Definition of Hazardous Waste
    721.104 Exclusions
    721.105 Special Requirements for Hazardous Waste Generated by Small Quantity Generators
    721.106 Requirements for Recyclable Materials
    721.107 Residues of Hazardous Waste in Empty Containers
    721.108 PCB Wastes Regulated under TSCA
    721.109 Requirements for Universal Waste

    SUBPART B: CRITERIA FOR IDENTIFYING THE CHARACTERISTICS OF HAZARDOUS WASTE AND FOR LISTING HAZARDOUS WASTES

    Section

     
    721.110 Criteria for Identifying the Characteristics of Hazardous Waste
    721.111 Criteria for Listing Hazardous Waste

    SUBPART C: CHARACTERISTICS OF HAZARDOUS WASTE

    Section

     
    721.120 General
    721.121 Characteristic of Ignitability
    721.122 Characteristic of Corrosivity
    721.123 Characteristic of Reactivity
    721.124 Toxicity Characteristic

    SUBPART D: LISTS OF HAZARDOUS WASTE

    Section

     
    721.130 General
    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 at 5 Ill. Reg. 9781, effective May 17, 1982; amended and codified in R81-22 at 6 Ill. Reg. 4828, effective May 17, 1982; amended in R82-18 at 7 Ill. Reg. 2518, effective February 22, 1983; amended in R82-19 at 7 Ill. Reg. 13999, effective October 12, 1983; amended in R84-34, 61 at 8 Ill. Reg. 24562, effective December 11, 1984; amended in R84-9 at 9 Ill. Reg. 11834, effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 998, effective January 2, 1986; amended in R85-2 at 10 Ill. Reg. 8112, effective May 2, 1986; amended in R86-1 at 10 Ill. Reg. 14002, effective August 12, 1986; amended in R86-19 at 10 Ill. Reg. 20647, effective December 2, 1986; amended in R86-28 at 11 Ill. Reg. 6035, effective March 24, 1987; amended in R86-46 at 11 Ill. Reg. 13466, effective August 4, 1987; amended in R87-32 at 11 Ill. Reg. 16698, effective September 30, 1987; amended in R87-5 at 11 Ill. Reg. 19303, effective November 12, 1987; amended in R87-26 at 12 Ill. Reg. 2456, effective January 15, 1988; amended in R87-30 at 12 Ill. Reg. 12070, effective July 12, 1988; amended in R87-39 at 12 Ill. Reg. 13006, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 382, effective December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18300, effective November 13, 1989; amended in R90-2 at 14 Ill. Reg. 14401, effective August 22, 1990; amended in R90-10 at 14 Ill. Reg. 16472, effective September 25, 1990; amended in R90-17 at 15 Ill. Reg. 7950, effective May 9, 1991; amended in R90-11 at 15 Ill. Reg. 9332, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14473, effective September 30, 1991; amended in R91-12 at 16 Ill. Reg. 2155, effective January 27, 1992; amended in R91-26 at 16 Ill. Reg. 2600, effective February 3, 1992; amended in R91-13 at 16 Ill. Reg. 9519, effective June 9, 1992; amended in R92-1 at 16 Ill. Reg. 17666, effective November 6, 1992; amended in R92-10 at 17 Ill. Reg. 5650, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20568, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6741, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12175, effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17490, effective November 23, 1994; amended in R95-6 at 19 Ill. Reg. 9522, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 10963, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 275, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7615, effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17531, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1718, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9135, effective July 26, 1999; amended in R00-13 at 24 Ill. Reg. 9481, effective June 20, 2000; amended in R01-3 at 25 Ill. Reg. 1281, effective January 11, 2001; amended in R01-21/R01-23 at 25 Ill. Reg. 9108, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. ________, effective ______________________.

     

     

    SUBPART A: GENERAL PROVISIONS

     

     
    Section 721.102 Definition of Solid Waste
     
    a) Solid waste.
      
    1) A solid waste is any discarded material that is not excluded by Section 721.104(a) or that is not excluded pursuant to 35 Ill. Adm. Code 720.130 and 720.131.
    2) A discarded material is any material that is:
        
    A) Abandoned, as explained in subsection (b) of this Section;
    B) Recycled, as explained in subsection (c) of this Section;
    C) Considered inherently waste-like, as explained in subsection (d) of this Section; or
    D) A military munition identified as a solid waste in 35 Ill. Adm. Code 726.302.
     
    b) Materials are solid waste if they are abandoned by being:
       
    1) Disposed of; or
    2) Burned or incinerated; or
    3) Accumulated, stored or treated (but not recycled) before or in lieu of being abandoned by being disposed of, burned or incinerated.
     
    c) Materials are solid wastes if they are recycled--or accumulated, stored or treated before recycling--as specified in subsections (c)(1) through (c)(4) of this Section if they are:
     
    1) Used in a manner constituting disposal.
     
    A) Materials noted with a “yes” in column 1 of the table in Appendix Z of this Part are solid wastes when they are:
      
    i) Applied to or placed on the land in a manner that constitutes disposal; or
    ii) Used to produce products that are applied to or placed on the land or are otherwise contained in products that are applied to or placed on the land (in which cases the product itself remains a solid waste).
     
    B) However, commercial chemical products listed in Section 721.133 are not solid wastes if they are applied to the land and that is their ordinary manner of use.
     
    2) Burned for energy recovery.
     
    A) Materials noted with a “yes” in column 2 of the table in Appendix Z of this Part are solid wastes when they are:
       
    i) Burned to recover energy;
    ii) Used to produce a fuel or are otherwise contained in fuels (in which case the fuel itself remains a solid waste);
    iii) Contained in fuels (in which case the fuel itself remains a solid waste).
     
    B) However, commercial chemical products listed in Section 721.133 are not solid wastes if they are themselves fuels.
      
    3) Reclaimed. Materials noted with a “yes” in column 3 of the table in Appendix Z of this Part are solid wastes when reclaimed (except as provided under Section 721.104(a)(17)). Materials noted with a “--” in column 3 of Appendix Z of this Part are not solid wastes when reclaimed (except as provided under Section 721.104(a)(17)).
    4) Accumulated speculatively. Materials noted with “yes” in column 4 of the table in Appendix Z of this Part are solid wastes when accumulated speculatively.
     
    d) Inherently waste-like materials. The following materials are solid wastes when they are recycled in any manner:
      
    1) Hazardous waste numbers F020, F021 (unless used as an ingredient to make a product at the site of generation), F022, F023, F026, and F028.
    2) Secondary materials fed to a halogen acid furnace that exhibit a characteristic of a hazardous waste or are listed as a hazardous waste as defined in Subpart C or D of this Part, except for brominated material that meets the following criteria:
       
    A) The material must contain a bromine concentration of at least 45 percent;
    B) The material must contain less than a total of one percent of toxic organic compounds listed in Appendix H of this Part; and
    C) The material is processed continually on-site in the halogen acid furnace via direct conveyance (hard piping).
     
    3) The following criteria are used to add wastes to the list:
     
    A) Disposal method or toxicity.
      
    i) The materials are ordinarily disposed of, burned, or incinerated; or
    ii) The materials contain toxic constituents listed in Appendix H of this Part and these constituents are not ordinarily found in raw materials or products for which the materials substitute (or are found in raw materials or products in smaller concentrations) and are not used or reused during the recycling process; and
     
    B) The material may pose a substantial hazard to human health and the environment when recycled.
     
    e) Materials that are not solid waste when recycled.
     
    1) Materials are not solid wastes when they can be shown to be recycled by being:
       
    A) Used or reused as ingredients in an industrial process to make a product, provided the materials are not being reclaimed; or
    B) Used or reused as effective substitutes for commercial products; or
    C) Returned to the original process from which they are generated, without first being reclaimed or land disposed. The material must be returned as a substitute for feedstock materials. In cases where the original process to which the material is returned is a secondary process, the materials must be managed in such a manner that there is no placement on the land. In cases where thematerials the materials are generated and reclaimed within the primary mineral processing industry, the conditions of the exclusion found at Section 721.104(a)(17) apply rather than this provision.
     
    2) The following materials are solid wastes, even if the recycling involves use, reuse, or return to the original process (described in subsections (e)(1)(A) through (e)(1)(C) of this Section):
        
    A) Materials used in a manner constituting disposal or used to produce products that are applied to the land; or
    B) Materials burned for energy recovery, used to produce a fuel, or contained in fuels; or
    C) Materials accumulated speculatively; or
    D) Materials listed in subsections (d)(1) and (d)(2) of this Section.
     
    f) Documentation of claims that materials are not solid wastes or are conditionally exempt from regulation. Respondents in actions to enforce regulations implementing Subtitle C of RCRA or Section 21 of the Environmental Protection Act that raise a claim that a certain material is not a solid waste or that the material is conditionally exempt from regulation must demonstrate that there is a known market or disposition for the material and that they meet the terms of the exclusion or exemption. In doing so, the person must provide appropriate documentation (such as contracts showing that a second person uses the material as an ingredient in a production process) to demonstrate that the material is not a waste or that the material is exempt from regulation. In addition, owners or operators of facilities claiming that they actually are recycling materials must show that they have the necessary equipment to do so.

    (Source: Amended at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 721.103 Definition of Hazardous Waste
     
    a) A solid waste, as defined in Section 721.102, is a hazardous waste if:
      
    1) It is not excluded from regulation as a hazardous waste under Section 721.104(b); and
    2) It meets any of the following criteria:
        
    A) It exhibits any of the characteristics of hazardous waste identified in Subpart C of this Part. However, any mixture of a waste from the extraction, beneficiation, and processing of ores and minerals excluded under Section 721.104(b)(7) and any other solid waste exhibiting a characteristic of hazardous waste under Subpart C of this Part is a hazardous waste only if it exhibits a characteristic that would not have been exhibited by the excluded waste alone if such mixture had not occurred, or if the mixture continues to exhibit any of the characteristics exhibited by the non-excluded wastes prior to mixture. Further, for the purposes of applying the toxicity characteristic to such mixtures, the mixture is also a hazardous waste if it exceeds the maximum concentration for any contaminant listed in Section 721.124 that would not have been exceeded by the excluded waste alone if the mixture had not occurred or if it continues to exceed the maximum concentration for any contaminant exceeded by the nonexempt waste prior to mixture.
    B) It is listed in Subpart D of this Part and has not been excluded from the lists in Subpart D of this Part under 35 Ill. Adm. Code 720.120 and 720.122.
    C) It is a mixture of a solid waste and a hazardous waste that is listed in Subpart D of this Part solely because it exhibits one or more of the characteristics of hazardous waste identified in Subpart C of this Part, unless the resultant mixture no longer exhibits any characteristic of hazardous waste identified in Subpart C of this Part, or unless the solid waste is excluded from regulation under Section 721.104(b)(7) and the resultant mixture no longer exhibits any characteristic of hazardous waste identified in Subpart C of this Part for which the hazardous waste listed in Subpart D of this Part was listed. (However, nonwastewater mixtures are still subject to the requirements of 35 Ill. Adm. Code 728, even if they no longer exhibit a characteristic at the point of land disposal.)This subsection corresponds with 40 CFR 261.3(a)(2)(iii), which USEPA removed and marked as “reserved” at 66 Fed. Reg. 27266 (May 16, 2001). This statement maintains structural consistency with the federal regulations.
    D) It is a mixture of solid waste and one or more hazardous wastes listed in Subpart D of this Part and has not been excluded from this subsection (a)(2) under 35 Ill. Adm. Code 720.120 and 720.122, subsection (g) of this Section, or subsection (h) of this Section; however, the following mixtures of solid wastes and hazardous wastes listed in Subpart D of this Part are not hazardous wastes (except by application of subsection (a)(2)(A) or (a)(2)(B) of this Section) if the generator demonstrates that the mixture consists of wastewater the discharge of which is subject to regulation under either 35 Ill. Adm. Code 309 or 310 (including wastewater at facilities that have eliminated the discharge of wastewater) and:
           
    i) One or more of the following solvents listed in Section 721.131: carbon tetrachloride, tetrachloroethylene, trichloroethylene, provided that the maximum total weekly usage of these solvents (other than the amounts that can be demonstrated not to be discharged to wastewater) divided by the average weekly flow of wastewater into the headworks of the facility’s wastewater treatment or pretreatment system does not exceed 1 part per million;
    ii) One or more of the following spent solvents listed in Section 721.131: methylene chloride, 1,1,1-trichloroethane, chlorobenzene, o-dichlorobenzene, cresols, cresylic acid, nitrobenzene, toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, spent chlorofluorocarbon solvents, provided that the maximum total weekly usage of these solvents (other than the amounts that can be demonstrated not to be discharged to wastewater) divided by the average weekly flow of wastewater into the headworks of the facility’s wastewater treatment or pretreatment system does not exceed 25 parts per million;
    iii) One of the following wastes listed in Section 721.132, provided that the wastes are discharged to the refinery oil recovery sewer before primary oil/water/solids separation: heat exchanger bundle cleaning sludge from the petroleum refining industry (USEPA hazardous waste no. K050), crude oil storage tank sediment from petroleum refining operations (USEPA hazardous waste number K169), clarified slurry oil tank sediment and/or in-line filter/separation solids from petroleum refining operations (USEPA hazardous waste number K170), spent hydrotreating catalyst (USEPA hazardous waste number K171), and spent hydrorefining catalyst (USEPA hazardous waste number K172);
    iv) A discarded commercial chemical product or chemical intermediate listed in Section 721.133 arising from de minimis losses of these materials from manufacturing operations in which these materials are used as raw materials or are produced in the manufacturing process. For purposes of this subsection, “de minimis” losses include those from normal material handling operations (e.g., spills from the unloading or transfer of materials from bins or other containers, leaks from pipes, valves, or other devices used to transfer materials); minor leaks of process equipment, storage tanks, or containers; leaks from well-maintained pump packings and seals; sample purgings; relief device discharges; discharges from safety showers and rinsing and cleaning of personal safety equipment; and rinsate from empty containers or from containers that are rendered empty by that rinsing;
    v) Wastewater resulting from laboratory operations containing toxic (T) wastes listed in Subpart D of this Part, provided that the annualized average flow of laboratory wastewater does not exceed one percent of total wastewater flow into the headworks of the facility’s wastewater treatment or pretreatment system or provided that the wastes’ combined annualized average concentration does not exceed one part per million in the headworks of the facility’s wastewater treatment or pretreatment facility. Toxic (T) wastes used in laboratories that are demonstrated not to be discharged to wastewater are not to be included in this calculation;
    vi) One or more of the following wastes listed in Section 721.132: wastewaters from the production of carbamates and carbamoyl oximes (USEPA Hazardous Waste No. K157), provided that the maximum weekly usage of formaldehyde, methyl chloride, methylene chloride, and triethylamine (including all amounts that cannot be demonstrated to be reacted in the process, destroyed through treatment, or recovered, i.e., what is discharged or volatilized) divided by the average weekly flow of process wastewater prior to any dilutions into the headworks of the facility’s wastewater treatment system does not exceed a total of 5 parts per million by weight; or
    vii) Wastewaters derived from the treatment of one or more of the following wastes listed in Section 721.132: organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes (USEPA Hazardous Waste No. K156), provided, that the maximum concentration of formaldehyde, methyl chloride, methylene chloride, and triethylamine prior to any dilutions into the headworks of the facility’s wastewater treatment system does not exceed a total of 5 milligrams per liter.
     
    E) Rebuttable presumption for used oil. Used oil containing more than 1,000 ppm total halogens is presumed to be a hazardous waste because it has been mixed with halogenated hazardous waste listed in Subpart D of this Part. Persons may rebut this presumption by demonstrating that the used oil does not contain hazardous waste (for example, by using an analytical method from SW-846, incorporated by reference at 35 Ill. Adm. Code 720.111, to show that the used oil does not contain significant concentrations of halogenated hazardous constituents listed in Appendix H of this Part).
      
    i) The rebuttable presumption does not apply to metalworking oils or fluids containing chlorinated paraffins if they are processed through a tolling arrangement as described in 35 Ill. Adm. Code 739.124(c) to reclaim metalworking oils or fluids. The presumption does apply to metalworking oils or fluids if such oils or fluids are recycled in any other manner, or disposed.
    ii) The rebuttable presumption does not apply to used oils contaminated with chlorofluorocarbons (CFCs) removed from refrigeration units where the CFCs are destined for reclamation. The rebuttable presumption does apply to used oils contaminated with CFCs that have been mixed with used oil from sources other than refrigeration units.
     
    b) A solid waste that is not excluded from regulation under subsection (a)(1) of this Section becomes a hazardous waste when any of the following events occur:
       
    1) In the case of a waste listed in Subpart D of this Part, when the waste first meets the listing description set forth in Subpart D of this Part.
    2) In the case of a mixture of solid waste and one or more listed hazardous wastes, when a hazardous waste listed in Subpart D of this Part is first added to the solid waste.
    3) In the case of any other waste (including a waste mixture), when the waste exhibits any of the characteristics identified in Subpart C of this Part.
     
    c) Unless and until it meets the criteria of subsection (d) of this Section, a hazardous waste will remain a hazardous waste.

    BOARD NOTE: This subsection corresponds with 40 CFR 261.3(c)(1). The Board has codified 40 CFR 261.3(c)(2) at subsection (e) of this Section.

     

     
    d) Any solid waste described in subsection (c) of this Section is not a hazardous waste if it meets the following criteria:
      
    1) In the case of any solid waste, it does not exhibit any of the characteristics of hazardous waste identified in Subpart C of this Part. (However, wastes that exhibit a characteristic at the point of generation may still be subject to the requirements of 35 Ill. Adm. Code 728, even if they no longer exhibit a characteristic at the point of land disposal.)
    2) In the case of a waste that is a listed waste under Subpart D of this Part, a waste that contains a waste listed under Subpart D of this Part, or a waste that is derived from a waste listed in Subpart D of this Part, it also has been excluded from subsection (c) of this Section under 35 Ill. Adm. Code 720.120 and 720.122.
     
    e) Specific inclusions and exclusions.
      
    1) Except as otherwise provided in subsection (e)(2), (g), or (h) of this Section, any solid waste generated from the treatment, storage, or disposal of a hazardous waste, including any sludge, spill residue, ash, emission control dust, or leachate (but not including precipitation run-off), is a hazardous waste. (However, materials that are reclaimed from solid wastes and that are used beneficially are not solid wastes and hence are not hazardous wastes under this provision unless the reclaimed material is burned for energy recovery or used in a manner constituting disposal.)
    2) The following solid wastes are not hazardous even though they are generated from the treatment, storage, or disposal of a hazardous waste unless they exhibit one or more of the characteristics of hazardous waste:
       
    A) Waste pickle liquor sludge generated by lime stabilization of spent pickle liquor from the iron and steel industry (SIC Codes 331 and 332).
    B) Wastes from burning any of the materials exempted from regulation by Section 721.106(a)(3)(C) and (a)(3)(D).
    C) Nonwastewater residues, such as slag, resulting from high temperature metal recovery (HTMR) processing of K061, K062, or F006 waste in the units identified in this subsection that are disposed of in non-hazardous waste units, provided that these residues meet the generic exclusion levels identified in the tables in this subsection for all constituents and the residues exhibit no characteristics of hazardous waste. The types of units identified are rotary kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors, rotary hearth furnace/electric furnace combinations, or the following types of industrial furnaces (as defined in 35 Ill. Adm. Code 720.110): blast furnaces, smelting, melting and refining furnaces (including pyrometallurgical devices such as cupolas, reverberator furnaces, sintering machines, roasters, and foundry furnaces), and other furnaces designated by the Agency pursuant to that definition.
      
    i) Testing requirements must be incorporated in a facility’s waste analysis plan or a generator’s self-implementing waste analysis plan; at a minimum, composite samples of residues must be collected and analyzed quarterly and when the process or operation generating the waste changes.
    ii) Persons claiming this exclusion in an enforcement action will have the burden of proving by clear and convincing evidence that the material meets all of the exclusion requirements. The generic exclusion levels are:

    Constituent

    Maximum for any single composite sample (mg/L)

      
    Generic exclusion levels for K061 and K062 nonwastewater HTMR residues.

    Antimony

    0.10

    Arsenic

    0.50

    Barium

    7.6

    Beryllium

    0.010

    Cadmium

    0.050

    Chromium (total)

    0.33

    Lead

    0.15

    Mercury

    0.009

    Nickel

    1.0

    Selenium

    0.16

    Silver

    0.30

    Thallium

    0.020

    Vanadium

    1.26

    Zinc

    70

      
    Generic exclusion levels for F006 nonwastewater HTMR residues

    Antimony

    0.10

    Arsenic

    0.50

    Barium

    7.6

    Beryllium

    0.010

    Cadmium

    0.050

    Chromium (total)

    0.33

    Cyanide (total) (mg/kg)

    1.8

    Lead

    0.15

    Mercury

    0.009

    Nickel

    1.0

    Selenium

    0.16

    Silver

    0.30

    Thallium

    0.020

    Zinc

    70

     
     
    iii) A one-time notification and certification must be placed in the facility’s files and sent to the Agency (or, for out-of-State shipments, to the appropriate Regional Administrator of USEPA or the state agency authorized to implement 40 CFR 268 requirements) for K061, K062, or F006 HTMR residues that meet the generic exclusion levels for all constituents and do not exhibit any characteristics and which are sent to RCRA Subtitle D (municipal solid waste landfill) units. The notification and certification that is placed in the generator’s or treater’s files must be updated if the process or operation generating the waste changes or if the RCRA Subtitle D unit receiving the waste changes. However, the generator or treater need only notify the Agency on an annual basis if such changes occur. Such notification and certification should be sent to the Agency by the end of the calendar year, but no later than December 31. The notification must include the following information: the name and address of the nonhazardous waste management unit receiving the waste shipment; the USEPA hazardous waste number and treatability group at the initial point of generation; and the treatment standards applicable to the waste at the initial point of generation. The certification must be signed by an authorized representative and must state as follows:

    “I certify under penalty of law that the generic exclusion levels for all constituents have been met without impermissible dilution and that no characteristic of hazardous waste is exhibited. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.”

     

      
    D) Biological treatment sludge from the treatment of one of the following wastes listed in Section 721.132: organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes (USEPA Hazardous Waste No. K156) and wastewaters from the production of carbamates and carbamoyl oximes (USEPA Hazardous Waste No. K157).
    E) Catalyst inert support media separated from one of the following wastes listed in Section 721.132: spent hydrotreating catalyst (USEPA hazardous waste number K171) and spent hydrorefining catalyst (USEPA hazardous waste number K172).

    BOARD NOTE: This subsection would normally correspond with 40 CFR 261.3(e), a subsection which has been deleted and marked “reserved” by USEPA. Rather, this subsection (e) corresponds with 40 CFR 261.3(c)(2), which the Board codified here to comport with codification requirements and to enhance clarity.

     

     
    f) Notwithstanding subsections (a) through (e) of this Section and provided the debris, as defined in 35 Ill. Adm. Code 728.102, does not exhibit a characteristic identified at Subpart C of this Part, the following materials are not subject to regulation under 35 Ill. Adm. Code 720, 721 to 726, 728, or 730:
      
    1) Hazardous debris as defined in 35 Ill. Adm. Code 728.102 that has been treated using one of the required extraction or destruction technologies specified in 35 Ill. Adm. Code 728.Table F; persons claiming this exclusion in an enforcement action will have the burden of proving by clear and convincing evidence that the material meets all of the exclusion requirements; or
    2) Debris as defined in 35 Ill. Adm. Code 728.102 that the Agency, considering the extent of contamination, has determined is no longer contaminated with hazardous waste.
     
    g) Exclusion of certain wastes listed in Subpart D solely because they exhibit a characteristic of ignitability, corrosivity, or reactivity.
      
    1) A hazardous waste that is listed in Subpart D of this Part solely because it exhibits one or more characteristics of ignitability, as defined under Section 721.121; corrosivity, as defined under Section 721.122; or reactivity, as defined under Section 721.123 is not a hazardous waste if the waste no longer exhibits any characteristic of hazardous waste identified in Subpart C of this Part.
    2) The exclusion described in subsection (g)(1) of this Section also pertains to the following:
      
    A) Any mixture of a solid waste and a hazardous waste listed in Subpart D of this Part solely because it exhibits the characteristics of ignitability, corrosivity, or reactivity, as regulated under subsection (a)(2)(D) of this Section; and
    B) Any solid waste generated from treating, storing, or disposing of a hazardous waste listed in Subpart D of this Part solely because it exhibits the characteristics of ignitability, corrosivity, or reactivity as regulated under subsection (e)(1) of this Section.
     
    3) Wastes excluded under this subection (g) are subject to 35 Ill. Adm. Code 728 (as applicable), even if they no longer exhibit a characteristic at the point of land disposal.
     
    h) Eligible radioactive mixed waste.
      
    1) Hazardous waste containing radioactive waste is no longer a hazardous waste when it meets the eligibility criteria and conditions of 35 Ill. Adm. Code 726.Subpart N (i.e., it is “eligible radioactive mixed waste”).
    2) The exemption described in subsection (h)(1) of this Section also pertains to the following:
      
    A) Any mixture of a solid waste and an eligible radioactive mixed waste; and
    B) Any solid waste generated from treating, storing, or disposing of an eligible radioactive mixed waste.
     
    3) Waste exempted under this subsection (h) must meet the eligibility criteria and specified conditions in 35 Ill. Adm. Code 726.325 and 726.330 (for storage and treatment) and in 35 Ill. Adm. Code 726.410 and 726.415 (for transportation and disposal). Waste that fails to satisfy these eligibility criteria and conditions is regulated as hazardous waste.

    (Source: Amended at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 721.104 Exclusions
     
    a) Materials that are not solid wastes. The following materials are not solid wastes for the purpose of this Part:
     
    1) Sewage:
      
    A) Domestic sewage (untreated sanitary wastes that pass through a sewer system); and
    B) Any mixture of domestic sewage and other waste that passes through a sewer system to publicly-owned treatment works for treatment.
     
    2) Industrial wastewater discharges that are point source discharges with National Pollutant Discharge Elimination System (NPDES) permits issued by the Agency pursuant to Section 12(f) of the Environmental Protection Act and 35 Ill. Adm. Code 309.

    BOARD NOTE: This exclusion applies only to the actual point source discharge. It does not exclude industrial wastewaters while they are being collected, stored, or treated before discharge, nor does it exclude sludges that are generated by industrial wastewater treatment.

     

          
    3) Irrigation return flows.
    4) Source, special nuclear, or by-product, or special nuclear material as defined by the Atomic Energy Act of 1954, as amended (42 USC 2011 et seq.).
    5) Materials subjected to in-situ mining techniques that are not removed from the ground as part of the extraction process.
    6) Pulping liquors (i.e., black liquors) that are reclaimed in a pulping liquor recovery furnace and then reused in the pulping process, unless accumulated speculatively, as defined in Section 721.101(c).
    7) Spent sulfuric acid used to produce virgin sulfuric acid unless it is accumulated speculatively, as defined in Section 721.101(c).
    8) Secondary materials that are reclaimed and returned to the original process or processes in which they were generated where they are reused in the production process, provided:
        
    A) Only tank storage is involved, and the entire process through completion of reclamation is closed by being entirely connected with pipes or other comparable enclosed means of conveyance;
    B) Reclamation does not involve controlled flame combustion (such as occurs in boilers, industrial furnaces, or incinerators);
    C) The secondary materials are never accumulated in such tanks for over twelve months without being reclaimed; and
    D) The reclaimed material is not used to produce a fuel or used to produce products that are used in a manner constituting disposal.
     
    9) Wood preserving wastes.
       
    A) Spent wood preserving solutions that have been used and which are reclaimed and reused for their original intended purpose;
    B) Wastewaters from the wood preserving process that have been reclaimed and which are reused to treat wood; and
    C) Prior to reuse, the wood preserving wastewaters and spent wood preserving solutions described in subsections (a)(9)(A) and (a)(9)(B) of this Section, so long as they meet all of the following conditions:
         
    i) The wood preserving wastewaters and spent wood preserving solutions are reused on-site at water borne plants in the production process for their original intended purpose;
    ii) Prior to reuse, the wastewaters and spent wood preserving solutions are managed to prevent release to either land or groundwater or both;
    iii) Any unit used to manage wastewaters or spent wood preserving solutions prior to reuse can be visually or otherwise determined to prevent such releases;
    iv) Any drip pad used to manage the wastewaters or spent wood preserving solutions prior to reuse complies with the standards in 35 Ill. Adm. Code 725.Subpart W, regardless of whether the plant generates a total of less than 100 kg/month of hazardous waste; and
    v) Prior to operating pursuant to this exclusion, the plant owner or operator submits a one-time notification to the Agency stating that the plant intends to claim the exclusion, giving the date on which the plant intends to begin operating under the exclusion, and containing the following language: “I have read the applicable regulation establishing an exclusion for wood preserving wastewaters and spent wood preserving solutions and understand it requires me to comply at all times with the conditions set out in the regulation.” The plant must maintain a copy of that document in its on-site records for a period of no less than three years from the date specified in the notice. The exclusion applies only so long as the plant meets all of the conditions. If the plant goes out of compliance with any condition, it may apply to the Agency for reinstatement. The Agency shall must reinstate the exclusion in writing if it finds that the plant has returned to compliance with all conditions and that violations are not likely to recur. If the Agency denies an application, it shall must transmit to the applicant specific, detailed statements in writing as to the reasons it denied the application. The applicant under this subsection (a)(9)(C)(v) may appeal the Agency’s determination to deny the reinstatement, to grant the reinstatement with conditions, or to terminate a reinstatement before the Board pursuant to Section 40 of the Act [415 ILCS 5/40].
       
    10) Hazardous waste numbers K060, K087, K141, K142, K143, K144, K145, K147, and K148, and any wastes from the coke by-products processes that are hazardous only because they exhibit the toxicity characteristic specified in Section 721.124, when subsequent to generation these materials are recycled to coke ovens, to the tar recovery process as a feedstock to produce coal tar, or are mixed with coal tar prior to the tar’s sale or refining. This exclusion is conditioned on there being no land disposal of the waste from the point it is generated to the point it is recycled to coke ovens, to tar recovery, to the tar refining processes, or prior to when it is mixed with coal.
    11) Nonwastewater splash condenser dross residue from the treatment of hazardous waste number K061 in high temperature metals recovery units, provided it is shipped in drums (if shipped) and not land disposed before recovery.
    12) Certain oil-bearing hazardous secondary materials and recovered oil, as follows:
      
    A) Oil-bearing hazardous secondary materials (i.e., sludges, byproducts by-products, or spent materials) that are generated at a petroleum refinery (standard industrial classification (SIC code 2911) and are inserted into the petroleum refining process (SIC code 2911: including, but not limited to, distillation, catalytic cracking, fractionation, or thermal cracking units (i.e., cokers)) unless the material is placed on the land, or speculatively accumulated before being so recycled. Materials inserted into thermal cracking units are excluded under this subsection (a)(12), provided that the coke product also does not exhibit a characteristic of hazardous waste. Oil-bearing hazardous secondary materials may be inserted into the same petroleum refinery where they are generated or sent directly to another petroleum refinery and still be excluded under this provision. Except as provided in subsection (a)(12)(B) of this Section, oil-bearing hazardous secondary materials generated elsewhere in the petroleum industry (i.e., from sources other than petroleum refineries) are not excluded under this section. Residuals generated from processing or recycling materials excluded under this subsection (a)(12)(A), where such materials as generated would have otherwise met a listing under Subpart D of this Part, are designated as USEPA hazardous waste number F037 listed wastes when disposed of or intended for disposal.
    B) Recovered oil that is recycled in the same manner and with the same conditions as described in subsection (a)(12)(A) of this Section. Recovered oil is oil that has been reclaimed from secondary materials (including wastewater) generated from normal petroleum industry practices, including refining, exploration and production, bulk storage, and transportation incident thereto (SIC codes 1311, 1321, 1381, 1382, 1389, 2911, 4612, 4613, 4922, 4923, 4789, 5171, and 5172). Recovered oil does not include oil-bearing hazardous wastes listed in Subpart D of this Part; however, oil recovered from such wastes may be considered recovered oil. Recovered oil does not include used oil, as defined in 35 Ill. Adm. Code 739.100.
      
    13) Excluded scrap metal (processed scrap metal, unprocessed home scrap metal, and unprocessed prompt scrap metal) being recycled.
    14) Shredded circuit boards being recycled, provided that they meet the following conditions:
      
    A) The circuit boards are stored in containers sufficient to prevent a release to the environment prior to recovery; and
    B) The circuit boards are free of mercury switches, mercury relays, and nickel-cadmium batteries and lithium batteries.
       
    15) Condensates derived from the overhead gases from kraft mill steam strippers that are used to comply with federal Clean Air Act regulation 40 CFR 63.446(e). The exemption applies only to combustion at the mill generating the condensates.
    16) Comparable fuels or comparable syngas fuels (i.e., comparable or syngas fuels) that meet the requirements of Section 721.138.
    17) Secondary Spent materials (i.e., sludges, by-products, and spent materials as defined in Section 721.101) (other than hazardous wastes listed in Subpart D of this Part) generated within the primary mineral processing industry from which minerals, acids, cyanide, water, or other values are recovered by mineral processing or by benefication, provided that:
        
    A) The secondary spent material is legitimately recycled to recover minerals, acids, cyanide, water, or other values;
    B) The secondary spent material is not accumulated speculatively;
    C) Except as provided in subsection (a)(16)(D) (a)(17)(D) of this Section, the secondary spent material is stored in tanks, containers, or buildings that meet the following minimum integrity standards: a building must be an engineered structure with a floor, walls, and a roof all of which are made of non-earthen materials providing structural support (except that smelter buildings may have partially earthen floors, provided that the secondary spent material is stored on the non-earthen portion), and have a roof suitable for diverting rainwater away from the foundation; a tank must be free standing, not be a surface impoundment (as defined in 35 Ill. Adm. Code 720.110), and be manufactured of a material suitable for containment of its contents; a container must be free standing and be manufactured of a material suitable for containment of its contents. If a tank or container contains any particulate which may be subject to wind dispersal, the owner or operator must operate the unit in a manner that controls fugitive dust. A tank, container, or building must be designed, constructed, and operated to prevent significant releases to the environment of these materials.
    D) The Agency shall must allow by permit that solid mineral processing secondary spent materials only may be placed on pads, rather than in tanks, containers, or buildings if the facility owner or operator can demonstrate the following: the solid mineral processing secondary materials do not contain any free liquid; the pads are designed, constructed, and operated to prevent significant releases of the secondary spent material into the environment; and the pads provide the same degree of containment afforded by the non-RCRA tanks, containers, and buildings eligible for exclusion.
       
    i) The Agency shall must also consider whether storage on pads poses the potential for significant releases via groundwater, surface water, and air exposure pathways. Factors to be considered for assessing the groundwater, surface water, and air exposure pathways must include the following: the volume and physical and chemical properties of the secondary spent material, including its potential for migration off the pad; the potential for human or environmental exposure to hazardous constituents migrating from the pad via each exposure pathway; and the possibility and extent of harm to human and environmental receptors via each exposure pathway.
    ii) Pads must meet the following minimum standards: they must be designed of non-earthen material that is compatible with the chemical nature of the mineral processing secondary spent material; they must be capable of withstanding physical stresses associated with placement and removal; they must have runon and runoff controls; they must be operated in a manner which controls fugitive dust; and they must have integrity assurance through inspections and maintenance programs.
    iii) Before making a determination under this subsection (a)(16)(D) (a)(17)(D), the Agency shall must provide notice and the opportunity for comment to all persons potentially interested in the determination. This can be accomplished by placing notice of this action in major local newspapers, or broadcasting notice over local radio stations.

    BOARD NOTE: See 35 Ill. Adm. Code 703.Subpart D for the RCRA Subtitle C permit public notice requirements.

     

      
    E) The owner or operator provides a notice to the Agency, identifying providing the following information: the types of materials to be recycled, the type and location of the storage units and recycling processes, and the annual quantities expected to be placed in non-land-based units. This notification must be updated when there is a change in the type of materials recycled or the location of the recycling process.
    F) For purposes of subsection (b)(7) of this Section, mineral processing secondary spent materials must be the result of mineral processing and may not include any listed hazardous wastes. Listed hazardous wastes and characteristic hazardous wastes generated by non-mineral processing industries are not eligible for the conditional exclusion from the definition of solid waste.
     
    18) Petrochemical recovered oil from an associated organic chemical manufacturing facility, where the oil is to be inserted into the petroleum refining process (SIC code 2911) along with normal petroleum refinery process streams, provided that both of the following conditions are true of the oil:
      
    A) The oil is hazardous only because it exhibits the characteristic of ignitability (as defined in Section 721.121) or toxicity for benzene (Section 721.124, USEPA hazardous waste code D018);
    B) The oil generated by the organic chemical manufacturing facility is not placed on the land, or speculatively accumulated before being recycled into the petroleum refining process. An “associated organic chemical manufacturing facility” is a facility for which all of the following is true: its primary SIC code is 2869, but its operations may also include SIC codes 2821, 2822, and 2865; it is physically co-located with a petroleum refinery; and the petroleum refinery to which the oil being recycled is returned also provides hydrocarbon feedstocks to the organic chemical manufacturing facility. “Petrochemical recovered oil” is oil that has been reclaimed from secondary materials (i.e., sludges, byproducts by-products, or spent materials, including wastewater) from normal organic chemical manufacturing operations, as well as oil recovered from organic chemical manufacturing processes.
     
    19) Spent caustic solutions from petroleum refining liquid treating processes used as a feedstock to produce cresylic or naphthenic acid unless the material is placed on the land, or accumulated speculatively as defined in Section 721.101(c).
     
    b) Solid wastes that are not hazardous wastes. The following solid wastes are not hazardous wastes:
     
    1) Household waste, including household waste that has been collected, transported, stored, treated, disposed, recovered (e.g., refuse-derived fuel), or reused. “Household waste” means any waste material (including garbage, trash, and sanitary wastes in septic tanks) derived from households (including single and multiple residences, hotels, and motels, bunkhouses, ranger stations, crew quarters, campgrounds, picnic grounds, and day-use recreation areas). A resource recovery facility managing municipal solid waste shall must not be deemed to be treating, storing, disposing of, or otherwise managing hazardous wastes for the purposes of regulation under this Part, if such facility:
     
    A) Receives and burns only:
      
    i) Household waste (from single and multiple dwellings, hotels, motels, and other residential sources); and
    ii) Solid waste from commercial or industrial sources that does not contain hazardous waste; and
     
    B) Such facility does not accept hazardous waste and the owner or operator of such facility has established contractual requirements or other appropriate notification or inspection procedures to assure that hazardous wastes are not received at or burned in such facility.

    BOARD NOTE: The U.S. Supreme Court determined, in City of Chicago v. Environmental Defense Fund, Inc., 511 U.S. 328, 114 S. Ct. 1588, 128 L. Ed. 2d 302 (1994), that this exclusion and RCRA section 3001(i) (42 USC 6921(i)) do not exclude the ash from facilities covered by this subsection from regulation as a hazardous waste. At 59 Fed. Reg. 29372 (June 7, 1994), USEPA granted facilities managing ash from such facilities that is determined a hazardous waste under Subpart C of this Part until December 7, 1994 to file a Part A permit application pursuant to 35 Ill. Adm. Code 703.181. At 60 Fed. Reg. 6666 (Feb. 3, 1995), USEPA stated that it interpreted that the point at which ash becomes subject to RCRA Subtitle C regulation is when that material leaves the combustion building (including connected air pollution control equipment).

     

     
    2) Solid wastes generated by any of the following that are returned to the soil as fertilizers:
      
    A) The growing and harvesting of agricultural crops, or
    B) The raising of animals, including animal manures.
        
    3) Mining overburden returned to the mine site.
    4) Fly ash waste, bottom ash waste, slag waste, and flue gas emission control waste generated primarily from the combustion of coal or other fossil fuels, except as provided in 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste.
    5) Drilling fluids, produced waters, and other wastes associated with the exploration, development, or production of crude oil, natural gas, or geothermal energy.
    6) Chromium wastes:
     
    A) Wastes that fail the test for the toxicity characteristic (Sections 721.124 and 721.Appendix B) because chromium is present or which are listed in Subpart D of this Part due to the presence of chromium, that do not fail the test for the toxicity characteristic for any other constituent or which are not listed due to the presence of any other constituent, and that do not fail the test for any other characteristic, if it is shown by a waste generator or by waste generators that:
       
    i) The chromium in the waste is exclusively (or nearly exclusively) trivalent chromium;
    ii) The waste is generated from an industrial process that uses trivalent chromium exclusively (or nearly exclusively) and the process does not generate hexavalent chromium; and
    iii) The waste is typically and frequently managed in non-oxidizing environments.
     
    B) Specific wastes that meet the standard in subsection (b)(6)(A) of this Section (so long as they do not fail the test for the toxicity characteristic for any other constituent and do not exhibit any other characteristic) are:
            
    i) Chrome (blue) trimmings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling;
    ii) Chrome (blue) shavings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling;
    iii) Buffing dust generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue;
    iv) Sewer screenings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling;
    v) Wastewater treatment sludges generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling;
    vi) Wastewater treatment sludges generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, and through-the-blue;
    vii) Waste scrap leather from the leather tanning industry, the shoe manufacturing industry, and other leather product manufacturing industries; and
    viii) Wastewater treatment sludges from the production of titanium dioxide pigment using chromium-bearing ores by the chloride process.
     
    7) Solid waste from the extraction, beneficiation, and processing of ores and minerals (including coal, phosphate rock, and overburden from the mining of uranium ore), except as provided by 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste.
      
    A) For purposes of this subsection (b)(7), beneficiation of ores and minerals is restricted to the following activities: crushing; grinding; washing; dissolution; crystallization; filtration; sorting; sizing; drying; sintering; pelletizing; briquetting; calcining to remove water or carbon dioxide; roasting; autoclaving or chlorination in preparation for leaching (except where the roasting (or autoclaving or chlorination) and leaching sequence produces a final or intermediate product that does not undergo further beneficiation or processing); gravity concentration; magnetic separation; electrostatic separation; floatation; ion exchange; solvent extraction; electrowinning; precipitation; amalgamation; and heap, dump, vat tank, and in situ leaching.
    B) For the purposes of this subsection (b)(7), solid waste from the processing of ores and minerals includes only the following wastes as generated:
                        
    i) Slag from primary copper processing;
    ii) Slag from primary lead processing;
    iii) Red and brown muds from bauxite refining;
    iv) Phosphogypsum from phosphoric acid production;
    v) Slag from elemental phosphorus production;
    vi) Gasifier ash from coal gasification;
    vii) Process wastewater from coal gasification;
    viii) Calcium sulfate wastewater treatment plant sludge from primary copper processing;
    ix) Slag tailings from primary copper processing;
    x) Fluorogypsum from hydrofluoric acid production;
    xi) Process wastewater from hydrofluoric acid production;
    xii) Air pollution control dust or sludge from iron blast furnaces;
    xiii) Iron blast furnace slag;
    xiv) Treated residue from roasting and leaching of chrome ore;
    xv) Process wastewater from primary magnesium processing by the anhydrous process;
    xvi) Process wastewater from phosphoric acid production;
    xvii) Basic oxygen furnace and open hearth furnace air pollution control dust or sludge from carbon steel production;
    xviii) Basic oxygen furnace and open hearth furnace slag from carbon steel production;
    xix) Chloride processing waste solids from titanium tetrachloride production; and
    xx) Slag from primary zinc production.
     
    C) A residue derived from co-processing mineral processing secondary materials with normal beneficiation raw materials or with normal mineral processing raw materials remains excluded under this subsection (b) if the following conditions are fulfilled:
      
    i) The owner or operator processes at least 50 percent by weight normal beneficiation raw materials or normal mineral processing raw materials; and
    ii) The owner or operator legitimately reclaims the secondary mineral processing materials.
          
    8) Cement kiln dust waste, except as provided by 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste.
    9) Solid waste that consists of discarded arsenical-treated wood or wood products that fails the test for the toxicity characteristic for hazardous waste codes D004 through D017 and which is not a hazardous waste for any other reason if the waste is generated by persons that utilize the arsenical-treated wood and wood products for these materials’ intended end use.
    10) Petroleum-contaminated media and debris that fail the test for the toxicity characteristic of Section 721.124 (hazardous waste codes D018 through D043 only) and which are subject to corrective action regulations under 35 Ill. Adm. Code 731.
    11) This subsection corresponds with 40 CFR 261.4(b)(11), which expired by its own terms on January 25, 1993. This statement maintains structural parity with USEPA regulations.
    12) Used chlorofluorocarbon refrigerants from totally enclosed heat transfer equipment, including mobile air conditioning systems, mobile refrigeration, and commercial and industrial air conditioning and refrigeration systems, that use chlorofluorocarbons as the heat transfer fluid in a refrigeration cycle, provided the refrigerant is reclaimed for further use.
    13) Non-terne plated used oil filters that are not mixed with wastes listed in Subpart D of this Part, if these oil filters have been gravity hot-drained using one of the following methods:
        
    A) Puncturing the filter anti-drain back valve or the filter dome end and hot-draining;
    B) Hot-draining and crushing;
    C) Dismantling and hot-draining; or
    D) Any other equivalent hot-draining method that will remove used oil.
      
    14) Used oil re-refining distillation bottoms that are used as feedstock to manufacture asphalt products.
    15) Leachate or gas condensate collected from landfills where certain solid wastes have been disposed of, under certain circumstances:
     
    A) The following conditions must be fulfilled:
     
    i) The solid wastes disposed of would meet one or more of the listing descriptions for Hazardous Waste Codes K169, K170, K171, and K172 if these wastes had been the following USEPA hazardous waste numbers that is generated after the effective date of the listing (January 19, 1999); listed for the waste:

    USEPA Hazardous Waste Numbers

     

    Listing Effective Date

     

    K169, K170, K171, and K172

     

    February 8, 1999

    K174 and K175

     

    May 7, 2001

    K176, K177, and K178

    May 20, 2002

     

       
    ii) The solid wastes described in subsection (b)(15)(A)(i) of this Section were disposed of prior to the effective date of the listing (as set forth in that subsection);
    iii) The leachate or gas condensate does not exhibit any characteristic of hazardous waste nor is derived from any other listed hazardous waste; and
    iv) Discharge of the leachate or gas condensate, including leachate or gas condensate transferred from the landfill to a POTW by truck, rail, or dedicated pipe, is subject to regulation under section 307(b) or 402 of the federal Clean Water Act.
     
    B) After February 13, 2001, leachate Leachate or gas condensate derived from K169, K170, K171, or K172 will no longer be exempt if it is stored or managed in a surface impoundment prior to discharge. After November 21, 2003, leachate or gas condensate derived from K176, K177, or K178 will no longer be exempt if it is stored or managed in a surface impoundment prior to discharge. There is one exception: if the surface impoundment is used to temporarily store leachate or gas condensate in response to an emergency situation (e.g., shutdown of wastewater treatment system), provided the impoundment has a double liner, and provided the leachate or gas condensate is removed from the impoundment and continues to be managed in compliance with the conditions of this subsection (b)(15) of this Section after the emergency ends.
      
    c) Hazardous wastes that are exempted from certain regulations. A hazardous waste that is generated in a product or raw material storage tank, a product or raw material transport vehicle or vessel, a product or raw material pipeline, or in a manufacturing process unit, or an associated non-waste-treatment manufacturing unit, is not subject to regulation under 35 Ill. Adm. Code 702, 703, 705, and 722 through 725, and 728 or to the notification requirements of section 3010 of RCRA until it exits the unit in which it was generated, unless the unit is a surface impoundment, or unless the hazardous waste remains in the unit more than 90 days after the unit ceases to be operated for manufacturing or for storage or transportation of product or raw materials.
    d) Samples
     
    1) Except as provided in subsection (d)(2) of this Section, a sample of solid waste or a sample of water, soil, or air that is collected for the sole purpose of testing to determine its characteristics or composition is not subject to any requirements of this Part or 35 Ill. Adm. Code 702, 703, 705, and 722 through 728. The sample qualifies when:
          
    A) The sample is being transported to a laboratory for the purpose of testing;
    B) The sample is being transported back to the sample collector after testing;
    C) The sample is being stored by the sample collector before transport to a laboratory for testing;
    D) The sample is being stored in a laboratory before testing;
    E) The sample is being stored in a laboratory for testing but before it is returned to the sample collector; or
    F) The sample is being stored temporarily in the laboratory after testing for a specific purpose (for example, until conclusion of a court case or enforcement action where further testing of the sample may be necessary).
     
    2) In order to qualify for the exemption in subsection (d)(1)(A) or (d)(1)(B) of this Section, a sample collector shipping samples to a laboratory and a laboratory returning samples to a sample collector shall must:
      
    A) Comply with U.S. Department of Transportation (USDOT), U.S. Postal Service (USPS), or any other applicable shipping requirements; or
    B) Comply with the following requirements if the sample collector determines that USDOT, USPS, or other shipping requirements do not apply to the shipment of the sample:
      
    i) Assure that the following information accompanies the sample: The sample collector’s name, mailing address, and telephone number; the laboratory’s name, mailing address, and telephone number; the quantity of the sample; the date of the shipment; and a description of the sample.
    ii) Package the sample so that it does not leak, spill, or vaporize from its packaging.
     
    3) This exemption does not apply if the laboratory determines that the waste is hazardous but the laboratory is no longer meeting any of the conditions stated in subsection (d)(1) of this Section.
     
    e) Treatability study samples.
     
    1) Except as is provided in subsection (e)(2) of this Section, a person that generates or collects samples for the purpose of conducting treatability studies, as defined in 35 Ill. Adm. Code 720.110, are not subject to any requirement of 35 Ill. Adm. Code 721 through 723 or to the notification requirements of section 3010 of the Resource Conservation and Recovery Act. Nor are such samples included in the quantity determinations of Section 721.105 and 35 Ill. Adm. Code 722.134(d) when:
       
    A) The sample is being collected and prepared for transportation by the generator or sample collector;
    B) The sample is being accumulated or stored by the generator or sample collector prior to transportation to a laboratory or testing facility; or
    C) The sample is being transported to the laboratory or testing facility for the purpose of conducting a treatability study.
     
    2) The exemption in subsection (e)(1) of this Section is applicable to samples of hazardous waste being collected and shipped for the purpose of conducting treatability studies provided that:
       
    A) The generator or sample collector uses (in “treatability studies”) no more than 10,000 kg of media contaminated with non-acute hazardous waste, 1000 kg of non-acute hazardous waste other than contaminated media, 1 kg of acute hazardous waste, or 2500 kg of media contaminated with acute hazardous waste for each process being evaluated for each generated wastestream waste stream;
    B) The mass of each shipment does not exceed 10,000 kg; the 10,000 kg quantity may be all media contaminated with non-acute hazardous waste, or may include 2500 kg of media contaminated with acute hazardous waste, 1000 kg of hazardous waste, and 1 kg of acute hazardous waste;
    C) The sample must be packaged so that it does not leak, spill, or vaporize from its packaging during shipment and the requirements of subsections (e)(2)(C)(i) or (e)(2)(C)(ii) of this Section are met.
      
    i) The transportation of each sample shipment complies with U.S. Department of Transportation (USDOT), U.S. Postal Service (USPS), or any other applicable shipping requirements; or
    ii) If the USDOT, USPS, or other shipping requirements do not apply to the shipment of the sample, the following information must accompany the sample: The name, mailing address, and telephone number of the originator of the sample; the name, address, and telephone number of the facility that will perform the treatability study; the quantity of the sample; the date of the shipment; and, a description of the sample, including its USEPA hazardous waste number;
      
    D) The sample is shipped to a laboratory or testing facility that is exempt under subsection (f) of this Section, or has an appropriate RCRA permit or interim status;
    E) The generator or sample collector maintains the following records for a period ending three years after completion of the treatability study:
       
    i) Copies of the shipping documents;
    ii) A copy of the contract with the facility conducting the treatability study;
    iii) Documentation showing: The amount of waste shipped under this exemption; the name, address, and USEPA identification number of the laboratory or testing facility that received the waste; the date the shipment was made; and whether or not unused samples and residues were returned to the generator; and
     
    F) The generator reports the information required in subsection (e)(2)(E)(iii) of this Section in its report under 35 Ill. Adm. Code 722.141.
     
    3) The Agency may grant requests on a case-by-case basis for up to an additional two years for treatability studies involving bioremediation. The Agency may grant requests, on a case-by-case basis, for quantity limits in excess of those specified in subsections (e)(2)(A), (e)(2)(B), and (f)(4) of this Section, for up to an additional 5000 kg of media contaminated with non-acute hazardous waste, 500 kg of non-acute hazardous waste, 2500 kg of media contaminated with acute hazardous waste, and 1 kg of acute hazardous waste:
       
    A) In response to requests for authorization to ship, store, and conduct further treatability studies on additional quantities in advance of commencing treatability studies. Factors to be considered in reviewing such requests include the nature of the technology, the type of process (e.g., batch versus continuous), the size of the unit undergoing testing (particularly in relation to scale-up considerations), the time or quantity of material required to reach steady-state operating conditions, or test design considerations, such as mass balance calculations.
    B) In response to requests for authorization to ship, store, and conduct treatability studies on additional quantities after initiation or completion of initial treatability studies when: There has been an equipment or mechanical failure during the conduct of the treatability study, there is need to verify the results of a previously-conducted treatability study, there is a need to study and analyze alternative techniques within a previously-evaluated treatment process, or there is a need to do further evaluation of an ongoing treatability study to determine final specifications for treatment.
    C) The additional quantities allowed and timeframes allowed in subsections (e)(3)(A) and (e)(3)(B) of this Section are subject to all the provisions in subsections (e)(1) and (e)(2)(B) through (e)(2)(F) of this Section. The generator or sample collector shall must apply to the Agency and provide in writing the following information:
         
    i) The reason why the generator or sample collector requires additional time or quantity of sample for the treatability study evaluation and the additional time or quantity needed;
    ii) Documentation accounting for all samples of hazardous waste from the wastestream waste stream that have been sent for or undergone treatability studies, including the date each previous sample from the waste stream was shipped, the quantity of each previous shipment, the laboratory or testing facility to which it was shipped, what treatability study processes were conducted on each sample shipped, and the available results of each treatability study;
    iii) A description of the technical modifications or change in specifications that will be evaluated and the expected results;
    iv) If such further study is being required due to equipment or mechanical failure, the applicant shall must include information regarding the reason for the failure or breakdown and also include what procedures or equipment improvements have been made to protect against further breakdowns; and
    v) Such other information as the Agency determines is necessary.
     
    4) Final Agency determinations pursuant to this subsection (e) may be appealed to the Board.
     
    f) Samples undergoing treatability studies at laboratories or testing facilities. Samples undergoing treatability studies and the laboratory or testing facility conducting such treatability studies (to the extent such facilities are not otherwise subject to RCRA requirements) are not subject to any requirement of this Part, or of 35 Ill. Adm. Code 702, 703, 705, 722 through 726, and 728 or to the notification requirements of Section 3010 of the Resource Conservation and Recovery Act, provided that the requirements of subsections (f)(1) through (f)(11) of this Section are met. A mobile treatment unit may qualify as a testing facility subject to subsections (f)(1) through (f)(11) of this Section. Where a group of mobile treatment units are located at the same site, the limitations specified in subsections (f)(1) through (f)(11) of this Section apply to the entire group of mobile treatment units collectively as if the group were one mobile treatment unit.
           
    1) No less than 45 days before conducting treatability studies, the facility notifies the Agency in writing that it intends to conduct treatability studies under this subsection (f).
    2) The laboratory or testing facility conducting the treatability study has a USEPA identification number.
    3) No more than a total of 10,000 kg of “as received” media contaminated with non-acute hazardous waste, 2500 kg of media contaminated with acute hazardous waste, or 250 kg of other “as received” hazardous waste is subject to initiation of treatment in all treatability studies in any single day. “As received” waste refers to the waste as received in the shipment from the generator or sample collector.
    4) The quantity of “as received” hazardous waste stored at the facility for the purpose of evaluation in treatability studies does not exceed 10,000 kg, the total of which can include 10,000 kg of media contaminated with non-acute hazardous waste, 2500 kg of media contaminated with acute hazardous waste, 1000 kg of non-acute hazardous wastes other than contaminated media, and 1 kg of acute hazardous waste. This quantity limitation does not include treatment materials (including non-hazardous solid waste) added to “as received” hazardous waste.
    5) No more than 90 days have elapsed since the treatability study for the sample was completed, or no more than one year (two years for treatability studies involving bioremediation) has elapsed since the generator or sample collector shipped the sample to the laboratory or testing facility, whichever date first occurs. Up to 500 kg of treated material from a particular waste stream from treatability studies may be archived for future evaluation up to five years from the date of initial receipt. Quantities of materials archived are counted against the total storage limit for the facility.
    6) The treatability study does not involve the placement of hazardous waste on the land or open burning of hazardous waste.
    7) The facility maintains records for three years following completion of each study that show compliance with the treatment rate limits and the storage time and quantity limits. The following specific information must be included for each treatability study conducted:
           
    A) The name, address, and USEPA identification number of the generator or sample collector of each waste sample;
    B) The date the shipment was received;
    C) The quantity of waste accepted;
    D) The quantity of “as received” waste in storage each day;
    E) The date the treatment study was initiated and the amount of “as received” waste introduced to treatment each day;
    F) The date the treatability study was concluded;
    G) The date any unused sample or residues generated from the treatability study were returned to the generator or sample collector or, if sent to a designated facility, the name of the facility and the USEPA identification number.
      
    8) The facility keeps, on-site, a copy of the treatability study contract and all shipping papers associated with the transport of treatability study samples to and from the facility for a period ending three years from the completion date of each treatability study.
    9) The facility prepares and submits a report to the Agency by March 15 of each year that estimates the number of studies and the amount of waste expected to be used in treatability studies during the current year, and includes the following information for the previous calendar year:
           
    A) The name, address, and USEPA identification number of the facility conducting the treatability studies;
    B) The types (by process) of treatability studies conducted;
    C) The names and addresses of persons for whom studies have been conducted (including their USEPA identification numbers);
    D) The total quantity of waste in storage each day;
    E) The quantity and types of waste subjected to treatability studies;
    F) When each treatability study was conducted; and
    G) The final disposition of residues and unused sample from each treatability study.
      
    10) The facility determines whether any unused sample or residues generated by the treatability study are hazardous waste under Section 721.103 and, if so, are subject to 35 Ill. Adm. Code 702, 703, and 721 through 728, unless the residues and unused samples are returned to the sample originator under the exemption of subsection (e) of this Section.
    11) The facility notifies the Agency by letter when the facility is no longer planning to conduct any treatability studies at the site.
     
    g) Dredged material that is not a hazardous waste. Dredged material that is subject to the requirements of a permit that has been issued under section 404 of the Federal Water Pollution Control Act (33 USC 1344) is not a hazardous waste. For the purposes of this subsection (g), the following definitions apply:

    “Dredged material” has the same meaning as in 40 CFR 232.2, incorporated by reference in 35 Ill. Adm. Code 720.111.

     

    “Permit” means any of the following:

     

    A permit issued by the U.S. Army Corps of Engineers (Army Corps) under section 404 of the Federal Water Pollution Control Act (33 USC 1344);

     

    A permit issued by the Army Corps under section 103 of the Marine Protection, Research, and Sanctuaries Act of 1972 (33 USC 1413); or

     

    In the case of Army Corps civil works projects, the administrative equivalent of the permits referred to in the preceding two paragraphs of this definition, as provided for in Army Corps regulations (for example, see 33 CFR 336.1, 336.2, and 337.6).

     

    (Source: Amended at 26 Ill. Reg. ________, effective ______________________)

     

     

    SUBPART C: CHARACTERISTICS OF HAZARDOUS WASTE

     

     
    Section 721.124 Toxicity Characteristic
     
    a) A solid waste (except manufactured gas plant waste) exhibits the characteristic of toxicity if, using the Toxicity Characteristic Leaching Procedure (TCLP), test Method 1311 in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, U.S. EPA USEPA Publication SW-846, as incorporated by reference in 35 Ill. Adm. Code 720.111, the extract from a representative sample of the waste contains any of the contaminants listed in the table in subsection (b) below at a concentration equal to or greater than the respective value given in that table. Where the waste contains less than 0.5 percent filterable solids, the waste itself, after filtering using the methodology outlined in Method 1311, is considered to be the extract for the purpose of this Section.

    BOARD NOTE: The reference to the “EP toxicity test” in 35 Ill. Adm. Code 808.410(b)(4) is to be understood as referencing the test required by this Section.

     

     
    b) A solid waste that exhibits the characteristic of toxicity has the U.S. EPA Hazardous Waste Number USEPA hazardous waste number specified in the following table that corresponds to the toxic contaminant causing it to be hazardous.
     
    MAXIMUM CONCENTRATION OF CONTAMINANTS FOR THE TOXICITY CHARACTERISTIC

    U.S. EPA USEPA

    Hazardous Waste No.

     

     

    Contaminant

     

    CAS

    Number

     

     

    Note

    Regulatory

    Level(mg/L)

     

    D004

    Arsenic

    7440-38-2

     

    5.0

    D005

    Barium

    7440-39-3

     

    100.0

    D018

    Benzene

    71-43-2

     

    0.5

    D006

    Cadmium

    7440-43-9

     

    1.0

    D019

    Carbon tetrachloride

    56-23-5

     

    0.5

    D020

    Chlordane

    57-74-9

     

    0.03

    D021

    Chlorobenzene

    108-90-7

     

    100.0

    D022

    Chloroform

    67-66-3

     

    6.0

    D007

    Chromium

    7440-47-3

     

    5.0

    D023

    o-Cresol

    95-48-7

    4

    200.0

    D024

    m-Cresol

    108-39-4

    4

    200.0

    D025

    p-Cresol

    106-44-5

    4

    200.0

    D026

    Cresol

     

    4

    200.0

    D016

    2,4-D

    94-75-7

     

    10.0

    D027

    1,4-Dichlorobenzene

    106-46-7

     

    7.5

    D028

    1,2-Dichloroethane

    107-06-2

     

    0.5

    D029

    1,1-Dichloroethylene

    75-35-4

     

    0.7

    D030

    2,4-Dinitrotoluene

    121-14-2

    3

    0.13

    D012

    Endrin

    72-20-8

     

    0.02

    D031

    Heptachlor (and its epoxide)

    76-44-8

     

    0.008

    D032

    Hexachlorobenzene

    118-74-1

    3

    0.13

    D033

    Hexachlorobutadiene

    87-68-3

     

    0.5

    D034

    Hexachloroethane

    67-72-1

     

    3.0

    D008

    Lead

    7439-92-1

     

    5.0

    D013

    Lindane

    58-89-9

     

    0.4

    D009

    Mercury

    7439-97-6

     

    0.2

    D014

    Methoxychlor

    72-43-5

     

    10.0

    D035

    Methyl ethyl ketone

    78-93-3

     

    200.0

    D036

    Nitrobenzene

    98-95-3

     

    2.0

    D037

    Pentachlorophenol

    87-86-5

     

    100.0

    D038

    Pyridine

    110-86-1

    3

    5.0

    D010

    Selenium

    7782-49-2

     

    1.0

    D011

    Silver

    7440-22-4

     

    5.0

    D039

    Tetrachloroethylene

    127-18-4

     

    0.7

    D015

    Toxaphene

    8001-35-2

     

    0.5

    D040

    Trichloroethylene

    79-01-6

     

    0.5

    D041

    2,4,5-Trichlorophenol

    95-95-4

     

    400.0

    D042

    2,4,6-Trichlorophenol

    88-06-2

     

    2.0

    D017

    2,4,5-TP (Silvex)

    93-72-1

     

    1.0

    D043

    Vinyl chloride

    75-01-4

     

    0.2

     

    Notes to Table:

     

      
    3 Quantitation limit is greater than the calculated regulatory level. The quantitation limit therefore becomes the regulatory level.
    4 If o-, m-, p-cresol concentrations cannot be differentiated, the total cresol (D026) concentration is used. The regulatory level of total cresol is 200.0 mg/L.

    (Source: Amended at 26 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 pentachlorophenol.

    (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)

     

    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)

     

    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)

     

    K107

    Column bottoms from product separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

    (C,T)

     

    K108

    Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

    (I,T)

     

    K109

    Spent filter cartridges from the product purification from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

    (T)

     

    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 dinitrotoluene.

    (T)

     

    K113

    Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

    (T)

     

    K114

    Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

    (T)

     

    K115

    Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

    (T)

     

    K116

    Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine.

    (T)

     

    K117

    Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene.

    (T)

     

    K118

    Spent adsorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.

    (T)

     

    K136

    Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.

    (T)

     

    K156

    Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.)

    (T)

     

    K157

    Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.)

    (T)

     

    K158

    Baghouse dusts and filter/separation solids from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.)

    (T)

     

    K159

    Organics from the treatment of thiocarbamate wastes.

    (T)

     

    K161

    Purification solids (including filtration, evaporation, and centrifugation solids), bag house dust and floor sweepings from the production of dithiocarbamate acids and their salts. (This listing does not include K125 or K126.)

    (R,T)

     

    K174

    Wastewater treatment sludges from the production of ethylene dichloride or vinyl chloride monomer (including sludges that result from commingled ethylene dichloride or vinyl chloride monomer wastewater and other wastewater), unless the sludges meet the following conditions: (1) they are disposed of in a subtitle C or non- hazardous non-hazardous landfill licensed or permitted by the state or federal government; (2) they are not otherwise placed on the land prior to final disposal; and (3) the generator maintains documentation demonstrating that the waste was either disposed of in an on-site landfill or consigned to a transporter or disposal facility that provided a written commitment to dispose of the waste in an off-site landfill. Upon a showing by the government that a respondent in any enforcement action brought to enforce the requirements of Subtitle C of this Part managed wastewater treatment sludges from the production of vinyl chloride monomer or ethylene dichloride, the respondent must demonstrate that it meets the conditions of the exclusion that are set forth above. In doing so, the respondent must provide appropriate documentation that the terms of the exclusion were met (e.g., contracts between the generator and the landfill owner or operator, invoices documenting delivery of waste to landfill, etc.).

    (T)

     

    K175

    Wastewater treatment sludges from the production of vinyl chloride monomer using mercuric chloride catalyst in an acetylene-based process.

    (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)

     

    K176

    Baghouse filters from the production of antimony oxide, including filters from the production of intermediates (e.g., antimony metal or crude antimony oxide).

    (E)

     

    K177

    Slag from the production of antimony oxide that is speculatively accumulated or disposed of, including slag from the production of intermediates (e.g., antimony metal or crude antimony oxide).

    (T)

     

    K178

    Residues from manufacturing and manufacturing-site storage of ferric chloride from acids formed during the production of titanium dioxide using the chloride-ilmenite process.

    (T)

     

     
    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 cyclopentadiene 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 tetrachlorobenzene in the production of 2,4,5-T.

    (T)

     

    K043

    2,6-Dichlorophenol waste from the production of 2,4-D.

    (T)

     

    K099

    Untreated wastewater from the production of 2,4-D.

    (T)

     

    K123

    Process wastewater (including supernates, filtrates and washwaters) from the production of ethylenebisdithiocarbamic acid and its salts.

    (T)

     

    K124

    Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.

    (C,T)

     

    K125

    Filtration, evaporation and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts.

    (T)

     

    K126

    Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts.

    (T)

     

    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)

     

    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 Aluminum:

    K088

    Spent potliners from primary aluminum reduction.

    (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)

     

     
    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 a - (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. (This waste does not include still bottoms from the distillation of benzyl chloride.)

    (T)

     

    K150

    Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydrochloric acid recovery processes associated with the production of a - (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 a - (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.

    (T)

     

    (Source: Amended at 26 Ill. Reg. ________, effective ______________________)

     

     

     
    Section 721.Appendix G
    Basis for Listing Hazardous Wastes

    USEPA hazardous waste No.

    Hazardous constituents for which listed

    F001

    Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, carbon tetrachloride, chlorinated fluorocarbons.

    F002

    Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, 1,1,2-trichlorethane, chlorobenzene, 1,1,2-trichloro-1,2,2-trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane.

    F003

    N.A.

    F004

    Cresols and cresylic acid, nitrobenzene.

    F005

    Toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, 2-ethoxyethanol, benzene, 2-nitropropane.

    F006

    Cadmium, hexavalent chromium, nickel, cyanide (complexed).

    F007

    Cyanide (salts).

    F008

    Cyanide (salts).

    F009

    Cyanide (salts).

    F010

    Cyanide (salts).

    F011

    Cyanide (salts).

    F012

    Cyanide (complexed).

    F019

    Hexavalent chromium, cyanide (complexed).

    F020

    Tetra- and pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans; tri- and tetrachlorophenols and their clorophenoxy derivative acids, esters, ethers, amines, and other salts.

    F021

    Penta- and hexachlorodibenzo-p-dioxins; penta- and hexachlorodibenzofurans; pentachlorophenol and its derivatives.

    F022

    Tetra-, penta- and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans.

    F023

    Tetra- and pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans; tri- and tetra- chlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines, and other salts.

    F024

    Chloromethane, dichloromethane, trichloromethane, carbon tetrachloride, chloroethylene, 1,1-dichloroethane, 1,2-dichloroethane, trans-1,2-dichloroethylene, 1,1-dichloroethylene, 1,1,1-trichloroethane, 1,1,2-trichloroethane, trichloroethylene, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane, tetrachloroethylene, pentachloroethane, hexachloroethane, allyl chloride (3-chloropropene), dichloropropane, dichloropropene, 2-chloro-1,3-butadiene, hexachloro-1,3-butadiene, hexachlorochylopentadiene, hexachlorocylohexane, benzene, chlorobenzene, dichlorobenzenes, 1,2,4-trichlorobenzene, tetrachlorobenzenes, pentachlorobenzene, hexachlorobenzene, toluene, naphthalene.

    F025

    Chloromethane, dicloromethane, trichloromethane; carbon tetrachloride; chloroethylene; 1,1-dichloroethane; 1,2-dichloroethane; trans-1,2-dichloroethylene; 1,1-dichloroethylene; 1,1,1-trichloroethane; 1,1,2-trichloroethane; trichloroethylene; 1,1,1,2-tetrachloroethane; 1,1,2,2-tetrachloroethane; tetrachloroethylene; pentachloroethane; hexachloroethane; allyl chloride (3-chloropropene); dichloropropane; dichloropropene; 2-chloro-1,3-butadiene; hexachloro-1,3-butadiene; hexachlorocyclopentadiene; benzene; chlorobenzene; dichlorobenzene; 1,2,4-trichlorobenzene; tetrachlorobenzene; pentachlorobenzene; hexachlorobenzene; toluene; naphthalene.

    F026

    Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans.

    F027

    Tetra-, penta, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans; tri-, tetra-, and pentachlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines, and other salts.

    F028

    Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans; tri-, tetra-, and pentachlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines, and other salts.

    F032

    Benz(a)anthracene,; benzo(a)pyrene,; dibenz(a,h)anthracene,; indeno(1,2,3-cd)pyrene,; pentachlorophenol,; arsenic,; chromium,; tetra-, penta-, hexa-, and heptachlorordibenzo-p-dioxins,; tetra-, penta-, hexa-, and heptachlorodibenzofurans.

    F034

    Benz(a)anthracene, benzo(k)fluoranthene, benzo(a)pyrene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene, naphthalene, arsenic, chromium.

    F035

    Arsenic, chromium, and lead.

    F037

    Benzene, benzo(a)pyrene, chrysene, lead, chromium.

    F038

    Benzene, benzo(a)pyrene, chrysene, lead, chromium.

    F039

    All constituents for which treatment standards are specified for multi-source leachate (wastewaters and non-wastewaters) under 35 Ill. Adm. Code 728.Table B (Constituent Concentrations in Waste).

    K001

    Pentachlorophenol, phenol, 2-chlorophenol, p-chloro-m-cresol, 2,4-dimethylphenol, 2,4- dinitrophenol, trichlorophenols, tetrachlorophenols, 2,4- dinitrophenol, cresosote creosote, chrysene, naphthalene, fluoranthene, benzo(b)fluoranthene, benzo(a)pyrene, indeno(1,2,3-cd)pyrene, benz(a) anthracene, dibenz(a)anthracene, acenaphthalene.

    K002

    Hexavalent chromium, lead.

    K003

    Hexavalent chromium, lead.

    K004

    Hexavalent chromium.

    K005

    Hexavalent chromium, lead.

    K006

    Hexavalent chromium.

    K007

    Cyanide (complexed), hexavalent chromium.

    K008

    Hexavalent chromium.

    K009

    Chloroform, formaldehyde, methylene chloride, methyl chloride, paraldehyde, formic acid.

    K010

    Chloroform, formaldehyde, methylene chloride, methyl chloride, paraldehyde, formic acid, chloroacetaldehyde.

    K011

    Acrylonitrile, acetonitrile, hydrocyanic acid.

    K013

    Hydrocyanic acid, acrylonitrile, acetonitrile.

    K014

    Acetonitrile, acrylamide.

    K015

    Benzyl chloride, chlorobenzene, toluene, benzotrichloride.

    K016

    Hexachlorobenzene, hexachlorobutadiene, carbon tetrachloride, hexachloroethane, perchloroethylene.

    K017

    Epichlorohydrin, chloroethers [bis(chloromethyl) ether and bis- (2-chloroethyl) ethers], trichloropropane, dichloropropanols.

    K018

    1,2-dichloroethane, trichloroethylene, hexachlorobutadiene, hexachlorobenzene.

    K019

    Ethylene dichloride, 1,1,1-trichloroethane, 1,1,2-trichloroethane, tetrachloroethanes (1,1,2,2-tetrachloroethane and 1,1,1,2-tetrachloroethane), trichloroethylene, tetrachloroethylene, carbon tetrachloride, chloroform, vinyl chloride, vinylidene chloride.

    K020

    Ethylene dichloride, 1,1,1-trichloroethane, 1,1,2-trichloroethane, tetrachloroethanes (1,1,2,2-tetrachloroethane and 1,1,1,2-tetrachloroethane), trichloroethylene, tetrachloroethylene, carbon tetrachloride, chloroform, vinyl chloride, vinylidene chloride.

    K021

    Antimony, carbon tetrachloride, chloroform.

    K022

    Phenol, tars (polycyclic aromatic hydrocarbons).

    K023

    Phthalic anhydride, maleic anhydride.

    K024

    Phthalic anhydride, 1,4-naphthoguinone.

    K025

    Meta-dinitrobenzene, 2,4-dinitrotoluene.

    K026

    Paraldehyde, pyridines, 2-picoline.

    K027

    Toluene diisocyanate, toluene-2,4-diamine.

    K028

    1,1,1-trichloroethane, vinyl chloride.

    K029

    1,2-dichloroethane, 1,1,1-trichloroethane, vinyl chloride, vinylidene chloride, chloroform.

    K030

    Hexachlorobenzene, hexachlorobutadiene, hexachloroethane, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane, ethylene dichloride.

    K031

    Arsenic.

    K032

    Hexachlorocyclopentadiene.

    K033

    Hexachlorocyclopentadiene.

    K034

    Hexachlorocyclopentadiene.

    K035

    Creosote, chrysene, naphthalene, fluoranthene, benzo(b) fluoranthene, benzo(a)-pyrene, indeno(1,2,3-cd) pyrene, benzo(a)anthracene, dibenzo(a)anthracene, acenaphthalene.

    K036

    Toluene, phosphorodithioic and phosphorothioic acid esters.

    K037

    Toluene, phosphorodithioic and phosphorothioic acid esters.

    K038

    Phorate, formaldehyde, phosphorodithioic and phosphorothioic acid esters.

    K039

    Phosphorodithioic and phosphorothioic acid esters.

    K040

    Phorate, formaldehyde, phosphorodithioic and phosphorothioic acid esters.

    K041

    Toxaphene.

    K042

    Hexachlorobenzene, ortho-dichlorobenzene.

    K043

    2,4-dichlorophenol, 2,6-dichlorophenol, 2,4,6-trichlorophenol.

    K044

    N.A.

    K045

    N.A.

    K046

    Lead.

    K047

    N.A.

    K048

    Hexavalent chromium, lead.

    K049

    Hexavalent chromium, lead.

    K050

    Hexavalent chromium.

    K051

    Hexavalent chromium, lead.

    K052

    Lead.

    K060

    Cyanide, naphthalene, phenolic compounds, arsenic.

    K061

    Hexavalent chromium, lead, cadmium.

    K062

    Hexavalent chromium, lead.

    K064

    Lead, cadmium.

    K065

    Lead, cadmium.

    K066

    Lead, cadmium.

    K069

    Hexavalent chromium, lead, cadmium.

    K071

    Mercury.

    K073

    Chloroform, carbon tetrachloride, hexachloroethane, trichloroethane, tetrachloroethylene, dichloroethylene, 1,1,2,2-tetrachloroethane.

    K083

    Aniline, diphenylamine, nitrobenzene, phenylenediamine.

    K084

    Arsenic.

    K085

    Benzene, dichlorobenzenes, trichlorobenzenes, tetrachlorobenzenes, pentachlorobenzene, hexachlorobenzene, benzyl chloride.

    K086

    Lead, hexavalent chromium.

    K087

    Phenol, naphthalene.

    K088

    Cyanide (complexes).

    K090

    Chromium.

    K091

    Chromium.

    K093

    Phthalic anhydride, maleic anhydride.

    K094

    Phthalic anhydride.

    K095

    1,1,2-trichloroethane, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane.

    K096

    1,2-dichloroethane, 1,1,1-trichloroethane, 1,1,2-trichloroethane.

    K097

    Chlordane, heptachlor.

    K098

    Toxaphene.

    K099

    2,4-dichlorophenol, 2,4,6-trichlorophenol.

    K100

    Hexavalent chromium, lead, cadmium.

    K101

    Arsenic.

    K102

    Arsenic.

    K103

    Aniline, nitrobenzene, phenylenediamine.

    K104

    Aniline, benzene, diphenylamine, nitrobenzene, phynylenediamine.

    K105

    Benzene, monochlorobenzene, dichlorobenzenes, 2,4,6-trichlorophenol.

    K106

    Mercury.

    K111

    2,4-Dinitrotoluene.

    K112

    2,4-Toluenediamine, o-toluidine, p-toluidine, aniline.

    K113

    2,4-Toluenediamine, o-toluidine, p-toluidine, aniline.

    K114

    2,4-Toluenediamine, o-toluidine, p-toluidine.

    K115

    2,4-Toluenediamine.

    K116

    Carbon tetrachloride, tetrachloroethylene, chloroform, phosgene.

    K117

    Ethylene dibromide.

    K118

    Ethylene dibromide.

    K123

    Ethylene thiourea.

    K124

    Ethylene thiourea.

    K125

    Ethylene thiourea.

    K126

    Ethylene thiourea.

    K131

    Dimethyl sulfate, methyl bromide.

    K132

    Methyl bromide.

    K136

    Ethylene dibromide.

    K141

    Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.

    K142

    Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.

    K143

    Benzene, benz(a)anthracene, benzo(b)fluoranthene, benzo(k)fluoranthene.

    K144

    Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene.

    K145

    Benzene, benz(a)anthracene, benzo(a)pyrene, dibenz(a,h)anthracene, naphthalene.

    K147

    Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.

    K148

    Benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.

    K149

    Benzotrichloride, benzyl chloride, chloroform, chloromethane, chlorobenzene, 1,4-dichlorobenzene, hexachlorobenzene, pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, toluene.

    K150

    Carbon tetrachloride, chloroform, chloromethane, 1,4-dichlorobenzene, hexachlorobenzene, pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, 1,1,2,2-tetrachloroethane, tetrachloroethylene, 1,2,4-trichlorobenzene.

    K151

    Benzene, carbon tetrachloride, chloroform, hexachlorobenzene, pentachlorobenzene, toluene, 1,2,4,5-tetrachlorobenzene, tetrachloroethylene.

    K156

    Benomyl, carbaryl, carbendazim, carbofuran, carbosulfan, formaldehyde, methylene chloride, triethylamine.

    K157

    Carbon tetrachloride, formaldehyde, methyl chloride, methylene chloride, pyridine, triethylamine.

    K158

    Benomyl, carbendazim, carbofuran, carbosulfan, chloroform, methylene chloride.

    K159

    Benzene, butylate, EPTC, molinate, pebulate, vernolate.

    K161

    Antimony, arsenic, metam-sodium, ziram.

    K169

    Benzene.

    K170

    Benzo(a)pyrene, dibenz(a,h)anthracene, benzo (a) anthracene, benzo(b)fluoranthene, benzo(k)fluoranthene, 3-methylcholanthrene, 7,12-dimethylbenz(a)anthracene.

    K171

    Benzene, arsenic.

    K172

    Benzene, arsenic.

    K174

    1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD), 1,2,3,4,6,7,8-heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF), 1,2,3,4,7,8,9-heptachlorodibenzofuran (1,2,3,6,7,8,9-HpCDF), all hexachlorodibenzo-p-dioxins (HxCDDs), all hexachlorodibenzofurans (HxCDFs), all pentachlorodibenzo-p-dioxins (PeCDDs), 1,2,3,4,6,7,8,9-octachlorodibenzo-p-dioxin (OCDD), 1,2,3,4,6,7,8,9- octachlorodibenzofuran (OCDF), all pentachlorodibenzofurans (PeCDFs), all tetrachlorodibenzo-p-dioxins (TCDDs), all tetrachlorodibenzofurans (TCDFs).

    K175

    Mercury

    K176

    Arsenic, lead.

    K177

    Antimony.

    K178

    Thallium.

     

     
    N.A.--Waste is hazardous because it fails the test for the characteristic of ignitability, corrosivity, or reactivity.

    (Source: Amended at 26 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

    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
    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
    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 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 SPECIAL PROVISIONS FOR SOLID WASTE MANAGEMENT UNITS CLEANUP

    Section

     
    724.650 Applicability of Corrective Action Management Unit Regulations
    724.652651 Grandfathered Corrective Action Management Units
    724.652 Corrective Action Management Units
    724.653 Temporary Units
    724.654 Staging Piles
    724.655 Disposal of CAMU-Eligible Wastes in Permitted Hazardous Waste Landfills

    SUBPART W: DRIP PADS

    Section

     
    724.670 Applicability
    724.671 Assessment of existing drip pad integrity
    724.672 Design and installation of new drip pads
    724.673 Design and operating requirements
    724.674 Inspections
    724.675 Closure

    SUBPART X: MISCELLANEOUS UNITS

    Section

     
    724.700 Applicability
    724.701 Environmental Performance Standards
    724.702 Monitoring, Analysis, Inspection, Response, Reporting and Corrective Action
    724.703 Post-closure Care

    SUBPART AA: AIR EMISSION STANDARDS FOR PROCESS VENTS

    Section

     
    724.930 Applicability
    724.931 Definitions
    724.932 Standards: Process Vents
    724.933 Standards: Closed-Vent Systems and Control Devices
    724.934 Test Methods and Procedures
    724.935 Recordkeeping requirements
    724.936 Reporting Requirements

    SUBPART BB: AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS

    Section

     
    724.950 Applicability
    724.951 Definitions
    724.952 Standards: Pumps in Light Liquid Service
    724.953 Standards: Compressors
    724.954 Standards: Pressure Relief Devices in Gas/Vapor Service
    724.955 Standards: Sampling Connecting Systems
    724.956 Standards: Open-ended Valves or Lines
    724.957 Standards: Valves in Gas/Vapor or Light Liquid Service
    724.958 Standards: Pumps, Valves, Pressure Relief Devices and Other Connectors
    724.959 Standards: Delay of Repair
    724.960 Standards: Closed-vent Systems and Control Devices
    724.961 Alternative Percentage Standard for Valves
    724.962 Skip Period Alternative for Valves
    724.963 Test Methods and Procedures
    724.964 Recordkeeping Requirements
    724.965 Reporting Requirements

    SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE IMPOUNDMENTS, AND CONTAINERS

    Section

     
    724.980 Applicability
    724.981 Definitions
    724.982 Standards: General
    724.983 Waste Determination Procedures
    724.984 Standards: Tanks
    724.985 Standards: Surface Impoundments
    724.986 Standards: Containers
    724.987 Standards: Closed-vent Systems and Control Devices
    724.988 Inspection and Monitoring Requirements
    724.989 Recordkeeping Requirements
    724.990 Reporting Requirements
    724.991 Alternative Control Requirements for Tanks

    SUBPART DD: CONTAINMENT BUILDINGS

    Section

     
    724.1100 Applicability
    724.1101 Design and operating standards
    724.1102 Closure and Post-closure Care

    SUBPART EE: HAZARDOUS WASTE MUNITIONS AND EXPLOSIVES STORAGE

    Section

     
    724.1200 Applicability
    724.1201 Design and Operating Standards
    724.1202 Closure and Post-Closure Care
     
    724.Appendix A Recordkeeping Instructions
    724.Appendix B EPA Report Form and Instructions (Repealed)
    724.Appendix D Cochran’s Approximation to the Behrens-Fisher Student’s T-Test
    724.Appendix E Examples of Potentially Incompatible Waste
    724.Appendix I Groundwater Monitoring List

    AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the Environmental Protection Act [415 ILCS 5/7.2, 22.4, and 27].

     

    SOURCE: Adopted in R82-19 at 7 Ill. Reg. 14059, effective October 12, 1983; amended in R84-9 at 9 Ill. Reg. 11964, effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 1136, effective January 2, 1986; amended in R86-1 at 10 Ill. Reg. 14119, effective August 12, 1986; amended in R86-28 at 11 Ill. Reg. 6138, effective March 24, 1987; amended in R86-28 at 11 Ill. Reg. 8684, effective April 21, 1987; amended in R86-46 at 11 Ill. Reg. 13577, effective August 4, 1987; amended in R87-5 at 11 Ill. Reg. 19397, effective November 12, 1987; amended in R87-39 at 12 Ill. Reg. 13135, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 458, effective December 28, 1988; amended in R89-1 at 13 Ill. Reg. 18527, effective November 13, 1989; amended in R90-2 at 14 Ill. Reg. 14511, effective August 22, 1990; amended in R90-10 at 14 Ill. Reg. 16658, effective September 25, 1990; amended in R90-11 at 15 Ill. Reg. 9654, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14572, effective October 1, 1991; amended in R91-13 at 16 Ill. Reg. 9833, effective June 9, 1992; amended in R92-1 at 16 Ill. Reg. 17702, effective November 6, 1992; amended in R92-10 at 17 Ill. Reg. 5806, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20830, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6973, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12487, effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17601, effective November 23, 1994; amended in R95-6 at 19 Ill. Reg. 9951, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 11244, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 636, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7638, effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17972, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 2186, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9437, effective July 26, 1999; amended in R00-5 at 24 Ill. Reg. 1146, effective January 6, 2000; amended in R00-13 at 24 Ill. Reg. 9833, effective June 20, 2000; expedited correction at 25 Ill. Reg. 5115, effective June 20, 2000; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. ________, effective ______________________.

     

     

    SUBPART O: INCINERATORS

     

     
    Section 724.440 Applicability
      
    a) The regulations in this Subpart apply to owners and operators of hazardous waste incinerators (as defined in 35 Ill. Adm. Code 720.110), except as Section 724.101 provides otherwise.
    b) Integration of the MACT standards.
      
    1) Except as provided by subsection subsections (b)(2) and (b)(3) of this Section, the standards of this Part no longer apply when an owner or operator demonstrates compliance with the maximum achievable control technology (MACT) requirements of 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.
     
    3) The particulate matter standard of Section 724.443(c) remains in effect for incinerators that elect to comply with the alternative to the particulate matter standard of 40 CFR 63.1206(b)(14), incorporated by reference in 35 Ill. Adm. Code 720.111.

    BOARD NOTE: Sections 9.1 and 39.5 of the Environmental Protection Act [415 ILCS 5/9.1 and 39.5] make the federal MACT standards directly applicable to entities in Illinois and authorize the Agency to issue permits based on the federal standards. In adopting this subsection (b), USEPA stated as follows:

     

    Under [the this approach adopted by USEPA as a] final rule. . . , MACT air emissions and related operating requirements are to be included in title Title V permits; RCRA permits will continue to be required for all other aspects of the combustion unit and the facility that are governed by RCRA (e.g., corrective action, general facility standards, other combustor-specific concerns such as materials handling, risk-based emissions limits and operating requirements, as appropriate, and other hazardous waste management units).

     

    64 Fed Reg. 52828, 52975 (Sept. 30,1999).

     

     
    c) After consideration of the waste analysis included with Part B of the permit application, the Agency, in establishing the permit conditions, must exempt the applicant from all requirements of this Subpart 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 Subpart D of 35 Ill. Adm. Code 721 solely because it is ignitable (Hazard Code I), corrosive (Hazard Code C), or both;
    B) Listed as a hazardous waste in Subpart D of 35 Ill. Adm. Code 721 solely because it is reactive (Hazard Code R) for characteristics other than those listed in Section 721.123(a)(4) and (5), and will not be burned when other hazardous wastes are present in the combustion zone;
    C) A hazardous waste solely because it possesses the characteristic of ignitability, as determined by the test for characteristics of hazardous wastes under Subpart C of 35 Ill. Adm. Code 721; or
    D) 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 Subpart H of 35 Ill. Adm. Code 721 that would reasonably be expected to be in the waste.
      
    d) If the waste to be burned is one that is described by subsection (b)(1)(A), (b)(1)(B), (b)(1)(C), or (b)(1)(D) of this Section and contains insignificant concentrations of the hazardous constituents listed in Subpart H of 35 Ill. Adm. Code 721, then the Agency may, in establishing permit conditions, exempt the applicant from all requirements of this Subpart, except Section 724.441 (Waste Analysis) and Section 724.451 (Closure), after consideration of the waste analysis included with Part B of the permit application, unless the Agency finds that the waste will pose a threat to human health or the environment when burned in an incinerator.
    e) The owner or operator of an incinerator may conduct trial burns subject only to the requirements of 35 Ill. Adm. Code 703.222 through 703.225 (short-term and incinerator permits).

    (Source: Amended at 26 Ill. Reg. ________, effective ______________________)

     

     

    SUBPART S: CORRECTIVE ACTION SPECIAL PROVISIONS FOR SOLID WASTE MANAGEMENT UNITS CLEANUP

     

     
    Section 724.650 Applicability of Corrective Action Management Unit Regulations
      
    a) Except as provided in subsection (b) of this Section, a CAMU is subject to the requirements of Section 724.652.
    b) A CAMU that is approved before April 22, 2002, or for which substantially complete applications (or equivalents) were submitted to the Agency on or before November 20, 2000, is subject to the requirements in Section 724.651 for a grandfathered CAMU. Within a grandfathered CAMU, CAMU waste, activities, and design will not be subject to the standards in Section 724.652, so long as the waste, activities, and design remain within the general scope of the CAMU, as approved.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

    Section 724.652 Corrective Action Management Units
      
    Section 724.651
    Grandfathered Corrective Action Management Units
    a) To implement remedies under Section 724.201 or RCRA section 3008(h), or to implement remedies at a permitted facility that is not subject to Section 724.201, the Agency may designate an area at the facility as a corrective action management unit, as defined in 35 Ill. Adm. Code 720.110, in accordance with the requirements of this Section. “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 that facility. A CAMU must be located within the contiguous property under the control of the owner or operator where the wastes to be managed in the CAMU originated. One or more CAMUs may be designated at a facility.
      
    1) Placement of remediation wastes into or within a CAMU does not constitute land disposal of hazardous wastes.
    2) Consolidation or placement of remediation wastes into or within a CAMU does not constitute creation of a unit subject to minimum technology requirements.
     
    b) Designation of a CAMU.
     
    1) The Agency may designate a regulated unit (as defined in Section 724.190(a)(2)) as a CAMU, or it may incorporate a regulated unit into a CAMU, if:
      
    A) The regulated unit is closed or closing, meaning it has begun the closure process under Section 724.213 or 35 Ill. Adm. Code 725.213; and
    B) Inclusion of the regulated unit will enhance implementation of effective, protective, and reliable remedial actions for the facility.
     
    2) The requirements of Subparts F, G, and H and the unit-specific requirements of this Part or the 35 Ill. Adm. Code 725 requirements that applied to that regulated unit will continue to apply to that portion of the CAMU after incorporation into the CAMU.
     
    c) The Agency shall must designate a CAMU in accordance with the following factors:
           
    1) The CAMU shall must facilitate the implementation of reliable, effective, protective, and cost-effective remedies;
    2) Waste management activities associated with the CAMU shall must not create unacceptable risks to humans or to the environment resulting from exposure to hazardous wastes or hazardous constituents;
    3) The CAMU shall must include uncontaminated areas of the facility only if including such areas for the purpose of managing remediation waste is more protective than managing such wastes at contaminated areas of the facility;
    4) Areas within the CAMU where wastes remain in place after its closure shall must be managed and contained so as to minimize future releases to the extent practicable;
    5) The CAMU shall must expedite the timing of remedial activity implementation, when appropriate and practicable;
    6) The CAMU shall must enable the use, when appropriate, of treatment technologies (including innovative technologies) to enhance the long-term effectiveness of remedial actions by reducing the toxicity, mobility, or volume of wastes that will remain in place after closure of the CAMU; and
    7) The CAMU shall must, to the extent practicable, minimize the land area of the facility upon which wastes will remain in place after closure of the CAMU.
      
    d) The owner or operator shall must provide sufficient information to enable the Agency to designate a CAMU in accordance with the standards of this Section.
    e) The Agency shall must specify in the permit the requirements applicable to a CAMU, including the following:
       
    1) The areal configuration of the CAMU.
    2) Requirements for remediation waste management, including the specification of applicable design, operation, and closure requirements.
    3) Requirements for groundwater monitoring that are sufficient to:
      
    A) Continue to detect and to characterize the nature, extent, concentration, direction, and movement of existing releases of hazardous constituents in groundwater from sources located within the CAMU; and
    B) Detect and subsequently characterize releases of hazardous constituents to groundwater that may occur from areas of the CAMU in which wastes will remain in place after closure of the CAMU.
     
    4) Closure and post-closure care requirements.
     
    A) Closure of a CAMU shall must:
      
    i) Minimize the need for further maintenance; and
    ii) Control, minimize, or eliminate, to the extent necessary to protect human health and the environment, for areas where wastes remain in place, post-closure escape of hazardous waste, hazardous constituents, leachate, contaminated runoff, or hazardous waste decomposition products to the ground, to surface waters, or to the atmosphere.
     
    B) Requirements for closure of a CAMU shall must include the following, as appropriate:
       
    i) Requirements for excavation, removal, treatment, or containment of wastes;
    ii) For areas in which wastes will remain after closure of the CAMU, requirements for the capping of such areas; and
    iii) Requirements for the removal and decontamination of equipment, devices, and structures used in remediation waste management activities within the CAMU.
     
    C) In establishing specific closure requirements for a CAMU under this subsection (c) (e), the Agency shall must consider the following factors:
          
    i) The characteristics of the CAMU;
    ii) The volume of wastes that remain in place after closure;
    iii) The potential for releases from the CAMU;
    iv) The physical and chemical characteristics of the waste;
    v) The hydrological and other relevant environmental conditions at the facility that may influence the migration of any potential or actual releases; and
    vi) The potential for exposure of humans and environmental receptors if releases were to occur from the CAMU.
     
    D) Post-closure care requirements as necessary to protect human health and the environment, including, for areas where wastes will remain in place, monitoring and maintenance activities and the frequency with which such activities shall must be performed to ensure the integrity of any cap, final cover, or other containment system.
       
    f) The Agency shall must document the rationale for designating the CAMU and shall must make such documentation available to the public.
    g) Incorporation of a CAMU into an existing permit must be approved by the Agency according to the procedures for Agency-initiated permit modifications under 35 Ill. Adm. Code 703.270 through 703.273 or according to the permit modification procedures of 35 Ill. Adm. Code 703.283.
    h) The designation of a CAMU does not change the Agency’s existing authority to address clean-up cleanup levels, media-specific points of compliance to be applied to remediation at a facility, or other remedy selection decisions.

    BOARD NOTE: USEPA promulgated this provision pursuant to HSWA provisions of RCRA Subtitle C. Since the federal provision became immediately effective in Illinois, and until USEPA authorizes this Illinois provision, an owner or operator must seek CAMU authorization from USEPA Region V, as well as authorization from the Agency under this provision.

     

    (Source: Section 724.651 renumbered from Section 724.652 and amended at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 724.652 Corrective Action Management Units
     
    a) To implement remedies under Section 724.201 or RCRA section 3008(h), or to implement remedies at a permitted facility that is not subject to Section 724.201, the Agency may designate an area at the facility as a corrective action management unit under the requirements in this Section. “Corrective action management unit” or “CAMU” means an area within a facility that is used only for managing CAMU-eligible wastes for implementing corrective action or cleanup at that facility. A CAMU must be located within the contiguous property under the control of the owner or operator where the wastes to be managed in the CAMU originated. One or more CAMUs may be designated at a facility.
     
    1) “CAMU-eligible waste” means:
      
    A) All solid and hazardous wastes, and all media (including groundwater, surface water, soils, and sediments) and debris, that are managed for implementing cleanup. As-generated wastes (either hazardous or non-hazardous) from ongoing industrial operations at a site are not CAMU-eligible wastes.
    B) Wastes that would otherwise meet the description in subsection (a)(1)(A) of this Section are not CAMU-eligible waste where:
      
    i) The wastes are hazardous waste found during cleanup in intact or substantially intact containers, tanks, or other non-land-based units found above ground, unless the wastes are first placed in the tanks, containers, or non-land-based units as part of cleanup, or the containers or tanks are excavated during the course of cleanup; or
    ii) The Agency makes the determination in subsection (a)(2) of this Section to prohibit the wastes from management in a CAMU.
     
    C) Notwithstanding subsection (a)(1)(A) of this Section, where appropriate, as-generated non-hazardous waste may be placed in a CAMU where such waste is being used to facilitate treatment or the performance of the CAMU.
      
    2) The Agency must prohibit the placement of waste in a CAMU where the Agency determines that the wastes have not been managed in compliance with applicable land disposal treatment standards of 35 Ill. Adm. Code 728, applicable unit design requirements of this Part or 35 Ill. Adm. Code 725, or other applicable requirements of this Subtitle G, and that the non-compliance likely contributed to the release of the waste.
    3) Prohibition against placing liquids in a CAMU.
        
    A) The placement of bulk or noncontainerized liquid hazardous waste or free liquids contained in hazardous waste (whether or not sorbents have been added) in any CAMU is prohibited except where placement of such wastes facilitates the remedy selected for the waste.
    B) The requirements in Section 724.414(d) for placement of containers holding free liquids in landfills apply to placement in a CAMU except where placement facilitates the remedy selected for the waste.
    C) The placement of any liquid which is not a hazardous waste in a CAMU is prohibited unless such placement facilitates the remedy selected for the waste or a demonstration is made pursuant to Section 724.414(f).
    D) The absence or presence of free liquids in either a containerized or a bulk waste must be determined in accordance with Section 724.414(c). Sorbents used to treat free liquids in a CAMU must meet the requirements of Section 724.414(e).
      
    4) Placement of CAMU-eligible wastes into or within a CAMU does not constitute land disposal of hazardous waste.
    5) Consolidation or placement of CAMU-eligible wastes into or within a CAMU does not constitute creation of a unit subject to minimum technology requirements.
     
    b) Establishing a CAMU.
     
    1) The Agency must designate a regulated unit (as defined in Section 724.190(a)(2)) as a CAMU or must incorporate a regulated unit into a CAMU, if it determines that the following is true of a regulated unit:
      
    A) The regulated unit is closed or closing, meaning it has begun the closure process under Section 724.213 or 35 Ill. Adm. Code 725.213; and
    B) Inclusion of the regulated unit will enhance implementation of effective, protective, and reliable remedial actions for the facility.
     
    2) The Subpart F, G, and H requirements and the unit-specific requirements of this Part or 35 Ill. Adm. Code 265 that applied to the regulated unit will continue to apply to that portion of the CAMU after incorporation into the CAMU.
     
    c) The Agency must designate a CAMU that will be used for storage or treatment only in accordance with subsection (f) of this Section. The Agency must designate any other CAMU in accordance with the following requirements:
           
    1) The CAMU must facilitate the implementation of reliable, effective, protective, and cost-effective remedies;
    2) Waste management activities associated with the CAMU must not create unacceptable risks to humans or to the environment resulting from exposure to hazardous wastes or hazardous constituents;
    3) The CAMU must include uncontaminated areas of the facility, only if including such areas for the purpose of managing CAMU-eligible waste is more protective than management of such wastes at contaminated areas of the facility;
    4) Areas within the CAMU, where wastes remain in place after closure of the CAMU, must be managed and contained so as to minimize future releases, to the extent practicable;
    5) The CAMU must expedite the timing of remedial activity implementation, when appropriate and practicable;
    6) The CAMU must enable the use, when appropriate, of treatment technologies (including innovative technologies) to enhance the long-term effectiveness of remedial actions by reducing the toxicity, mobility, or volume of wastes that will remain in place after closure of the CAMU; and
    7) The CAMU must, to the extent practicable, minimize the land area of the facility upon which wastes will remain in place after closure of the CAMU.
     
    d) The owner or operator must provide sufficient information to enable the Agency to designate a CAMU in accordance with the criteria in this Section. This must include, unless not reasonably available, information on the following:
       
    1) The origin of the waste and how it was subsequently managed (including a description of the timing and circumstances surrounding the disposal or release);
    2) Whether the waste was listed or identified as hazardous at the time of disposal or release; and
    3) Whether the disposal or release of the waste occurred before or after the land disposal requirements of 35 Ill. Adm. Code 728 were in effect for the waste listing or characteristic.
     
    e) The Agency must specify, in the permit or order, requirements for the CAMU to include the following:
       
    1) The areal configuration of the CAMU.
    2) Except as provided in subsection (g) of this Section, requirements for CAMU-eligible waste management to include the specification of applicable design, operation, treatment and closure requirements.
    3) Minimum Design Requirements: a CAMU, except as provided in subsection (f) of this Section, into which wastes are placed must be designed in accordance with the following:
      
    A) Unless the Agency approves alternative requirements under subsection (e)(3)(B) of this Section, a CAMU that consists of new, replacement, or laterally expanded units must include a composite liner and a leachate collection system that is designed and constructed to maintain less than a 30-cm depth of leachate over the liner. For purposes of this Section, “composite liner” means a system consisting of two components; the upper component must consist of a minimum 30-mil flexible membrane liner (FML), and the lower component must consist of at least a two-foot layer of compacted soil with a hydraulic conductivity of no more than 1x10-7 cm/sec. FML components consisting of high density polyethylene (HDPE) must be at least 60 mil thick. The FML component must be installed in direct and uniform contact with the compacted soil component;
    B) Alternative Requirements. The Agency must approve alternate requirements if it determines that either of the following is true:
      
    i) The Agency determines that alternative design and operating practices, together with location characteristics, will prevent the migration of any hazardous constituents into the groundwater or surface water at least as effectively as the liner and leachate collection systems in subsection (e)(3)(A) of this Section; or
    ii) The CAMU is to be established in an area with existing significant levels of contamination, and the Agency determines that an alternative design, including a design that does not include a liner, would prevent migration from the unit that would exceed long-term remedial goals.
     
    4) Minimum treatment requirements: Unless the wastes will be placed in a CAMU for storage or treatment only in accordance with subsection (f) of this Section, CAMU-eligible wastes that, absent this Section, would be subject to the treatment requirements of 35 Ill. Adm. Code 728, and that the Agency determines contain principal hazardous constituents must be treated to the standards specified in subsection (e)(4)(C) of this Section.
     
    A) Principal hazardous constituents are those constituents that the Agency determines pose a risk to human health and the environment substantially higher than the cleanup levels or goals at the site.
     
    i) In general, the Agency must designate as principal hazardous constituents those contaminants specified in subsection (e)(4)(H) of this Section.

    BOARD NOTE: The Board has codified 40 CFR 264.552(e)(4)(i)(A)(1) and (e)(4)(i)(A)(2) as subsections (e)(4)(H)(i) and (e)(4)(H)(ii) of this Section in order to comply with Illinois Administrative Code codification requirements.

     

      
    ii) The Agency must also designate constituents as principal hazardous constituents, where appropriate, when risks to human health and the environment posed by the potential migration of constituents in wastes to groundwater are substantially higher than cleanup levels or goals at the site; when making such a designation, the Agency must consider such factors as constituent concentrations, and fate and transport characteristics under site conditions.
    iii) The Agency must also designate other constituents as principal hazardous constituents that the Agency determines pose a risk to human health and the environment substantially higher than the cleanup levels or goals at the site.
       
    B) In determining which constituents are “principal hazardous constituents,” the Agency must consider all constituents which, absent this Section, would be subject to the treatment requirements in 35 Ill. Adm. Code 728.
    C) Waste that the Agency determines contains principal hazardous constituents must meet treatment standards determined in accordance with subsection (e)(4)(D) or (e)(4)(E) of this Section:
    D) Treatment standards for wastes placed in a CAMU.
          
    i) For non-metals, treatment must achieve 90 percent reduction in total principal hazardous constituent concentrations, except as provided by subsection (e)(4)(D)(iii) of this Section.
    ii) For metals, treatment must achieve 90 percent reduction in principal hazardous constituent concentrations as measured in leachate from the treated waste or media (tested according to the TCLP) or 90 percent reduction in total constituent concentrations (when a metal removal treatment technology is used), except as provided by subsection (e)(4)(D)(iii) of this Section.
    iii) When treatment of any principal hazardous constituent to a 90 percent reduction standard would result in a concentration less than 10 times the Universal Treatment Standard for that constituent, treatment to achieve constituent concentrations less than 10 times the Universal Treatment Standard is not required. Universal Treatment Standards are identified in 35 Ill. Adm. Code 728.Table U.
    iv) For waste exhibiting the hazardous characteristic of ignitability, corrosivity, or reactivity, the waste must also be treated to eliminate these characteristics.
    v) For debris, the debris must be treated in accordance with § 268.45, or by methods or to levels established under subsections (e)(4)(D)(i) through (e)(4)(D)(iv) or subsection (e)(4)(E) of this Section, whichever the Agency determines is appropriate.
    vi) Alternatives to TCLP. For metal bearing wastes for which metals removal treatment is not used, the Agency must specify a leaching test other than the TCLP (SW846, Method 1311, incorporated by reference in 35 Ill. Adm. Code 720.111) to measure treatment effectiveness, provided the Agency determines that an alternative leach testing protocol is appropriate for use, and that the alternative more accurately reflects conditions at the site that affect leaching.
     
    E) Adjusted standards. The Board will grant an adjusted standard pursuant to Section 28.1 of the Act to adjust the treatment level or method in subsection (e)(4)(D) of this Section to a higher or lower level, based on one or more of the following factors, as appropriate, if the owner or operator demonstrates that the adjusted level or method would be protective of human health and the environment, based on consideration of the following:
         
    i) The technical impracticability of treatment to the levels or by the methods in subsection (e)(4)(D) of this Section;
    ii) The levels or methods in subsection (e)(4)(D) of this Section would result in concentrations of principal hazardous constituents (PHCs) that are significantly above or below cleanup standards applicable to the site (established either site-specifically, or promulgated under State or federal law);
    iii) The views of the affected local community on the treatment levels or methods in subsection (e)(4)(D) of this Section, as applied at the site, and, for treatment levels, the treatment methods necessary to achieve these levels;
    iv) The short-term risks presented by the on-site treatment method necessary to achieve the levels or treatment methods in subsection (e)(4)(D) of this Section;
    v) The long-term protection offered by the engineering design of the CAMU and related engineering controls under the circumstances set forth in subsection (e)(4)(I) of this Section.

    BOARD NOTE: The Board has codified 40 CFR 264.552(e)(4)(v)(E)(1) through (e)(4)(v)(E)(5) as subsections (e)(4)(I)(i) through (e)(4)(I)(v) of this Section in order to comply with Illinois Administrative Code codification requirements.

     

       
    F) The treatment required by the treatment standards must be completed prior to, or within a reasonable time after, placement in the CAMU.
    G) For the purpose of determining whether wastes placed in a CAMU have met site-specific treatment standards, the Agency must specify a subset of the principal hazardous constituents in the waste as analytical surrogates for determining whether treatment standards have been met for other principal hazardous constituents if it determines that the specification is appropriate based on the degree of difficulty of treatment and analysis of constituents with similar treatment properties.
    H) Principal hazardous constituents that the Agency must designate are the following:
      
    i) Carcinogens that pose a potential direct risk from ingestion or inhalation at the site at or above 10-3; and
    ii) Non-carcinogens that pose a potential direct risk from ingestion or inhalation at the site an order of magnitude or greater over their reference dose.
     
    I) Circumstances relating to the long-term protection offered by engineering design of the CAMU and related engineering controls are the following:
         
    i) Where the treatment standards in subsection (e)(4)(D) of this Section are substantially met and the principal hazardous constituents in the waste or residuals are of very low mobility;
    ii) Where cost-effective treatment has been used and the CAMU meets the Subtitle C liner and leachate collection requirements for new land disposal units at Section 724.401(c) and (d);
    iii) Where, after review of appropriate treatment technologies, the Board determines that cost-effective treatment is not reasonably available, and the CAMU meets the Subtitle C liner and leachate collection requirements for new land disposal units at Section 724.401(c) and (d);
    iv) Where cost-effective treatment has been used and the principal hazardous constituents in the treated wastes are of very low mobility; or
    v) Where, after review of appropriate treatment technologies, the Board determines that cost-effective treatment is not reasonably available, the principal hazardous constituents in the wastes are of very low mobility, and either the CAMU meets or exceeds the liner standards for new, replacement, or a laterally expanded CAMU in subsections (e)(3)(A) and (e)(3)(B) of this Section or the CAMU provides substantially equivalent or greater protection.
     
    5) Except as provided in subsection (f) of this Section, requirements for groundwater monitoring and corrective action that are sufficient to:
       
    A) Continue to detect and to characterize the nature, extent, concentration, direction, and movement of existing releases of hazardous constituents in groundwater from sources located within the CAMU; and
    B) Detect and subsequently characterize releases of hazardous constituents to groundwater that may occur from areas of the CAMU in which wastes will remain in place after closure of the CAMU; and
    C) Require notification to the Agency and corrective action as necessary to protect human health and the environment for releases to groundwater from the CAMU.
     
    6) Except as provided in subsection (f) of this Section, closure and post-closure requirements, as follows:
     
    A) Closure of corrective action management units must do the following:
      
    i) Minimize the need for further maintenance; and
    ii) Control, minimize, or eliminate, to the extent necessary to protect human health and the environment, for areas where wastes remain in place, post-closure escape of hazardous wastes, hazardous constituents, leachate, contaminated runoff, or hazardous waste decomposition products to the ground, to surface waters, or to the atmosphere.
     
    B) Requirements for closure of a CAMU must include the following, as appropriate and as deemed necessary by the Agency for a given CAMU:
      
    i) Requirements for excavation, removal, treatment or containment of wastes; and
    ii) Requirements for removal and decontamination of equipment, devices, and structures used in CAMU-eligible waste management activities within the CAMU.
     
    C) In establishing specific closure requirements for a CAMU under this subsection (e), the Agency must consider the following factors:
          
    i) CAMU characteristics;
    ii) Volume of wastes which remain in place after closure;
    iii) Potential for releases from the CAMU;
    iv) Physical and chemical characteristics of the waste;
    v) Hydrological and other relevant environmental conditions at the facility which may influence the migration of any potential or actual releases; and
    vi) Potential for exposure of humans and environmental receptors if releases were to occur from the CAMU.
     
    D) Cap requirements:
     
    i) At final closure of the CAMU, for areas in which wastes will remain with constituent concentrations at or above remedial levels or goals applicable to the site after closure of the CAMU, the owner or operator must cover the CAMU with a final cover designed and constructed to meet the performance criteria listed in subsection (e)(6)(F) of this Section, except as provided in subsection (e)(6)(D)(ii) of this Section:

    BOARD NOTE: The Board has codified 40 CFR 264.552(e)(6)(iv)(A)(1) through (e)(6)(iv)(A)(5) as subsections (e)(6)(F)(i) through (e)(6)(F)(v) of this Section in order to comply with Illinois Administrative Code codification requirements.

     

     
    ii) The Agency must apply cap requirements that deviate from those prescribed in subsection (e)(6)(D)(i) of this Section if it determines that the modifications are needed to facilitate treatment or the performance of the CAMU (e.g., to promote biodegradation).
      
    E) Post-closure requirements as necessary to protect human health and the environment, to include, for areas where wastes will remain in place, monitoring and maintenance activities, and the frequency with which such activities must be performed to ensure the integrity of any cap, final cover, or other containment system.
    F) The final cover design and performance criteria are as follows:
         
    i) Provide long-term minimization of migration of liquids through the closed unit;
    ii) Function with minimum maintenance;
    iii) Promote drainage and minimize erosion or abrasion of the cover;
    iv) Accommodate settling and subsidence so that the cover’s integrity is maintained; and
    v) Have a permeability less than or equal to the permeability of any bottom liner system or natural subsoils present.
     
    f) A CAMU used for storage or treatment only is a CAMU in which wastes will not remain after closure. Such a CAMU must be designated in accordance with all of the requirements of this Section, except as follows:
      
    1) A CAMU that is used for storage or treatment only and that operates in accordance with the time limits established in the staging pile regulations at Section 724.654(d)(1)(C), (h), and (i) is subject to the requirements for staging piles at Section 724.654(d)(1)(A) and (d)(1)(B), (d)(2), (e), (f), (j), and (k), in lieu of the performance standards and requirements for a CAMU in subsections (c) and (e)(3) through (e)(6) of this Section.
    2) A CAMU that is used for storage or treatment only and that does not operate in accordance with the time limits established in the staging pile regulations at Section 724.654(d)(1)(C), (h), and (i):
      
    A) The owner or operator must operate in accordance with a time limit, established by the Agency, that is no longer than necessary to achieve a timely remedy selected for the waste and
    B) The CAMU is subject to the requirements for staging piles at Section 724.654(d)(1)(A) and (d)(1)(B), (d)(2), (e), (f), (j), and (k) in lieu of the performance standards and requirements for a CAMU in subsections (c) and (e)(4) and (6) of this Section.
         
    g) A CAMU into which wastes are placed where all wastes have constituent levels at or below remedial levels or goals applicable to the site do not have to comply with the requirements for liners at subsection (e)(3)(A) of this Section, caps at subsection (e)(6)(D) of this Section, groundwater monitoring requirements at subsection (e)(5) of this Section or, for treatment or storage-only a CAMU, the design standards at subsection (f) of this Section.
    h) The Agency must provide public notice and a reasonable opportunity for public comment before designating a CAMU. Such notice must include the rationale for any proposed adjustments under subsection (e)(4)(E) of this Section to the treatment standards in subsection (e)(4)(D) of this Section.
    i) Notwithstanding any other provision of this Section, the Agency must impose those additional requirements that it determines are necessary to protect human health and the environment.
    j) Incorporation of a CAMU into an existing permit must be approved by the Agency according to the procedures for Agency-initiated permit modifications under 35 Ill. Adm. Code 703.270 through 703.273, or according to the permit modification procedures of 35 Ill. Adm. Code 703.280 through 703.283.
    k) The designation of a CAMU does not change the Agency’s existing authority to address cleanup levels, media-specific points of compliance to be applied to remediation at a facility, or other remedy selection decisions.

    (Source: Former Section Section 724.652 renumbered to Section 724.651 and new Section 724.652 added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 724.654 Staging Piles

    This Section is written in a special format to make it easier to understand the regulatory requirements. Like all other regulations, this Section establishes enforceable legal requirements.

     

     
    a) What is a staging pile? Definition of a staging pile. A staging pile is an accumulation of solid, non-flowing remediation waste (as defined in 35 Ill. Adm. Code 720.110) that is not a containment building and which is used only during remedial operations for temporary storage at a facility. A staging pile must be located within the contiguous property under the control of the owner or operator where the wastes to be managed in the staging pile originated. Staging piles must be designated by the Agency in accordance with the requirements in this Section.
      
    1) For the purposes of this Section, storage includes mixing, sizing, blending, or other similar physical operations as long as they are intended to prepare the wastes for subsequent management or treatment.
    2) This subsection (a)(2) corresponds with 40 CFR 264.554(a)(2), which USEPA has marked as “reserved.” This statement maintains structural consistency with the federal regulations.
      
    b) When may an owner or operator use a staging pile? Use of a staging pile. An owner or operator may use a staging pile to store hazardous remediation waste (or remediation waste otherwise subject to land disposal restrictions) only if an owner or operator follows the standards and design criteria the Agency has designated for that staging pile. The Agency shall must designate the staging pile in a permit or, at an interim status facility, in a closure plan or order (consistent with 35 Ill. Adm. Code 703.155(a)(5) and (b)(5)). The Agency shall must establish conditions in the permit, closure plan, or order that comply with subsections (d) through (k) of this Section.
    c) What information must an owner or operator provide to get a staging pile designated? Information that an owner or operator must submit to gain designation of a staging pile. When seeking a staging pile designation, an owner or operator shall must provide:
       
    1) Sufficient and accurate information to enable the Agency to impose standards and design criteria for the facility’s staging pile according to subsections (d) through (k) of this Section;
    2) Certification by an independent, qualified, registered professional engineer of technical data, such as design drawings and specifications, and engineering studies, unless the Agency determines, based on information that an owner or operator provides, that this certification is not necessary to ensure that a staging pile will protect human health and the environment; and
    3) Any additional information the Agency determines is necessary to protect human health and the environment.
     
    d) What performance criteria must a staging pile satisfy? Performance criteria that a staging pile must satisfy. The Agency shall must establish the standards and design criteria for the staging pile in the permit, closure plan, or order.
     
    1) The standards and design criteria must comply with the following:
       
    A) The staging pile must facilitate a reliable, effective, and protective remedy;
    B) The staging pile must be designed so as to prevent or minimize releases of hazardous wastes and hazardous constituents into the environment, and minimize or adequately control cross-media transfer, as necessary to protect human health and the environment (for example, through the use of liners, covers, or runoff and runon controls, as appropriate); and
    C) The staging pile must not operate for more than two years, except when the Agency grants an operating term extension under subsection (i) of this Section. An owner or operator shall must measure the two-year limit or other operating term specified by the Agency in the permit, closure plan, or order from the first time an owner or operator places remediation waste into a staging pile. An owner or operator shall must maintain a record of the date when it first placed remediation waste into the staging pile for the life of the permit, closure plan, or order, or for three years, whichever is longer.
     
    2) In setting the standards and design criteria, the Agency shall must consider the following factors:
          
    A) The length of time the pile will be in operation;
    B) The volumes of wastes the owner or operator intends to store in the pile;
    C) The physical and chemical characteristics of the wastes to be stored in the unit;
    D) The potential for releases from the unit;
    E) The hydrogeological and other relevant environmental conditions at the facility that may influence the migration of any potential releases; and
    F) The potential for human and environmental exposure to potential releases from the unit.
     
    e) May a staging pile receive ignitable or reactive remediation waste? Receipt of ignitable or reactive remediation waste. An owner or operator shall must not place ignitable or reactive remediation waste in a staging pile unless:
     
    1) The owner or operator has treated, rendered, or mixed the remediation waste before it placed the waste in the staging pile so that the following is true of the waste:
      
    A) The remediation waste no longer meets the definition of ignitable or reactive under 35 Ill. Adm. Code 721.121 or 721.123; and
    B) The owner or operator has complied with Section 724.117(b); or
     
    2) An owner or operator manages the remediation waste to protect it from exposure to any material or condition that may cause it to ignite or react.
     
    f) How does an owner or operator handle incompatible remediation wastes in a staging pile? Managing incompatible remediation wastes in a staging pile. The term “incompatible waste” is defined in 35 Ill. Adm. Code 720.110. An owner or operator shall must comply with the following requirements for incompatible wastes in staging piles:
       
    1) An owner or operator shall must not place incompatible remediation wastes in the same staging pile unless an owner or operator has complied with Section 724.117(b);
    2) If remediation waste in a staging pile is incompatible with any waste or material stored nearby in containers, other piles, open tanks, or land disposal units (for example, surface impoundments), an owner or operator shall must separate the incompatible materials, or protect them from one another by using a dike, berm, wall, or other device; and
    3) An owner or operator shall must not pile remediation waste on the same base where incompatible wastes or materials were previously piled, unless the base has been decontaminated sufficiently to comply with Section 724.117(b).
       
    g) Are staging piles subject to Land Disposal Restrictions (LDR) and federal Minimum Technological Requirements (MTR)? No. Staging piles are not subject to land disposal restrictions and federal minimum technological requirements. Placing hazardous remediation wastes into a staging pile does not constitute land disposal of hazardous wastes or create a unit that is subject to the federal minimum technological requirements of RCRA 3004(o), 42 USC 6924(o).
    h) How long may an owner or operator operate a staging pile? How long an owner or operator may operate a staging pile. The Agency may allow a staging pile to operate for up to two years after hazardous remediation waste is first placed into the pile. An owner or operator shall must use a staging pile no longer than the length of time designated by the Agency in the permit, closure plan, or order (the “operating term”), except as provided in subsection (i) of this Section.
    i) May an owner or operator receive an operating extension for a staging pile? Receiving an operating extension for a staging pile.
     
    1) The Agency may grant one operating term extension of up to 180 days beyond the operating term limit contained in the permit, closure plan, or order (see subsection (l) of this Section for modification procedures). To justify the need for an extension, an owner or operator shall must provide sufficient and accurate information to enable the Agency to determine that the following is true of continued operation of the staging pile:
      
    A) Continued operation will not pose a threat to human health and the environment; and
    B) Continued operation is necessary to ensure timely and efficient implementation of remedial actions at the facility.
     
    2) The Agency shall must, as a condition of the extension, specify further standards and design criteria in the permit, closure plan, or order, as necessary, to ensure protection of human health and the environment.
     
    j) What is the closure requirement for a staging pile located in a previously contaminated area? The closure requirement for a staging pile located in a previously contaminated area.
     
    1) Within 180 days after the operating term of the staging pile expires, an owner or operator shall must close a staging pile located in a previously contaminated area of the site by removing or decontaminating all of the following:
       
    A) Remediation waste;
    B) Contaminated containment system components; and
    C) Structures and equipment contaminated with waste and leachate.
      
    2) An owner or operator shall must also decontaminate contaminated subsoils in a manner and according to a schedule that the Agency determines will protect human health and the environment.
    3) The Agency shall must include the above requirements in the permit, closure plan, or order in which the staging pile is designated.
     
    k) What is the closure requirement for a staging pile located in an uncontaminated area? The closure requirement for a staging pile located in a previously uncontaminated area.
      
    1) Within 180 days after the operating term of the staging pile expires, an owner or operator shall must close a staging pile located in an uncontaminated area of the site according to Sections 724.358(a) and 724.211 or according to 35 Ill. Adm. Code 725.358(a) and 725.211.
    2) The Agency shall must include the above requirement in the permit, closure plan, or order in which the staging pile is designated.
     
    l) How may an existing permit (for example, RAP), closure plan, or order be modified to allow an owner or operator to use a staging pile? Modifying an existing permit (e.g., a RAP), closure plan, or order to allow the use of a staging pile.
     
    1) To modify a permit, other than a RAP, to incorporate a staging pile or staging pile operating term extension, either of the following must occur:
      
    A) The Agency shall must approve the modification under the procedures for Agency-initiated permit modifications in 35 Ill. Adm. Code 703.270 through 703.273; or
    B) An owner or operator shall must request a Class 2 modification under 35 Ill. Adm. Code 703.280 through 703.283.
       
    2) To modify a RAP to incorporate a staging pile or staging pile operating term extension, an owner or operator shall must comply with the RAP modification requirements under 35 Ill. Adm. Code 703.304(a) and (b).
    3) To modify a closure plan to incorporate a staging pile or staging pile operating term extension, an owner or operator shall must follow the applicable requirements under Section 724.212(c) or 35 Ill. Adm. Code 725.212(c).
    4) To modify an order to incorporate a staging pile or staging pile operating term extension, an owner or operator shall must follow the terms of the order and the applicable provisions of 35 Ill. Adm. Code 703.155(a)(5) or (b)(5).
     
    m) Is information about the staging pile available to the public? Public availability of information about a staging pile. The Agency shall must document the rationale for designating a staging pile or staging pile operating term extension and make this documentation available to the public.

    (Source: Amended at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 724.655 Disposal of CAMU-Eligible Wastes in Permitted Hazardous Waste Landfills
     
    a) The Agency must approve placement of CAMU-eligible wastes in hazardous waste landfills not located at the site from which the waste originated, without the wastes meeting the requirements of 35 Ill. Adm. Code 728, if it determines that the following conditions are met:
      
    1) The waste meets the definition of CAMU-eligible waste in Section 724.652(a)(1) and (a)(2).
    2) The Agency identifies principal hazardous constitutes in such waste, in accordance with Section 724.652(e)(4)(A) and (e)(4)(B), and requires that such principal hazardous constituents are treated to any of the following standards specified for CAMU-eligible wastes:
       
    A) The treatment standards under Section 724.652(e)(4)(D); or
    B) Treatment standards adjusted in accordance with Section 724.652(e)(4)(E)(i), (e)(4)(E)(iii), (e)(4)(E)(iv) or (e)(4)(F)(i); or
    C) Treatment standards adjusted in accordance with Section 724.652(e)(4)(I)(ii), where treatment has been used and that treatment significantly reduces the toxicity or mobility of the principal hazardous constituents in the waste, minimizing the short-term and long-term threat posed by the waste, including the threat at the remediation site.
     
    3) The landfill receiving the CAMU-eligible waste must have a RCRA hazardous waste permit, meet the requirements for new landfills in Subpart N of this Part, and be authorized to accept CAMU-eligible wastes; for the purposes of this requirement, “permit” does not include interim status.
        
    b) The person seeking approval shall provide sufficient information to enable the Agency to approve placement of CAMU-eligible waste in accordance with subsection (a) of this Section. Information required by Section 724.652(d)(1) through (d)(3) for CAMU applications must be provided, unless not reasonably available.
    c) The Agency must provide public notice and a reasonable opportunity for public comment before approving CAMU eligible waste for placement in an off-site permitted hazardous waste landfill, consistent with the requirements for CAMU approval at Section 724.652(h). The approval must be specific to a single remediation.
    d) Applicable hazardous waste management requirements in this Part, including recordkeeping requirements to demonstrate compliance with treatment standards approved under this Section, for CAMU-eligible waste must be incorporated into the receiving facility permit through permit issuance or a permit modification, providing notice and an opportunity for comment and a hearing. Notwithstanding 35 Ill. Adm. Code 702.181(a), a landfill may not receive hazardous CAMU-eligible waste under this Section unless its permit specifically authorizes receipt of such waste.
    e) For each remediation, CAMU-eligible waste may not be placed in an off-site landfill authorized to receive CAMU-eligible waste in accordance with subsection (d) of this Section until the following additional conditions have been met:
          
    1) The landfill owner or operator notifies the Agency and persons on the facility mailing list, maintained in accordance with 35 Ill. Adm. Code 705.163(a), of his or her intent to receive CAMU-eligible waste in accordance with this Section; the notice must identify the source of the remediation waste, the principal hazardous constituents in the waste, and treatment requirements.
    2) Persons on the facility mailing list may provide comments, including objections to the receipt of the CAMU-eligible waste, to the Agency within 15 days after notification.
    3) The Agency must object to the placement of the CAMU-eligible waste in the landfill within 30 days of notification; the Agency must extend the review period an additional 30 days if it determines that the extension is necessary because of public concerns or insufficient information.
    4) CAMU-eligible wastes may not be placed in the landfill until the Agency has notified the facility owner or operator that it does not object to its placement.
    5) If the Agency objects to the placement or does not notify the facility owner or operator that it has chosen not to object, the facility may not receive the waste, notwithstanding 35 Ill. Adm. Code 702.181(a), until the objection has been resolved, or the owner/operator obtains a permit modification in accordance with the procedures of 35 Ill. Adm. Code 703.280 through 703.283 specifically authorizing receipt of the waste.
    6) The Board will grant an adjusted standard under Section 28.1 of the Act that modifies, reduces, or eliminates the notification requirements of this subsection (e) as they apply to specific categories of CAMU-eligible waste, if the owner or operator demonstrates that this is possible based on miminal risk.

    f)  Generators of CAMU-eligible wastes sent off-site to a hazardous waste landfill under this Section must comply with the requirements of 35 Ill. Adm. Code 728.107(a)(4). Off-site facilities treating CAMU-eligible wastes to comply with this Section must comply with the requirements of 35 Ill. Adm. Code 728.107(b)(4), except that the certification must be with respect to the treatment requirements of subsection (a)(2) of this Section.

     

     
    g) For the purposes of this Section only, the “design of the CAMU” in Section 724.652(e)(4)(E)(v) means design of the permitted Subtitle C landfill.

    (Source: Added at 26 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 (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

    SUBPART N: CONDITIONAL EXEMPTION FOR LOW-LEVEL MIXED WASTE STORAGE, TREATMENT, TRANSPORTATION AND DISPOSAL

    Section

     
    726.310 Definitions
    726.320 Storage and Treatment Conditional Exemption
    726.325 Wastes Eligible for a Storage and Treatment Conditional Exemption for Low-Level Mixed Waste
    726.330 Conditions to Qualify for and Maintain a Storage and Treatment Conditional Exemption
    726.335 Treatment Allowed by a Storage and Treatment Conditional Exemption
    726.340 Loss of a Storage and Treatment Conditional Exemption and Required Action
    726.345 Reclaiming a Lost Storage and Treatment Conditional Exemption
    726.350 Recordkeeping for a Storage and Treatment Conditional Exemption
    726.355 Waste No Longer Eligible for a Storage and Treatment Conditional Exemption
    726.360 Applicability of Closure Requirements to Storage Units
    726.405 Transportation and Disposal Conditional Exemption
    726.410 Wastes Eligible for a Transportation and Disposal Conditional Exemption
    726.415 Conditions to Qualify for and Maintain a Transportation and Disposal Conditional Exemption
    726.420 Treatment Standards for Eligible Waste
    726.425 Applicability of the Manifest and Transportation Condition
    726.430 Effectiveness of a Transportation and Disposal Exemption
    726.435 Disposal of Exempted Waste
    726.440 Containers Used for Disposal of Exempted Waste
    726.445 Notification
    726.450 Recordkeeping for a Transportation and Disposal Conditional Exemption
    726.455 Loss of a Transportation and Disposal Conditional Exemption and Required Action
    726.460 Reclaiming a Lost Transportation and Disposal Conditional Exemption
     
    726.Appendix A Tier I and Tier II Feed Rate and Emissions Screening Limits for Metals
    726.Appendix B Tier I Feed Rate Screening Limits for Total Chlorine
    726.Appendix C Tier II Emission Rate Screening Limits for Free Chlorine and Hydrogen Chloride
    726.Appendix D Reference Air Concentrations
    726.Appendix E Risk Specific Doses
    726.Appendix F Stack Plume Rise
    726.Appendix G Health-Based Limits for Exclusion of Waste-Derived Residues
    726.Appendix H Potential PICs for Determination of Exclusion of Waste-Derived Residues
    726.Appendix I Methods Manual for Compliance with BIF Regulations
    726.Appendix J Guideline on Air Quality Models
    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. 9853, effective June 20, 2000; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. ________, effective ______________________.

     

     

    SUBPART N: CONDITIONAL EXEMPTION FOR LOW-LEVEL MIXED WASTE STORAGE, TREATMENT, TRANSPORTATION AND DISPOSAL

     

     
    Section 726.310 Definitions

    Terms are defined as follows for the purposes of this Subpart N:

     

    “CERCLA reportable quantity” means that quantity of a particular substance designated by USEPA in 40 CFR 302.4 pursuant to the Comprehensive Environmental Response, Compensation and Liability Act of 1980 (42 USC 9601 et seq.) for which notification is required upon a release to the environment.

     

    “Certified delivery” means certified mail with return receipt requested, equivalent courier service, or other means that provides the sender with a receipt confirming delivery.

     

    “Director” is as defined in 35 Ill. Adm. Code 702.110.

     

    “DNS” means the Department of Nuclear Safety, the State of Illinois agency charged with regulating source, by-product, and special nuclear material in Illinois in accordance with an agreement between the State and the federal Nuclear Regulatory Commission (NRC) under section 274(b) of the federal Atomic Energy Act of 1954, as amended (42 USC 2021(b)).

     

    BOARD NOTE: In addition to the materials regulated under this Part, the DNS regulates radioactive materials under the Radiation Protection Act of 1990 [420 ILCS 40] that are not licensed by the federal NRC. For the purposes of notices to the DNS required under this Subpart N, the address is as follows:

     

    Illinois Department of Nuclear Safety

    1035 Outer Park Drive

    Springfield, Illinois 62704

     

    “Eligible naturally occurring or accelerator-produced radioactive material” means naturally occurring or accelerator-produced radioactive material (NARM) that is eligible for a transportation and disposal conditional exemption. It is a NARM waste that contains RCRA hazardous waste, meets the waste acceptance criteria of, and is allowed by State NARM regulations to be disposed of at a low-level radioactive waste disposal facility (LLRWDF) licensed in accordance with 10 CFR 61, DNS regulations, or the equivalent regulations of a licensing agency in another state.

     

    BOARD NOTE: The Illinois DNS regulations are codified at 32 Ill. Adm. Code: Chapter II, Subchapter b and d.

     

    “Exempted waste” means a waste that meets the eligibility criteria in Section 726.325 and all of the conditions in Section 726.330 or a waste that meets the eligibility criteria in Section 726.410 and which complies with all the conditions in Section 726.415. Such waste is conditionally exempted from the regulatory definition of hazardous waste in 35 Ill. Adm. Code 721.103.

     

    “Hazardous waste” means hazardous waste as defined in 35 Ill. Adm. Code 721.103.

     

    “Land disposal restriction treatment standards” or “LDR treatment standards” means treatment standards, under 35 Ill. Adm. Code 728, that a RCRA hazardous waste must meet before it can be disposed of in a RCRA hazardous waste land disposal unit.

     

    “License” means a license issued by the federal NRC or the Illinois DNS to a user that manages radionuclides regulated by the federal NRC or the Illinois DNS under authority of the Atomic Energy Act of 1954, as amended (42 USC 2014 et seq.) or the Radiation Protection Act of 1990 [420 ILCS 40].

     

    “Low-level mixed waste” or “LLMW” is a waste that contains both low-level radioactive waste and RCRA hazardous waste.

     

    “Low-level radioactive waste” or “LLRW” is a radioactive waste that contains source, by-product, or special nuclear material and which is not classified as high-level radioactive waste, transuranic waste, spent nuclear fuel, or by-product material, as defined in section 11(e)(2) of the Atomic Energy Act of 1954 (42 USC 2014(e)(2)). (See also the NRC definition of waste at 10 CFR 61.2.)

     

    BOARD NOTE: This definition differs from the similar definitions of low-level radioactive waste in the Illinois Low-Level Radioactive Waste Management Act [420 ILCS 20/3(k)], the Central Midwest Interstate Low-Level Radioactive Waste Compact Act [45 ILCS 140/1, Article II(k)], and 32 Ill. Adm. Code 606.20(g) of the DNS regulations. Those basically define low-level radioactive waste as radioactive waste that is not (1) high-level radioactive waste, (2) transuranic waste, (3) spent nuclear fuel, or (4) by-product material, as such are defined in section 11 of the federal Atomic Energy Act of 1954 (42 USC 2014).

     

    “Mixed waste” means a waste that contains both RCRA hazardous waste and source, by-product, or special nuclear material subject to the Atomic Energy Act of 1954, as amended (42 USC 2014 et seq.).

     

    BOARD NOTE: This definition differs from the similar definitions of mixed waste in the Illinois Low-Level Radioactive Waste Management Act [420 ILCS 20/3(l)] and 32 Ill. Adm. Code 606.20(h) of the DNS regulations. Those basically define mixed waste as containing both RCRA hazardous waste and low-level radioactive waste, as such is defined under Section 3(k) of the Illinois Low-Level Radioactive Waste Management Act [420 ILCS 20/3(k)].

     

    “Naturally occurring or accelerator-produced radioactive material” or “NARM” means a radioactive material that fulfills one of the following conditions:

     

    It is naturally occurring and it is not a source, by-product, or special nuclear material, as defined by the federal Atomic Energy Act (42 USC 2014 et seq.), or

     

    It is produced by an accelerator.

     

    BOARD NOTE: NARM is regulated by the State, under the Radiation Protection Act of 1990 [420 ILCS 40] and 32 Ill. Adm. Code: Chapter II, Subchapter b and d, or by the federal Department of Energy (DOE), as authorized by the federal Atomic Energy Act (42 USC 2014 et seq.), under DOE regulations and orders.

     

    “NRC” means the United States Nuclear Regulatory Commission.

     

    BOARD NOTE: For the purposes of notices to the NRC required under this Subpart N, the address is as follows:

     

    U.S. Nuclear Regulatory Commission, Region III

    801 Warrenville Road

    Lisle, Illinois 60532-4351

     

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.320 Storage and Treatment Conditional Exemption

    The storage and treatment conditional exemption exempts low-level mixed waste from the regulatory definition of hazardous waste in 35 Ill. Adm. Code 721.103 if the waste meets the eligibility criteria in Section 726.325 and the generator meets the conditions in Section 726.330.

     

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.325 Wastes Eligible for a Storage and Treatment Conditional Exemption for Low-Level Mixed Waste

    Low-level mixed waste (LLMW), as defined in Section 726.310, is eligible for a storage and treatment conditional exemption if it is generated and managed by a person under a single federal NRC or Illinois DNS license. (Mixed waste generated at a facility with a different license number and shipped to a different person’s facility for storage or treatment requires a permit, and such mixed waste is ineligible for this exemption. In addition, NARM waste is ineligible for this exemption.)

     

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

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

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.335 Treatment Allowed by a Storage and Treatment Conditional Exemption

    The generator may treat its low-level mixed waste at its facility within a tank or container in accordance with the terms of its federal NRC or Illinois DNS license. Treatment that cannot be done in a tank or container without a RCRA permit (such as incineration) is not allowed under this exemption.

     

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.340 Loss of a Storage and Treatment Conditional Exemption and Required Action
     
    a) A generator’s LLMW will automatically lose the storage and treatment conditional exemption if the generator fails to meet any of the conditions specified in Section 726.330. When a generator’s LLMW loses the exemption, the generator must immediately manage that waste which failed the condition as RCRA hazardous waste, and the storage unit storing the LLMW immediately becomes subject to RCRA hazardous waste container or tank storage requirements.
     
    1) If a generator fails to meet any of the conditions specified in Section 726.330, the generator must report to the Agency, the Illinois DNS, and the NRC in writing by certified delivery within 30 days after learning of the failure. The generator’s report must be signed by the generator’s authorized representative certifying that the information provided is true, accurate, and complete. This report must include:
       
    A) The specific conditions that the generator failed to meet;
    B) A description of the LLMW (including the waste name, hazardous waste codes and quantity) and storage location at the facility; and
    C) The dates on which the generator failed to meet the conditions.
     
    2) If the failure to meet any of the conditions may endanger human health or the environment, the generator must also immediately notify the Agency orally within 24 hours and follow up with a written notification within five days. A failure that may endanger human health or the environment may include, but is not limited to, discharge of a CERCLA reportable quantity or other leaking or exploding tanks or containers, or detection of radionuclides above background or hazardous constituents in the leachate collection system of a storage area. If the failure may endanger human health or the environment, the generator must follow the provisions of its emergency plan.
     
    b) The Board may, by an order issued in an enforcement proceeding against the generator, terminate the generator’s conditional exemption for its LLMW, or require the generator to meet additional conditions to claim a conditional exemption, for serious or repeated noncompliance with any requirements of this Subpart N.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.345 Reclaiming a Lost Storage and Treatment Conditional Exemption
     
    a) A generator may reclaim a lost storage and treatment conditional exemption for its LLMW if the following conditions are fulfilled:
      
    1) The generator again meets the conditions specified in Section 726.330; and
    2) The generator sends the Agency a notice by certified delivery that the generator is reclaiming the exemption for its LLMW. The generator’s notice must be signed by its authorized representative certifying that the information contained in the generator’s notice is true, complete, and accurate. In its notice, the generator must do the following:
        
    A) Explain the circumstances of each failure.
    B) Certify that the generator has corrected each failure that caused it to lose the exemption for its LLMW and that the generator again meets all the conditions as of the date that the generator specifies.
    C) Describe plans that the generator has implemented, listing specific steps that it has taken, to ensure that the conditions will be met in the future.
    D) Include any other information that the generator wants the Agency to consider when it reviews the generator’s notice reclaiming the exemption.
     
    b) The Agency may terminate a reclaimed conditional exemption if it determines, in writing, pursuant to Section 39 of the Act, that the generator’s claim is inappropriate based on factors including, but not limited to, the following: the generator has failed to correct the problem; the generator explained the circumstances of the failure unsatisfactorily; or the generator failed to implement a plan with steps to prevent another failure to meet the conditions of Section 726.330. In reviewing a reclaimed conditional exemption under this Section, the Agency may add conditions to the exemption to ensure that waste management during storage and treatment of the LLMW will protect human health and the environment. Any Agency determination made pursuant to this subsection (b) is subject to review by the Board pursuant to Section 40 of the Act.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.350 Recordkeeping for a Storage and Treatment Conditional Exemption
     
    a) In addition to those records required by the generator’s federal NRC or Illinois DNS license, the generator must keep records as follows:
        
    1) The generator’s initial notification records, return receipts, reports to the Agency of failures to meet the exemption conditions, and all records supporting any reclaim of an exemption;
    2) Records of the generator’s LLMW annual inventories and quarterly inspections;
    3) The generator’s certification that facility personnel who manage stored mixed waste are trained in safe management of LLMW including training in chemical waste management and hazardous materials incidents response; and
    4) The generator’s emergency plan, as specified in Section 726.330(b).
     
    b) The generator must maintain records concerning notification, personnel trained, and its emergency plan for as long as the generator claims this exemption and for three years thereafter, or in accordance with federal NRC regulations under 10 CFR 20 or under Illinois DNS regulations under 32 Ill. Adm. Code: Chapter II, Subchapter b, whichever is longer. A generator must maintain records concerning its annual inventory and quarterly inspections for three years after the waste is sent for disposal, or in accordance with federal NRC regulations under 10 CFR 20 or with Illinois DNS regulations under 32 Ill. Adm. Code: Chapter II, Subchapter b, whichever is longer.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.355 Waste No Longer Eligible for a Storage and Treatment Conditional Exemption
      
    a) When a generator’s LLMW has met the requirements of its federal NRC or Illinois DNS license for decay-in-storage and can be disposed of as non-radioactive waste, then the conditional exemption for storage no longer applies. On that date the generator’s waste is subject to hazardous waste regulation under the relevant Sections of 35 Ill. Adm. Code 702, 703, 720 through 726, and 728, and the time period for accumulation of a hazardous waste, as specified in 35 Ill. Adm. Code 722.134 begins.
    b) When a generator’s conditionally exempt LLMW, which has been generated and stored under a single federal NRC or Illinois DNS license number, is removed from storage, it is no longer eligible for the storage and treatment exemption. However, a generator’s waste may be eligible for the transportation and disposal conditional exemption at Section 726.405.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.360 Applicability of Closure Requirements to Storage Units

    An interim status and permitted storage unit that has been used to store only LLMW prior to April 22, 2002 and which, after that date, stores only LLMW that becomes exempt under this subpart N, is not subject to the closure requirements of 35 Ill. Adm. Code 724 and 725. A storage unit (or portions of units) that has been used to store both LLMW and non-mixed hazardous waste prior to April 22, 2002 or which is used to store both after that date remain subject to closure requirements with respect to the non-mixed hazardous waste.

     

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.405 Transportation and Disposal Conditional Exemption

    A transportation and disposal conditional exemption exempts a generator’s waste from the regulatory definition of hazardous waste in 35 Ill. Adm. Code 721.103 if the generator’s waste meets the eligibility criteria under Section 726.410, and the generator meets the conditions in Section 726.415.

     

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.410 Wastes Eligible for a Transportation and Disposal Conditional Exemption

    Eligible waste must be one or both of the following:

     

      
    a) A low-level mixed waste (LLMW), as defined in Section 726.310, that meets the waste acceptance criteria of a LLRWDF; or
    b) An eligible NARM waste, defined in Section 726.310.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.415 Conditions to Qualify for and Maintain a Transportation and Disposal Conditional Exemption

    A generator must meet the following conditions for its eligible waste to qualify for and maintain the exemption:

     

        
    a) The eligible waste must meet or be treated to meet LDR treatment standards, as described in Section 726.420;
    b) If the generator is not already subject to federal NRC or Illinois DNS manifest and transportation regulations for the shipment of its waste, the generator must manifest and transport its waste according to federal NRC or Illinois DNS regulations, as described in Section 726.425;
    c) The exempted waste must be in containers when it is disposed of in the LLRWDF, as described in Section 726.440; and
    d) The exempted waste must be disposed of at a designated LLRWDF, as described in Section 726.435.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.420 Treatment Standards for Eligible Waste

    A generator’s LLMW or eligible NARM waste must meet the applicable LDR treatment standards specified in 35 Ill. Adm. Code 728.Subpart D.

     

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.425 Applicability of the Manifest and Transportation Condition

    If a generator is not already subject to federal NRC or Illinois DNS manifest and transportation regulations for the shipment of its waste, the generator must meet the federal NRC manifest requirements under 10 CFR 20.2006, incorporated by reference in 35 Ill. Adm. Code 720.111, and Illinois DNS manifest requirements under 32 Ill. Adm. Code 340, and the federal NRC transportation requirements under 10 CFR 71.5 and the Illinois DNS transportation requirements under 32 Ill. Adm. Code 341 to ship the exempted waste.

     

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.430 Effectiveness of a Transportation and Disposal Exemption

    The exemption becomes effective once all of the following have occurred:

     

        
    a) The generator’s eligible waste meets the applicable LDR treatment standards;
    b) The generator has received return receipts that it has notified the Agency and the LLRWDF, as described in Section 726.445;
    c) The generator has completed the packaging and preparation for shipment requirements for its waste according to federal NRC packaging and transportation regulations found under 10 CFR 71, incorporated by reference in 35 Ill. Adm. Code 720.111, and under Illinois DNS regulations under 32 Ill. Adm. Code 341; and a generator has prepared a manifest for a generator’s waste according to NRC manifest regulations found under 10 CFR 20 or under Illinois DNS regulations under 32 Ill. Adm. Code 340; and
    d) The generator has placed its waste on a transportation vehicle destined for a LLRWDF licensed by the federal NRC, the Illinois DNS, or by a nuclear licensing agency in another state.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.435 Disposal of Exempted Waste

    A generator’s exempted waste must be disposed of in a LLRWDF that is regulated and licensed by the federal NRC under 10 CFR 61, by the Illinois DNS under 32 Ill. Adm. Code: Chapter II, Subchapters b and d, or by a licensing agency in another state, including State NARM licensing regulations for eligible NARM.

     

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.440 Containers Used for Disposal of Exempted Waste

    A generator’s exempted waste must be placed in containers before it is disposed of. The container must be one of the following:

     

       
    a) A carbon steel drum;
    b) An alternative container with equivalent containment performance in the disposal environment as a carbon steel drum; or
    c) A high-integrity container, as defined by NRC in Appendix G to 40 CFR 20, incorporated by reference in 35 Ill. Adm. Code 720.111.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.445 Notification
      
    a) A generator must provide a one time notice to the Agency and the Illinois DNS stating that it is claiming the transportation and disposal conditional exemption prior to the initial shipment of an exempted waste from the generator’s facility to a LLRWDF. The generator’s dated written notice must include its facility name, address, phone number, and RCRA ID number and be sent by certified delivery.
    b) A generator must notify the LLRWDF receiving its exempted waste by certified delivery before shipment of each exempted waste. The generator can only ship the exempted waste after it has received the return receipt of its notice to the LLRWDF. This notification must include the following information:
           
    1) A statement that the generator has claimed the exemption for the waste;
    2) A statement that the eligible waste meets applicable LDR treatment standards;
    3) The generator’s facility’s name, address, and RCRA ID number;
    4) The RCRA hazardous waste codes prior to the exemption of the waste streams;
    5) A statement that the exempted waste must be placed in a container according to Section 726.440 prior to disposal in order for the waste to remain exempt under the transportation and disposal conditional exemption of this Subpart N;
    6) The manifest number of the shipment that will contain the exempted waste; and
    7) A certification that all the information provided is true, complete, and accurate. The statement must be signed by the generator’s authorized representative.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.450 Recordkeeping for a Transportation and Disposal Conditional Exemption

    In addition to those records required by a generator’s NRC or Illinois DNS license, the generator must keep records as follows:

     

         
    a) The generator must follow the applicable existing recordkeeping requirements under 35 Ill. Adm. Code 724.173, 725.173, and 728.107 to demonstrate that its waste has met LDR treatment standards prior to the generator claiming the exemption.
    b) The generator must keep a copy of all notifications and return receipts required under Sections 726.455, and 726.460 for three years after the exempted waste is sent for disposal.
    c) The generator must keep a copy of all notifications and return receipts required under Section 726.445(a) for three years after the last exempted waste is sent for disposal.
    d) The generator must keep a copy of the notification and return receipt required under Section 726.445(b) for three years after the exempted waste is sent for disposal.
    e) If the generator is not already subject to federal NRC and Illinois DNS manifest and transportation regulations for the shipment of its waste, the generator must also keep all other documents related to tracking the exempted waste as required under federal 10 CFR 20.2006, incorporated by reference in 35 Ill. Adm. Code 720.111, and Illinois DNS requirements under 32 Ill. Adm. Code 340, including applicable NARM requirements, in addition to the records specified in subsections (a) through (d) of this Section.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.455 Loss of a Transportation and Disposal Conditional Exemption and Required Action
     
    a) Any waste will automatically lose the transportation and disposal exemption if the generator fails to manage it in accordance with all of the conditions specified in Section 726.415.
     
    1) When the generator fails to meet any of the conditions specified in Section 726.415 for any of its wastes, the generator must report to the Agency and the Illinois DNS, in writing by certified delivery, within 30 days after learning of the failure. The generator’s report must be signed by its authorized representative certifying that the information provided is true, accurate, and complete. This report must include the following:
       
    A) The specific conditions that the generator failed to meet for the waste;
    B) A description of the waste (including the waste name, hazardous waste codes and quantity) that lost the exemption; and
    C) The dates on which the generator failed to meet the conditions for the waste.
     
    2) If the failure to meet any of the conditions may endanger human health or the environment, the generator must also immediately notify the Agency orally within 24 hours and follow up with a written notification within 5 days.
     
    b) The Board may, by an order issued in an enforcement proceeding against the generator, terminate the generator’s ability to claim a conditional exemption for its waste, or require the generator to meet additional conditions to claim a conditional exemption, for serious or repeated noncompliance with any requirements of this Subpart N.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 726.460 Reclaiming a Lost Transportation and Disposal Conditional Exemption
     
    a) A generator may reclaim a lost transportation and disposal conditional exemption for a waste after the generator has received a return receipt confirming that the Agency and the Illinois DNS have received the generator’s notification of the loss of the exemption specified in Section 726.455(a) and if the following conditions are fulfilled:
      
    1) The generator again meets the conditions specified in Section 726.415 for the waste; and
    2) The generator sends a notice, by certified delivery, to the Agency that the generator is reclaiming the exemption for the waste. A generator’s notice must be signed by the generator’s authorized representative certifying that the information provided is true, accurate, and complete. The notice must include all of the following:
        
    A) An explanation of the circumstances of each failure;
    B) A certification that each failure that caused the generator to lose the exemption for the waste has been corrected and that the generator again meets all conditions for the waste as of the date the generator specifies;
    C) A description of plans that the generator has implemented, listing the specific steps that the generator has taken, to ensure that conditions will be met in the future; and
    D) Any other information that the generator wants the Agency to consider when the Agency reviews the generator’s notice reclaiming the exemption.
     
    b) The Agency may terminate a reclaimed conditional exemption if it determines, in writing, pursuant to Section 39 of the Act, that the generator’s claim is inappropriate based on factors including, but not limited to, the following: the generator has failed to correct the problem; the generator explained the circumstances of the failure unsatisfactorily; or the generator has failed to implement a plan with steps to prevent another failure to meet the conditions of Section 726.415. In reviewing a reclaimed conditional exemption under this Section, the Agency may add conditions to the exemption to ensure that transportation and disposal activities will protect human health and the environment. Any Agency determination made pursuant to this subsection (b) is subject to review by the Board pursuant to Section 40 of the Act.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     

    TITLE 35: ENVIRONMENTAL PROTECTION

    SUBTITLE G: WASTE DISPOSAL

    CHAPTER I: POLLUTION CONTROL BOARD

    SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS

     

    PART 728

    LAND DISPOSAL RESTRICTIONS

     

    SUBPART A: GENERAL

    Section

     
    728.101 Purpose, Scope, and Applicability
    728.102 Definitions
    728.103 Dilution Prohibited as a Substitute for Treatment
    728.104 Treatment Surface Impoundment Exemption
    728.105 Procedures for case-by-case Extensions to an Effective Date
    728.106 Petitions to Allow Land Disposal of a Waste Prohibited under Subpart C
    728.107 Testing, Tracking, and Recordkeeping Requirements for Generators, Treaters, and Disposal Facilities
    728.108 Landfill and Surface Impoundment Disposal Restrictions (Repealed)
    728.109 Special Rules for Characteristic Wastes

    SUBPART B: SCHEDULE FOR LAND DISPOSAL PROHIBITION AND ESTABLISHMENT OF TREATMENT STANDARDS

    Section

     
    728.110 First Third (Repealed)
    728.111 Second Third (Repealed)
    728.112 Third Third (Repealed)
    728.113 Newly Listed Wastes
    728.114 Surface Impoundment exemptions

    SUBPART C: PROHIBITION ON LAND DISPOSAL

    Section

     
    728.130 Waste Specific Prohibitions -- Wood Preserving Wastes
    728.131 Waste Specific Prohibitions -- Dioxin-Containing Wastes
    728.132 Waste Specific Prohibitions -- Soils Exhibiting the Toxicity Characteristic for Metals and Containing PCBs
    728.133 Waste-Specific Prohibitions -- Chlorinated Aliphatic Wastes
    728.134 Waste-Specific Prohibitions -- Toxicity Characteristic Metal Wastes
    728.135 Waste Specific Prohibitions -- Petroleum Refining Wastes
    728.136 Waste Specific Prohibitions -- Newly Listed Wastes (Repealed) Inorganic Chemical Wastes
    728.137 Waste Specific Prohibitions -- Ignitable and Corrosive Characteristic Wastes Whose Treatment Standards Were Vacated
    728.138 Waste-Specific Prohibitions: Newly-Identified Organic Toxicity Characteristic Wastes and Newly-Listed Coke By-Product and Chlorotoluene Production Wastes
    728.139 Waste-Specific Prohibitions: Spent Aluminum Potliners and Carbamate Wastes

    SUBPART D: TREATMENT STANDARDS

    Section

    728.140 Applicability of Treatment Standards
    728.141 Treatment Standards Expressed as Concentrations in Waste Extract
    728.142 Treatment Standards Expressed as Specified Technologies
    728.143 Treatment Standards Expressed as Waste Concentrations
    728.144 Adjustment of Treatment Standard
    728.145 Treatment Standards for Hazardous Debris
    728.146 Alternative Treatment Standards Based on HTMR
    728.148 Universal Treatment Standards

    728.149  Alternative LDR Treatment Standards for Contaminated Soil

     

    SUBPART E: PROHIBITIONS ON STORAGE

    Section

     
    728.150 Prohibitions on Storage of Restricted Wastes
      
    728.Appendix A Toxicity Characteristic Leaching Procedure (TCLP) (Repealed)
    728.Appendix B Treatment Standards (As concentrations in the Treatment Residual Extract) (Repealed)
    728.Appendix C List of Halogenated Organic Compounds (Repealed) Regulated under Section 728.132
    728.Appendix D Wastes Excluded from Lab Packs
    728.Appendix E Organic Lab Packs (Repealed)
    728.Appendix F Technologies to Achieve Deactivation of Characteristics
    728.Appendix G Federal Effective Dates
    728.Appendix H National Capacity LDR Variances for UIC Wastes
    728.Appendix I EP Toxicity Test Method and Structural Integrity Test
    728.Appendix J Recordkeeping, Notification, and Certification Requirements (Repealed)
    728.Appendix K Metal Bearing Wastes Prohibited From Dilution in a Combustion Unit According to Section 728.103(c)
    728.Table A Constituent Concentrations in Waste Extract (CCWE)
    728.Table B Constituent Concentrations in Wastes (CCW)
    728.Table C Technology Codes and Description of Technology-Based Standards
    728.Table D Technology-Based Standards by RCRA Waste Code
    728.Table E Standards for Radioactive Mixed Waste
    728.Table F Alternative Treatment Standards for Hazardous Debris
    728.Table G Alternative Treatment Standards Based on HTMR
    728.Table H Wastes Excluded from CCW Treatment Standards
    728.Table I Generator Paperwork Requirements
    728.Table T Treatment Standards for Hazardous Wastes
    728.Table U Universal Treatment Standards (UTS)

    AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].

     

    SOURCE: Adopted in R87-5 at 11 Ill. Reg. 19354, effective November 12, 1987; amended in R87-39 at 12 Ill. Reg. 13046, effective July 29, 1988; amended in R89-1 at 13 Ill. Reg. 18403, effective November 13, 1989; amended in R89-9 at 14 Ill. Reg. 6232, effective April 16, 1990; amended in R90-2 at 14 Ill. Reg. 14470, effective August 22, 1990; amended in R90-10 at 14 Ill. Reg. 16508, effective September 25, 1990; amended in R90-11 at 15 Ill. Reg. 9462, effective June 17, 1991; amended 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. 9623, effective June 20, 2000; amended in R01-3 at 25 Ill. Reg. 1296, effective January 11, 2001; amended in R01-21/R01-23 at 25 Ill. Reg. 9181, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. ________, effective ______________________.

     

     

    SUBPART C: PROHIBITION ON LAND DISPOSAL

     

     
    Section 728.134 Waste-Specific Prohibitions -- Toxicity Characteristic Metal Wastes
         
    a) The following wastes are prohibited from land disposal: the wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous waste numbers D004 through D011 that are newly identified (i.e., wastes, soil, or debris identified as hazardous by the Toxic Characteristic Leaching Procedure but not the Extraction Procedure), and waste, soil, or debris from mineral processing operations that is identified as hazardous by the specifications at 35 Ill. Adm. Code 721.
    b) The following waste is prohibited from land disposal: slag from secondary lead smelting that exhibits the characteristic of toxicity due to the presence of one or more metals.
    c) Effective May 26, 2000, the The following wastes are prohibited from land disposal: newly identified characteristic wastes from elemental phosphorus processing; radioactive wastes mixed with USEPA hazardous waste numbers D004 through D011 wastes that are newly identified (i.e., wastes, soil, or debris identified as hazardous by the Toxic Characteristic Leaching Procedure but not the Extraction Procedure); or mixed with newly identified characteristic mineral processing wastes, soil, or debris.
    d) Until May 26, 2000, newly identified characteristic wastes from elemental phosphorus processing, radioactive waste mixed with USEPA hazardous waste numbers D004 through D011 wastes that are newly identified (i.e., wastes, soil, or debris identified as hazardous by the Toxic Characteristic Leaching Procedure but not the Extraction Procedure), or mixed with newly identified characteristic mineral processing wastes, soil, or debris may be disposed in a landfill or surface impoundment only if such unit is in compliance with the requirements specified in Section 728.105(h)(2).This provision corresponds with 40 CFR 269.34(d), which was applicable by its own terms only until May 26, 2000. We have removed this subsection (d), since it no longer applies. This statement maintains structural consistency with the corresponding federal regulations.
    e) The requirements of subsections (a) and (b) of this Section do not apply if any of the following applies to the waste:
        
    1) The wastes meet the applicable treatment standards specified in Subpart D of this Part;
    2) The Board has granted an exemption from a prohibition pursuant to a petition under Section 728.106, with respect to those wastes and units covered by the petition;
    3) The wastes meet the applicable alternate treatment standards established pursuant to a petition granted under Section 728.144; or
    4) USEPA has granted an extension to the effective date of a prohibition pursuant to 40 CFR 268.5, with respect to those wastes covered by the extension.
     
    f) To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards specified in Section 728.140 and Table T of this Part, the initial generator must test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or the waste, or the generator may use knowledge of the waste. If the waste contains constituents (including underlying hazardous constituents in characteristic wastes) in excess of the applicable universal treatment standard levels of Section 728.148 and Table U of this Part, the waste is prohibited from land disposal, and all requirements of this Part are applicable, except as otherwise specified.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 728.136 Waste Specific Prohibitions -- Newly Listed Wastes (Repealed) Inorganic Chemical Wastes
      
    a) Effective May 20, 2002, the wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous wastes numbers K176, K177, and K178, and soil and debris contaminated with these wastes, radioactive wastes mixed with these wastes, and soil and debris contaminated with radioactive wastes mixed with these wastes are prohibited from land disposal.
    b) The requirements of subsection (a) of this Section do not apply if any of the following is true with regard to the waste:
         
    1) The wastes meet the applicable treatment standards specified in Subpart D of this Part;
    2) 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) The wastes meet the applicable treatment standards established pursuant to a petition granted under Section 728.144;
    4) Hazardous debris has met the treatment standards in Sections 728.140 and 728.Table T or the alternative treatment standards in Section 728.145; or
    5) Persons have been granted an extension to the effective date of a prohibition pursuant to Section 728.105, with respect to these wastes covered by the extension.
     
    c) To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards specified in Sections 728.140 and 728.Table T, the initial generator must test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or the waste, or the generator may use knowledge of the waste. If the waste contains regulated constituents in excess of the applicable Subpart D levels, the waste is prohibited from land disposal, and all requirements of this part are applicable, except as otherwise specified.

    (Source: Added at 26 Ill. Reg. ________, effective ______________________)

     

     

    SUBPART D: TREATMENT STANDARDS

     

     
    Section 728.149 Alternative LDR Treatment Standards for Contaminated Soil
     
    a) Applicability. An owner or operator must 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:

    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 contaminated the soil*.

    Apply to the listed waste now.

    The soil is determined to contain the listed waste when the soil is first generated.

    Must comply with LDRs.

    Did not apply to the listed waste when it contaminated the soil*.

    Apply to the listed waste now.

    The soil is determined not 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 contaminated 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:
       
    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, entitled “Universal Treatment Standards,” that are reasonably expected to be present in any given volume of contaminated soil, except fluoride, selenium, sulfides, vanadium, zinc, and that are present at concentrations greater than ten times the universal treatment standard. PCBs are not constituents subject to treatment in any given volume of soil that exhibits the toxicity characteristic solely because of the presence of metals.
    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: Added at 26 Ill. Reg. ________, effective ______________________)

     

     

     
    Section 728.Appendix G
    Federal Effective Dates

    The following are the effective dates for the USEPA rules in 40 CFR 268. These generally became effective as Illinois rules at a later date.

     

    TABLE 1

    EFFECTIVE DATES OF SURFACE DISPOSED WASTES (NON-SOIL AND DEBRIS) REGULATED IN THE LDRSa—COMPREHENSIVE LIST

     

    Waste code

    Waste category

    Effective date

    D001c

    All (except High TOC Ignitable Liquids)

    Aug. 9, 1993.

    D001

    High TOC Ignitable Liquids

    Aug. 8, 1990.

    D002c

    All

    Aug. 9, 1993.

    D003e

    Newly identified surface-disposed elemental phosphorus processing wastes

    May 26, 2000.

    D004

    Newly identified D004 and mineral processing wastes

    Aug. 24, 1998.

    D004

    Mixed radioactive/newly identified D004 or mineral processing wastes

    May 26, 2000.

    D005

    Newly identified D005 and mineral processing wastes

    Aug. 24, 1998.

    D005

    Mixed radioactive/newly identified D005 or mineral processing wastes

    May 26, 2000.

    D006

    Newly identified D006 and mineral processing wastes

    Aug. 24, 1998.

    D006

    Mixed radioactive/newly identified D006 or mineral processing wastes

    May 26, 2000.

    D007

    Newly identified D007 and mineral processing wastes

    Aug. 24, 1998.

    D007

    Mixed radioactive/newly identified D007or mineral processing wastes

    May 26, 2000.

    D008

    Newly identified D008 and mineral processing waste

    Aug. 24, 1998.

    D008

    Mixed radioactive/newly identified D008 or mineral processing wastes

    May 26, 2000.

    D009

    Newly identified D009 and mineral processing waste

    Aug. 24, 1998.

    D009

    Mixed radioactive/newly identified D009or mineral processing wastes

    May 26, 2000.

    D010

    Newly identified D010 and mineral processing wastes

    Aug. 24, 1998.

    D010

    Mixed radioactive/newly identified D010 or mineral processing wastes

    May 26, 2000.

    D011

    Newly identified D011 and mineral processing wastes

    Aug. 24, 1998.

    D011

    Mixed radioactive/newly identified D011or mineral processing wastes

    May 26, 2000.

    D012 (that exhibit the toxicity characteristic based on the TCLP)d

    All

    Dec. 14, 1994.

    D013 (that exhibit the toxicity characteristic based on the TCLP)d

    All

    Dec. 14, 1994.

    D014 (that exhibit the toxicity characteristic based on the TCLP)d

    All

    Dec. 14, 1994.

    D015 (that exhibit the toxicity characteristic based on the TCLP)d

    All

    Dec. 14, 1994.

    D016 (that exhibit the toxicity characteristic based on the TCLP)d

    All

    Dec. 14, 1994.

    D017 (that exhibit the toxicity characteristic based on the TCLP)d

    All

    Dec. 14, 1994.

    D018

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D018

    All others

    Dec. 19, 1994.

    D019

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D019

    All others

    Dec. 19, 1994.

    D020

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D020

    All others

    Dec. 19, 1994.

    D021

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D021

    All others

    Dec. 19, 1994.

    D022

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D022

    All others

    Dec. 19, 1994.

    D023

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D023

    All others

    Dec. 19, 1994.

    D024

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D024

    All others

    Dec. 19, 1994.

    D025

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D025

    All others

    Dec. 19, 1994.

    D026

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D026

    All others

    Dec. 19, 1994.

    D027

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D027

    All others

    Dec. 19, 1994.

    D028

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D028

    All others

    Dec. 19, 1994.

    D029

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D029

    All others

    Dec. 19, 1994.

    D030

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D030

    All others

    Dec. 19, 1994.

    D031

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D031

    All others

    Dec. 19, 1994.

    D032

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D032

    All others

    Dec. 19, 1994.

    D033

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D033

    All others

    Dec. 19, 1994.

    D034

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D034

    All others

    Dec. 19, 1994.

    D035

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D035

    All others

    Dec. 19, 1994.

    D036

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D036

    All others

    Dec. 19, 1994.

    D037

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D037

    All others

    Dec. 19, 1994.

    D038

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D038

    All others

    Dec. 19, 1994.

    D039

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D039

    All others

    Dec. 19, 1994.

    D040

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D040

    All others

    Dec. 19, 1994.

    D041

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D041

    All others

    Dec. 19, 1994.

    D042

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D042

    All others

    Dec. 19, 1994.

    D043

    Mixed with radioactive wastes

    Sep. 19, 1996.

    D043

    All others

    Dec. 19, 1994.

    F001

    Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids

    Nov. 8, 1988.

    F001

    All others

    Nov. 8, 1986.

    F002 (1,1,2-trichloroethane)

    Wastewater and Nonwastewater

    Aug. 8, 1990.

    F002

    Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids

    Nov. 8, 1988.

    F002

    All others

    Nov. 8, 1986.

    F003

    Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids

    Nov. 8, 1988.

    F003

    All others

    Nov. 8, 1986.

    F004

    Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids

    Nov. 8, 1988.

    F004

    All others

    Nov. 8, 1986.

    F005 (benzene, 2-ethoxy ethanol, 2-nitropropane)

    Wastewater and Nonwastewater

    Aug. 8, 1990.

    F005

    Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids

    Nov. 8, 1988.

    F005

    All others

    Nov. 8, 1986.

    F006

    Wastewater

    Aug. 8, 1990.

    F006

    Nonwastewater

    Aug. 8, 1988.

    F006 (cyanides)

    Nonwastewater

    July 8, 1989.

    F007

    All

    July 8, 1989.

    F008

    All

    July 8, 1989.

    F009

    All

    July 8, 1989.

    F010

    All

    June 8, 1989.

    F011 (cyanides)

    Nonwastewater

    Dec. 8, 1989.

    F011

    All others

    July 8, 1989.

    F012 (cyanides)

    Nonwastewater

    Dec. 8, 1989.

    F012

    All others

    July 8, 1989.

    F019

    All

    Aug. 8, 1990.

    F020

    All

    Nov. 8, 1988.

    F021

    All

    Nov. 8, 1988.

    F025

    All

    Aug. 8, 1990.

    F026

    All

    Nov. 8, 1988.

    F027

    All

    Nov. 8, 1988.

    F028

    All

    Nov. 8, 1988.

    F032

    Mixed with radioactive wastes

    May 12, 1999.

    F032

    All others

    Aug. 12, 1997.

    F034

    Mixed with radioactive wastes

    May 12, 1999.

    F034

    All others

    Aug. 12, 1997.

    F035

    Mixed with radioactive wastes

    May 12, 1999.

    F035

    All others

    Aug. 12, 1997.

    F037

    Not generated from surface impoundment cleanouts or closures

    June 30, 1993.

    F037

    Generated from surface impoundment cleanouts or closures

    June 30, 1994.

    F037

    Mixed with radioactive wastes

    June 30, 1994.

    F038

    Not generated from surface impoundment cleanouts or closures

    June 30, 1993.

    F038

    Generated from surface impoundment cleanouts or closures

    June 30, 1994.

    F038

    Mixed with radioactive wastes

    June 30, 1994.

    F039

    Wastewater

    Aug. 8, 1990.

    F039

    Nonwastewater

    May 8, 1992.

    K001 (organics)b

    All

    Aug. 8, 1988.

    K001

    All others

    Aug. 8, 1988.

    K002

    All

    Aug. 8, 1990.

    K003

    All

    Aug. 8, 1990.

    K004

    Wastewater

    Aug. 8, 1990.

    K004

    Nonwastewater

    Aug. 8, 1988.

    K005

    Wastewater

    Aug. 8, 1990.

    K005

    Nonwastewater

    June 8, 1989.

    K006

    All

    Aug. 8, 1990.

    K007

    Wastewater

    Aug. 8, 1990.

    K007

    Nonwastewater

    June 8, 1989.

    K008

    Wastewater

    Aug. 8, 1990.

    K008

    Nonwastewater

    Aug. 8, 1988.

    K009

    All

    June 8, 1989.

    K010

    All

    June 8, 1989.

    K011

    Wastewater

    Aug. 8, 1990.

    K011

    Nonwastewater

    June 8, 1989.

    K013

    Wastewater

    Aug. 8, 1990.

    K013

    Nonwastewater

    June 8, 1989.

    K014

    Wastewater

    Aug. 8, 1990.

    K014

    Nonwastewater

    June 8, 1989.

    K015

    Wastewater

    Aug. 8, 1988.

    K015

    Nonwastewater

    Aug. 8, 1990.

    K016

    All

    Aug. 8, 1988.

    K017

    All

    Aug. 8, 1990.

    K018

    All

    Aug. 8, 1988.

    K019

    All

    Aug. 8, 1988.

    K020

    All

    Aug. 8, 1988.

    K021

    Wastewater

    Aug. 8, 1990.

    K021

    Nonwastewater

    Aug. 8, 1988.

    K022

    Wastewater

    Aug. 8, 1990.

    K022

    Nonwastewater

    Aug. 8, 1988.

    K023

    All

    June 8, 1989.

    K024

    All

    Aug. 8, 1988.

    K025

    Wastewater

    Aug. 8, 1990.

    K025

    Nonwastewater

    Aug. 8, 1988.

    K026

    All

    Aug. 8, 1990.

    K027

    All

    June 8, 1989.

    K028 (metals)

    Nonwastewater

    Aug. 8, 1990.

    K028

    All others

    June 8, 1989.

    K029

    Wastewater

    Aug. 8, 1990.

    K029

    Nonwastewater

    June 8, 1989.

    K030

    All

    Aug. 8, 1988.

    K031

    Wastewater

    Aug. 8, 1990.

    K031

    Nonwastewater

    May 8, 1992.

    K032

    All

    Aug. 8, 1990.

    K033

    All

    Aug. 8, 1990.

    K034

    All

    Aug. 8, 1990.

    K035

    All

    Aug. 8, 1990.

    K036

    Wastewater

    June 8, 1989.

    K036

    Nonwastewater

    Aug. 8, 1988.

    K037b

    Wastewater

    Aug. 8, 1988.

    K037

    Nonwastewater

    Aug. 8, 1988.

    K038

    All

    June 8, 1989.

    K039

    All

    June 8, 1989.

    K040

    All

    June 8, 1989.

    K041

    All

    Aug. 8, 1990.

    K042

    All

    Aug. 8, 1990.

    K043

    All

    June 8, 1989.

    K044

    All

    Aug. 8, 1988.

    K045

    All

    Aug. 8, 1988.

    K046 (Nonreactive)

    Nonwastewater

    Aug. 8, 1988.

    K046

    All others

    Aug. 8, 1990.

    K047

    All

    Aug. 8, 1988.

    K048

    Wastewater

    Aug. 8, 1990.

    K048

    Nonwastewater

    Nov. 8, 1990.

    K049

    Wastewater

    Aug. 8, 1990.

    K049

    Nonwastewater

    Nov. 8, 1990.

    K050

    Wastewater

    Aug. 8, 1990.

    K050

    Nonwastewater

    Nov. 8, 1990.

    K051

    Wastewater

    Aug. 8, 1990.

    K051

    Nonwastewater

    Nov. 8, 1990.

    K052

    Wastewater

    Aug. 8, 1990.

    K052

    Nonwastewater

    Nov. 8, 1990.

    K060

    Wastewater

    Aug. 8, 1990.

    K060

    Nonwastewater

    Aug. 8, 1988.

    K061

    Wastewater

    Aug. 8, 1990.

    K061

    Nonwastewater

    June 30, 1992.

    K062

    All

    Aug. 8, 1988.

    K069 (Non-Calcium Sulfate)

    Nonwastewater

    Aug. 8, 1988.

    K069

    All others

    Aug. 8, 1990.

    K071

    All

    Aug. 8, 1990.

    K073

    All

    Aug. 8, 1990.

    K083

    All

    Aug. 8, 1990.

    K084

    Wastewater

    Aug. 8, 1990.

    K084

    Nonwastewater

    May 8, 1992.

    K085

    All

    Aug. 8, 1990.

    K086 (organics)b

    All

    Aug. 8, 1988.

    K086

    All others

    Aug. 8, 1988.

    K087

    All

    Aug. 8, 1988.

    K088

    Mixed with radioactive wastes

    Apr. 8, 1998.

    K088

    All others

    Oct. 8, 1997.

    K093

    All

    June 8, 1989.

    K094

    All

    June 8, 1989.

    K095

    Wastewater

    Aug. 8, 1990.

    K095

    Nonwastewater

    June 8, 1989.

    K096

    Wastewater

    Aug. 8, 1990.

    K096

    Nonwastewater

    June 8, 1989.

    K097

    All

    Aug. 8, 1990.

    K098

    All

    Aug. 8, 1990.

    K099

    All

    Aug. 8, 1988.

    K100

    Wastewater

    Aug. 8, 1990.

    K100

    Nonwastewater

    Aug. 8, 1988.

    K101 (organics)

    Wastewater

    Aug. 8, 1988.

    K101 (metals)

    Wastewater

    Aug. 8, 1990.

    K101 (organics)

    Nonwastewater

    Aug. 8, 1988.

    K101 (metals)

    Nonwastewater

    May 8, 1992.

    K102 (organics)

    Wastewater

    Aug. 8, 1988.

    K102 (metals)

    Wastewater

    Aug. 8, 1990.

    K102 (organics)

    Nonwastewater

    Aug. 8, 1988.

    K102 (metals)

    Nonwastewater

    May 8, 1992.

    K103

    All

    Aug. 8, 1988.

    K104

    All

    Aug. 8, 1988.

    K105

    All

    Aug. 8, 1990.

    K106

    Wastewater

    Aug. 8, 1990.

    K106

    Nonwastewater

    May 8, 1992.

    K107

    Mixed with radioactive wastes

    June 30, 1994.

    K107

    All others

    Nov. 9, 1992.

    K108

    Mixed with radioactive wastes

    June 30, 1994.

    K108

    All others

    Nov. 9, 1992.

    K109

    Mixed with radioactive wastes

    June 30, 1994.

    K109

    All others

    Nov. 9, 1992.

    K110

    Mixed with radioactive wastes

    June 30, 1994.

    K110

    All others

    Nov. 9, 1992.

    K111

    Mixed with radioactive wastes

    June 30, 1994.

    K111

    All others

    Nov. 9, 1992.

    K112

    Mixed with radioactive wastes

    June 30, 1994.

    K112

    All others

    Nov. 9, 1992.

    K113

    All

    June 8, 1989.

    K114

    All

    June 8, 1989.

    K115

    All

    June 8, 1989.

    K116

    All

    June 8, 1989.

    K117

    Mixed with radioactive wastes

    June 30, 1994.

    K117

    All others

    Nov. 9, 1992.

    K118

    Mixed with radioactive wastes

    June 30, 1994.

    K118

    All others

    Nov. 9, 1992.

    K123

    Mixed with radioactive wastes

    June 30, 1994.

    K123

    All others

    Nov. 9, 1992.

    K124

    Mixed with radioactive wastes

    June 30, 1994.

    K124

    All others

    Nov. 9, 1992.

    K125

    Mixed with radioactive wastes

    June 30, 1994.

    K125

    All others

    Nov. 9, 1992.

    K126

    Mixed with radioactive wastes

    June 30, 1994.

    K126

    All others

    Nov. 9, 1992.

    K131

    Mixed with radioactive wastes

    June 30, 1994.

    K131

    All others

    Nov. 9, 1992.

    K132

    Mixed with radioactive wastes

    June 30, 1994.

    K132

    All others

    Nov. 9, 1992.

    K136

    Mixed with radioactive wastes

    June 30, 1994.

    K136

    All others

    Nov. 9, 1992.

    K141

    Mixed with radioactive wastes

    Sep. 19, 1996.

    K141

    All others

    Dec. 19, 1994.

    K142

    Mixed with radioactive wastes

    Sep. 19, 1996.

    K142

    All others

    Dec. 19, 1994.

    K143

    Mixed with radioactive wastes

    Sep. 19, 1996.

    K143

    All others

    Dec. 19, 1994.

    K144

    Mixed with radioactive wastes

    Sep. 19, 1996.

    K144

    All others

    Dec. 19, 1994.

    K145

    Mixed with radioactive wastes

    Sep. 19, 1996.

    K145

    All others

    Dec. 19, 1994.

    K147

    Mixed with radioactive wastes

    Sep. 19, 1996.

    K147

    All others

    Dec. 19, 1994.

    K148

    Mixed with radioactive wastes

    Sep. 19, 1996.

    K148

    All others

    Dec. 19, 1994.

    K149

    Mixed with radioactive wastes

    Sep. 19, 1996.

    K149

    All others

    Dec. 19, 1994.

    K150

    Mixed with radioactive wastes

    Sep. 19, 1996.

    K150

    All others

    Dec. 19, 1994.

    K151

    Mixed with radioactive wastes

    Sep. 19, 1996.

    K151

    All others

    Dec. 19, 1994.

    K156

    Mixed with radioactive wastes

    Apr. 8, 1998.

    K156

    All others

    July 8, 1996.

    K157

    Mixed with radioactive wastes

    Apr. 8, 1998.

    K157

    All others

    July 8, 1996.

    K158

    Mixed with radioactive wastes

    Apr. 8, 1998.

    K158

    All others

    July 8, 1996.

    K159

    Mixed with radioactive wastes

    Apr. 8, 1998.

    K159

    All others

    July 8, 1996.

    K160

    Mixed with radioactive wastes

    Apr. 8, 1998.

    K160

    All others

    July 8, 1996.

    K161

    Mixed with radioactive wastes

    Apr. 8, 1998.

    K161

    All others

    July 8, 1996.

    P001

    All

    Aug. 8, 1990.

    P002

    All

    Aug. 8, 1990.

    P003

    All

    Aug. 8, 1990.

    P004

    All

    Aug. 8, 1990.

    P005

    All

    Aug. 8, 1990.

    P006

    All

    Aug. 8, 1990.

    P007

    All

    Aug. 8, 1990.

    P008

    All

    Aug. 8, 1990.

    P009

    All

    Aug. 8, 1990.

    P010

    Wastewater

    Aug. 8, 1990.

    P010

    Nonwastewater

    May 8, 1992.

    P011

    Wastewater

    Aug. 8, 1990.

    P011

    Nonwastewater

    May 8, 1992.

    P012

    Wastewater

    Aug. 8, 1990.

    P012

    Nonwastewater

    May 8, 1992.

    P013 (barium)

    Nonwastewater

    Aug. 8, 1990.

    P013

    All others

    June 8, 1989.

    P014

    All

    Aug. 8, 1990.

    P015

    All

    Aug. 8, 1990.

    P016

    All

    Aug. 8, 1990.

    P017

    All

    Aug. 8, 1990.

    P018

    All

    Aug. 8, 1990.

    P020

    All

    Aug. 8, 1990.

    P021

    All

    June 8, 1989.

    P022

    All

    Aug. 8, 1990.

    P023

    All

    Aug. 8, 1990.

    P024

    All

    Aug. 8, 1990.

    P026

    All

    Aug. 8, 1990.

    P027

    All

    Aug. 8, 1990.

    P028

    All

    Aug. 8, 1990.

    P029

    All

    June 8, 1989.

    P030

    All

    June 8, 1989.

    P031

    All

    Aug. 8, 1990.

    P033

    All

    Aug. 8, 1990.

    P034

    All

    Aug. 8, 1990.

    P036

    Wastewater

    Aug. 8, 1990.

    P036

    Nonwastewater

    May 8, 1992.

    P037

    All

    Aug. 8, 1990.

    P038

    Wastewater

    Aug. 8, 1990.

    P038

    Nonwastewater

    May 8, 1992.

    P039

    All

    June 8, 1989.

    P040

    All

    June 8, 1989.

    P041

    All

    June 8, 1989.

    P042

    All

    Aug. 8, 1990.

    P043

    All

    June 8, 1989.

    P044

    All

    June 8, 1989.

    P045

    All

    Aug. 8, 1990.

    P046

    All

    Aug. 8, 1990.

    P047

    All

    Aug. 8, 1990.

    P048

    All

    Aug. 8, 1990.

    P049

    All

    Aug. 8, 1990.

    P050

    All

    Aug. 8, 1990.

    P051

    All

    Aug. 8, 1990.

    P054

    All

    Aug. 8, 1990.

    P056

    All

    Aug. 8, 1990.

    P057

    All

    Aug. 8, 1990.

    P058

    All

    Aug. 8, 1990.

    P059

    All

    Aug. 8, 1990.

    P060

    All

    Aug. 8, 1990.

    P062

    All

    June 8, 1989.

    P063

    All

    June 8, 1989.

    P064

    All

    Aug. 8, 1990.

    P065

    Wastewater

    Aug. 8, 1990.

    P065

    Nonwastewater

    May 8, 1992.

    P066

    All

    Aug. 8, 1990.

    P067

    All

    Aug. 8, 1990.

    P068

    All

    Aug. 8, 1990.

    P069

    All

    Aug. 8, 1990.

    P070

    All

    Aug. 8, 1990.

    P071

    All

    June 8, 1989.

    P072

    All

    Aug. 8, 1990.

    P073

    All

    Aug. 8, 1990.

    P074

    All

    June 8, 1989.

    P075

    All

    Aug. 8, 1990.

    P076

    All

    Aug. 8, 1990.

    P077

    All

    Aug. 8, 1990.

    P078

    All

    Aug. 8, 1990.

    P081

    All

    Aug. 8, 1990.

    P082

    All

    Aug. 8, 1990.

    P084

    All

    Aug. 8, 1990.

    P085

    All

    June 8, 1989.

    P087

    All

    May 8, 1992.

    P088

    All

    Aug. 8, 1990.

    P089

    All

    June 8, 1989.

    P092

    Wastewater

    Aug. 8, 1990.

    P092

    Nonwastewater

    May 8, 1992.

    P093

    All

    Aug. 8, 1990.

    P094

    All

    June 8, 1989.

    P095

    All

    Aug. 8, 1990.

    P096

    All

    Aug. 8, 1990.

    P097

    All

    June 8, 1989.

    P098

    All

    June 8, 1989.

    P099 (silver)

    Wastewater

    Aug. 8, 1990.

    P099

    All others

    June 8, 1989.

    P101

    All

    Aug. 8, 1990.

    P102

    All

    Aug. 8, 1990.

    P103

    All

    Aug. 8, 1990.

    P104 (silver)

    Wastewater

    Aug. 8, 1990.

    P104

    All others

    June 8, 1989.

    P105

    All

    Aug. 8, 1990.

    P106

    All

    June 8, 1989.

    P108

    All

    Aug. 8, 1990.

    P109

    All

    June 8, 1989.

    P110

    All

    Aug. 8, 1990.

    P111

    All

    June 8, 1989.

    P112

    All

    Aug. 8, 1990.

    P113

    All

    Aug. 8, 1990.

    P114

    All

    Aug. 8, 1990.

    P115

    All

    Aug. 8, 1990.

    P116

    All

    Aug. 8, 1990.

    P118

    All

    Aug. 8, 1990.

    P119

    All

    Aug. 8, 1990.

    P120

    All

    Aug. 8, 1990.

    P121

    All

    June 8, 1989.

    P122

    All

    Aug. 8, 1990.

    P123

    All

    Aug. 8, 1990.

    P127

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P127

    All others

    July 8, 1996.

    P128

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P128

    All others

    July 8, 1996.

    P185

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P185

    All others

    July 8, 1996.

    P188

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P188

    All others

    July 8, 1996.

    P189

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P189

    All others

    July 8, 1996.

    P190

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P190

    All others

    July 8, 1996.

    P191

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P191

    All others

    July 8, 1996.

    P192

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P192

    All others

    July 8, 1996.

    P194

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P194

    All others

    July 8, 1996.

    P196

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P196

    All others

    July 8, 1996.

    P197

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P197

    All others

    July 8, 1996.

    P198

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P198

    All others

    July 8, 1996.

    P199

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P199

    All others

    July 8, 1996.

    P201

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P201

    All others

    July 8, 1996.

    P202

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P202

    All others

    July 8, 1996.

    P203

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P203

    All others

    July 8, 1996.

    P204

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P204

    All others

    July 8, 1996.

    P205

    Mixed with radioactive wastes

    Apr. 8, 1998.

    P205

    All others

    July 8, 1996.

    U001

    All

    Aug. 8, 1990.

    U002

    All

    Aug. 8, 1990.

    U003

    All

    Aug. 8, 1990.

    U004

    All

    Aug. 8, 1990.

    U005

    All

    Aug. 8, 1990.

    U006

    All

    Aug. 8, 1990.

    U007

    All

    Aug. 8, 1990.

    U008

    All

    Aug. 8, 1990.

    U009

    All

    Aug. 8, 1990.

    U010

    All

    Aug. 8, 1990.

    U011

    All

    Aug. 8, 1990.

    U012

    All

    Aug. 8, 1990.

    U014

    All

    Aug. 8, 1990.

    U015

    All

    Aug. 8, 1990.

    U016

    All

    Aug. 8, 1990.

    U017

    All

    Aug. 8, 1990.

    U018

    All

    Aug. 8, 1990.

    U019

    All

    Aug. 8, 1990.

    U020

    All

    Aug. 8, 1990.

    U021

    All

    Aug. 8, 1990.

    U022

    All

    Aug. 8, 1990.

    U023

    All

    Aug. 8, 1990.

    U024

    All

    Aug. 8, 1990.

    U025

    All

    Aug. 8, 1990.

    U026

    All

    Aug. 8, 1990.

    U027

    All

    Aug. 8, 1990.

    U028

    All

    June 8, 1989.

    U029

    All

    Aug. 8, 1990.

    U030

    All

    Aug. 8, 1990.

    U031

    All

    Aug. 8, 1990.

    U032

    All

    Aug. 8, 1990.

    U033

    All

    Aug. 8, 1990.

    U034

    All

    Aug. 8, 1990.

    U035

    All

    Aug. 8, 1990.

    U036

    All

    Aug. 8, 1990.

    U037

    All

    Aug. 8, 1990.

    U038

    All

    Aug. 8, 1990.

    U039

    All

    Aug. 8, 1990.

    U041

    All

    Aug. 8, 1990.

    U042

    All

    Aug. 8, 1990.

    U043

    All

    Aug. 8, 1990.

    U044

    All

    Aug. 8, 1990.

    U045

    All

    Aug. 8, 1990.

    U046

    All

    Aug. 8, 1990.

    U047

    All

    Aug. 8, 1990.

    U048

    All

    Aug. 8, 1990.

    U049

    All

    Aug. 8, 1990.

    U050

    All

    Aug. 8, 1990.

    U051

    All

    Aug. 8, 1990.

    U052

    All

    Aug. 8, 1990.

    U053

    All

    Aug. 8, 1990.

    U055

    All

    Aug. 8, 1990.

    U056

    All

    Aug. 8, 1990.

    U057

    All

    Aug. 8, 1990.

    U058

    All

    June 8, 1989.

    U059

    All

    Aug. 8, 1990.

    U060

    All

    Aug. 8, 1990.

    U061

    All

    Aug. 8, 1990.

    U062

    All

    Aug. 8, 1990.

    U063

    All

    Aug. 8, 1990.

    U064

    All

    Aug. 8, 1990.

    U066

    All

    Aug. 8, 1990.

    U067

    All

    Aug. 8, 1990.

    U068

    All

    Aug. 8, 1990.

    U069

    All

    June 30, 1992.

    U070

    All

    Aug. 8, 1990.

    U071

    All

    Aug. 8, 1990.

    U072

    All

    Aug. 8, 1990.

    U073

    All

    Aug. 8, 1990.

    U074

    All

    Aug. 8, 1990.

    U075

    All

    Aug. 8, 1990.

    U076

    All

    Aug. 8, 1990.

    U077

    All

    Aug. 8, 1990.

    U078

    All

    Aug. 8, 1990.

    U079

    All

    Aug. 8, 1990.

    U080

    All

    Aug. 8, 1990.

    U081

    All

    Aug. 8, 1990.

    U082

    All

    Aug. 8, 1990.

    U083

    All

    Aug. 8, 1990.

    U084

    All

    Aug. 8, 1990.

    U085

    All

    Aug. 8, 1990.

    U086

    All

    Aug. 8, 1990.

    U087

    All

    June 8, 1989.

    U088

    All

    June 8, 1989.

    U089

    All

    Aug. 8, 1990.

    U090

    All

    Aug. 8, 1990.

    U091

    All

    Aug. 8, 1990.

    U092

    All

    Aug. 8, 1990.

    U093

    All

    Aug. 8, 1990.

    U094

    All

    Aug. 8, 1990.

    U095

    All

    Aug. 8, 1990.

    U096

    All

    Aug. 8, 1990.

    U097

    All

    Aug. 8, 1990.

    U098

    All

    Aug. 8, 1990.

    U099

    All

    Aug. 8, 1990.

    U101

    All

    Aug. 8, 1990.

    U102

    All

    June 8, 1989.

    U103

    All

    Aug. 8, 1990.

    U105

    All

    Aug. 8, 1990.

    U106

    All

    Aug. 8, 1990.

    U107

    All

    June 8, 1989.

    U108

    All

    Aug. 8, 1990.

    U109

    All

    Aug. 8, 1990.

    U110

    All

    Aug. 8, 1990.

    U111

    All

    Aug. 8, 1990.

    U112

    All

    Aug. 8, 1990.

    U113

    All

    Aug. 8, 1990.

    U114

    All

    Aug. 8, 1990.

    U115

    All

    Aug. 8, 1990.

    U116

    All

    Aug. 8, 1990.

    U117

    All

    Aug. 8, 1990.

    U118

    All

    Aug. 8, 1990.

    U119

    All

    Aug. 8, 1990.

    U120

    All

    Aug. 8, 1990.

    U121

    All

    Aug. 8, 1990.

    U122

    All

    Aug. 8, 1990.

    U123

    All

    Aug. 8, 1990.

    U124

    All

    Aug. 8, 1990.

    U125

    All

    Aug. 8, 1990.

    U126

    All

    Aug. 8, 1990.

    U127

    All

    Aug. 8, 1990.

    U128

    All

    Aug. 8, 1990.

    U129

    All

    Aug. 8, 1990.

    U130

    All

    Aug. 8, 1990.

    U131

    All

    Aug. 8, 1990.

    U132

    All

    Aug. 8, 1990.

    U133

    All

    Aug. 8, 1990.

    U134

    All

    Aug. 8, 1990.

    U135

    All

    Aug. 8, 1990.

    U136

    Wastewater

    Aug. 8, 1990.

    U136

    Nonwastewater

    May 8, 1992.

    U137

    All

    Aug. 8, 1990.

    U138

    All

    Aug. 8, 1990.

    U140

    All

    Aug. 8, 1990.

    U141

    All

    Aug. 8, 1990.

    U142

    All

    Aug. 8, 1990.

    U143

    All

    Aug. 8, 1990.

    U144

    All

    Aug. 8, 1990.

    U145

    All

    Aug. 8, 1990.

    U146

    All

    Aug. 8, 1990.

    U147

    All

    Aug. 8, 1990.

    U148

    All

    Aug. 8, 1990.

    U149

    All

    Aug. 8, 1990.

    U150

    All

    Aug. 8, 1990.

    U151

    Wastewater

    Aug. 8, 1990.

    U151

    Nonwastewater

    May 8, 1992.

    U152

    All

    Aug. 8, 1990.

    U153

    All

    Aug. 8, 1990.

    U154

    All

    Aug. 8, 1990.

    U155

    All

    Aug. 8, 1990.

    U156

    All

    Aug. 8, 1990.

    U157

    All

    Aug. 8, 1990.

    U158

    All

    Aug. 8, 1990.

    U159

    All

    Aug. 8, 1990.

    U160

    All

    Aug. 8, 1990.

    U161

    All

    Aug. 8, 1990.

    U162

    All

    Aug. 8, 1990.

    U163

    All

    Aug. 8, 1990.

    U164

    All

    Aug. 8, 1990.

    U165

    All

    Aug. 8, 1990.

    U166

    All

    Aug. 8, 1990.

    U167

    All

    Aug. 8, 1990.

    U168

    All

    Aug. 8, 1990.

    U169

    All

    Aug. 8, 1990.

    U170

    All

    Aug. 8, 1990.

    U171

    All

    Aug. 8, 1990.

    U172

    All

    Aug. 8, 1990.

    U173

    All

    Aug. 8, 1990.

    U174

    All

    Aug. 8, 1990.

    U176

    All

    Aug. 8, 1990.

    U177

    All

    Aug. 8, 1990.

    U178

    All

    Aug. 8, 1990.

    U179

    All

    Aug. 8, 1990.

    U180

    All

    Aug. 8, 1990.

    U181

    All

    Aug. 8, 1990.

    U182

    All

    Aug. 8, 1990.

    U183

    All

    Aug. 8, 1990.

    U184

    All

    Aug. 8, 1990.

    U185

    All

    Aug. 8, 1990.

    U186

    All

    Aug. 8, 1990.

    U187

    All

    Aug. 8, 1990.

    U188

    All

    Aug. 8, 1990.

    U189

    All

    Aug. 8, 1990.

    U190

    All

    June 8, 1989.

    U191

    All

    Aug. 8, 1990.

    U192

    All

    Aug. 8, 1990.

    U193

    All

    Aug. 8, 1990.

    U194

    All

    June 8, 1989.

    U196

    All

    Aug. 8, 1990.

    U197

    All

    Aug. 8, 1990.

    U200

    All

    Aug. 8, 1990.

    U201

    All

    Aug. 8, 1990.

    U202

    All

    Aug. 8, 1990.

    U203

    All

    Aug. 8, 1990.

    U204

    All

    Aug. 8, 1990.

    U205

    All

    Aug. 8, 1990.

    U206

    All

    Aug. 8, 1990.

    U207

    All

    Aug. 8, 1990.

    U208

    All

    Aug. 8, 1990.

    U209

    All

    Aug. 8, 1990.

    U210

    All

    Aug. 8, 1990.

    U211

    All

    Aug. 8, 1990.

    U213

    All

    Aug. 8, 1990.

    U214

    All

    Aug. 8, 1990.

    U215

    All

    Aug. 8, 1990.

    U216

    All

    Aug. 8, 1990.

    U217

    All

    Aug. 8, 1990.

    U218

    All

    Aug. 8, 1990.

    U219

    All

    Aug. 8, 1990.

    U220

    All

    Aug. 8, 1990.

    U221

    All

    June 8, 1989.

    U222

    All

    Aug. 8, 1990.

    U223

    All

    June 8, 1989.

    U225

    All

    Aug. 8, 1990.

    U226

    All

    Aug. 8, 1990.

    U227

    All

    Aug. 8, 1990.

    U228

    All

    Aug. 8, 1990.

    U234

    All

    Aug. 8, 1990.

    U235

    All

    June 8, 1989.

    U236

    All

    Aug. 8, 1990.

    U237

    All

    Aug. 8, 1990.

    U238

    All

    Aug. 8, 1990.

    U239

    All

    Aug. 8, 1990.

    U240

    All

    Aug. 8, 1990.

    U243

    All

    Aug. 8, 1990.

    U244

    All

    Aug. 8, 1990.

    U246

    All

    Aug. 8, 1990.

    U247

    All

    Aug. 8, 1990.

    U248

    All

    Aug. 8, 1990.

    U249

    All

    Aug. 8, 1990.

    U271

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U271

    All others

    July 8, 1996.

    U277

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U277

    All others

    July 8, 1996.

    U278

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U278

    All others

    July 8, 1996.

    U279

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U279

    All others

    July 8, 1996.

    U280

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U280

    All others

    July 8, 1996.

    U328

    Mixed with radioactive wastes

    June 30, 1994.

    U328

    All others

    Nov. 9, 1992.

    U353

    Mixed with radioactive wastes

    June 30, 1994.

    U353

    All others

    Nov. 9, 1992.

    U359

    Mixed with radioactive wastes

    June 30, 1994.

    U359

    All others

    Nov. 9, 1992.

    U364

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U364

    All others

    July 8, 1996.

    U365

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U365

    All others

    July 8, 1996.

    U366

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U366

    All others

    July 8, 1996.

    U367

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U367

    All others

    July 8, 1996.

    U372

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U372

    All others

    July 8, 1996.

    U373

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U373

    All others

    July 8, 1996.

    U375

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U375

    All others

    July 8, 1996.

    U376

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U376

    All others

    July 8, 1996.

    U377

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U377

    All others

    July 8, 1996.

    U378

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U378

    All others

    July 8, 1996.

    U379

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U379

    All others

    July 8, 1996.

    U381

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U381

    All others

    July 8, 1996.

    U382

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U382

    All others

    July 8, 1996.

    U383

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U383

    All others

    July 8, 1996.

    U384

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U384

    All others

    July 8, 1996.

    U385

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U385

    All others

    July 8, 1996.

    U386

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U386

    All others

    July 8, 1996.

    U387

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U387

    All others

    July 8, 1996.

    U389

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U389

    All others

    July 8, 1996.

    U390

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U390

    All others

    July 8, 1996.

    U391

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U391

    All others

    July 8, 1996.

    U392

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U392

    All others

    July 8, 1996.

    U393

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U393

    All others

    July 8, 1996.

    U394

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U394

    All others

    July 8, 1996.

    U395

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U395

    All others

    July 8, 1996.

    U396

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U396

    All others

    July 8, 1996.

    U400

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U400

    All others

    July 8, 1996.

    U401

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U401

    All others

    July 8, 1996.

    U402

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U402

    All others

    July 8, 1996.

    U403

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U403

    All others

    July 8, 1996.

    U404

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U404

    All others

    July 8, 1996.

    U407

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U407

    All others

    July 8, 1996.

    U409

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U409

    All others

    July 8, 1996.

    U410

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U410

    All others

    July 8, 1996.

    U411

    Mixed with radioactive wastes

    Apr. 8, 1998.

    U411

    All others

    July 8, 1996.

     

     
    a This table does not include mixed radioactive wastes (from the First, Second, and Third rules) which are receiving a national capacity variance until May 8, 1992. This table also does not include contaminated soil and debris wastes.
     
    b The standard was revised in the Third Third Final Rule (adopted by USEPA at 55 Fed. Reg. 22520 (June 1, 1990) and by the Board in docket R90-11 by orders dated April 11, May 23, and August 8 and 22, 1991).
     
    c USEPA amended the standard in the Third Third Emergency Rule (at 58 Fed. Reg. 29860 (May 24, 1993), which the Board adopted in docket R93-16 on March 17, 1994); the original effective date was August 8, 1990.
     
    d The standard was revised in the Phase II Final Rule (which USEPA adopted at 59 Fed. Reg. 47982 (Sept. 19, 1994) and the Board adopted in docket R95-6 by orders dated June 1 and 15, 1995); the original effective date was August 8, 1990.
     
    e The standards for selected reactive wastes was revised in the Phase III Final Rule (which USEPA adopted at 61 Fed. Reg. 15566 (Apr. 8, 1996) and the Board adopted in docket R96-10/R97-3/R97-5 (consolidated) by an order dated November 6, 1997); the original effective date was August 8, 1990.

    TABLE 2

    SUMMARY OF EFFECTIVE DATES OF LAND DISPOSAL RESTRICTIONS FOR CONTAMINATED SOIL AND DEBRIS (CSD)

     

    Restricted hazardous waste in CSD

    Effective date

    1.  Solvent-(F001-F005) and dioxin-(F020-F023 and F026-F028) containing soil and debris from CERCLA response or RCRA corrective actions.

    Nov. 8, 1990.

    2.  Soil and debris not from CERCLA response or RCRA corrective actions contaminated with less than one percent total solvents (F001-F005) or dioxins (F020-F023 and F026-F028).

    Nov. 8, 1988.

    3.  All soil and debris contaminated with First Third wastes for which treatment standards are based on incineration.

    Aug. 8, 1990.

    4.  All soil and debris contaminated with Second Third wastes for which treatment standards are based on incineration.

    June 8, 1991.

    5.  All soil and debris contaminated with Third Third wastes or, First or Second Third “soft hammer” wastes which had treatment standards promulgated in the Third Third rule, for which treatment standards are based on incineration, vitrification, or mercury retorting, acid leaching followed by chemical precipitation, or thermal recovery of metals, as well as all inorganic solids debris contaminated with D004-D011 wastes, and all soil and debris contaminated with mixed RCRA/radioactive wastes.

    May 8, 1992.

    6.  Soil and debris contaminated with D012-D043, K141-K145, and K147-151 wastes.

    Dec. 19, 1994.

    7.  Debris (only) contaminated with F037, F038, K107-K112, K117, K118, K123-K126, K131, K132, K136, U328, U353, U359.

    Dec. 19, 1994

    8.  Soil and debris contaminated with K156- K161, P127, P128, P188-P192, P194, P196- P199, P201-P205, U271, U277-U280, U364-U367, U372, U373, U375-U379, U381-U387, U389-U396, U400-U404, U407, and U409-U411 wastes.

    July 8, 1996.

    9.  Soil and debris contaminated with K088 wastes.

    Oct. 8, 1997.

    10.  Soil and debris contaminated with radioactive wastes mixed with K088, K156-K161, P127, P128, P188-P192, P194, P196-P199, P201-P205, U271, U277-U280, U364-U367, U372, U373, U375-U379, U381-U387, U389-U396, U400-U404, U407, and U409-U411 wastes.

     

    April 8, 1998.

    11.  Soil and debris contaminated with F032, F034, and F035.

    May 12, 1997.

    12.  Soil and debris contaminated with newly identified D004-D011 toxicity characteristic wastes and mineral processing wastes.

    Aug. 24, 1998.

    13.  Soil and debris contaminated with mixed radioactive newly identified D011 characteristic wastes and mineral processing wastes.

    May 26, 2000.

     

    BOARD NOTE: This table is provided for the convenience of the reader.

     

    (Source: Amended at 26 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 Subcategory1

    Regulated Hazardous Constituent

    Wastewaters

    Nonwastewaters

     

     

     

     

    Common Name

     

     

     

     

    CAS2 Number

     

     

    Concentration in mg/l3; or Technology Code4

    Concentration in mg/kg5 unless noted as “mg/l TCLP”; or Technology Code4

     

    D0019

    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 standards8; or RORGS; or CMBST

    DEACT and meet Section 728.148 standards8; or RORGS; or CMBST

     

    D0019

    High TOC Ignitable Characteristic Liquids Subcategory based on 35 Ill. Adm. Code 721.121(a)(1) - Greater than or equal to 10 percent total organic carbon.

    (Note: This subcategory consists of nonwastewaters only.)

    NA

    NA

    NA

    RORGS; CMBST; or POLYM

     

    D0029

    Corrosive Characteristic Wastes.

    NA

    NA

    DEACT and meet Section 728.148 standards8

    DEACT and meet Section 728.148 standards8

     

    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

     

    D0039

    Reactive Sulfides Subcategory based on 35 Ill. Adm. Code 721.123(a)(5).

    NA

    NA

    DEACT

    DEACT

     

    D0039

    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 standards8

    DEACT and meet Section 728.148 standards8

     

    D0039

    Unexploded ordnance and other explosive devices that have been the subject of an emergency response.

    NA

    NA

    DEACT

    DEACT

     

    D0039

    Other Reactives Subcategory based on 35 Ill. Adm. Code 721.123(a)(1).

    NA

    NA

    DEACT and meet Section 728.148 standards8

    DEACT and meet Section 728.148 standards8

     

    D0039

    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 standards8

     

    D0039

    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

     

    D0049

    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 standards8

    5.0 mg/l TCLP and meet Section 728.148 standards8

     

    D0059

    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 standards8

    21 mg/l TCLP and meet Section 728.148 standards8

     

    D0069

    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 standards8

    0.11 mg/l TCLP and meet Section 728.148 standards8

     

    D0069

    Cadmium-Containing Batteries Subcategory

    (Note: This subcategory consists of nonwastewaters only.)

    Cadmium

    7440-43-9

    NA

    RTHRM

     

    D0079

    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 standards8

    0.60 mg/l TCLP and meet Section 728.148 standards8

     

    D0089

    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 standards8

    0.75 mg/l TCLP and meet Section 728.148 standards8

     

    D0089

    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

     

    D0089

    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

     

    D0099

    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

     

    D0099

    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

     

    D0099

    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 standards8

     

    D0099

    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 standards8

     

    D0099

    All D009 wastewaters.

    Mercury

    7439-97-6

    0.15 and meet Section 728.148 standards8

    NA

     

    D0099

    Elemental mercury contaminated with radioactive materials.

    (Note: This subcategory consists of nonwastewaters only.)

    Mercury

    7439-97-6

    NA

    AMLGM

     

    D0099

    Hydraulic oil contaminated with Mercury Radioactive Materials Subcategory.

    (Note: This subcategory consists of nonwastewaters only.)

    Mercury

    7439-97-6

    NA

    IMERC

     

    D0109

    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 standards8

     

    D0119

    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 standards8

     

    D0129

    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 standards8

    Endrin aldehyde

    7421-93-4

    BIODG; or CMBST

    0.13 and meet Section 728.148 standards8

     

    D0139

    Wastes that are TC for Lindane based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.

    a -BHC

    319-84-6

    CARBN; or CMBST

    0.066 and meet Section 728.148 standards8

    b -BHC

    319-85-7

    CARBN; or CMBST

    0.066 and meet Section 728.148 standards8

    d -BHC

    319-86-8

    CARBN; or CMBST

    0.066 and meet Section 728.148 standards8

    c -BHC g -BHC (Lindane)

    58-89-9

    CARBN; or CMBST

    0.066 and meet Section 728.148 standards8

     

    D0149

    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 standards8

     

    D0159

    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 standards8

     

    D0169

    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-Dichlorophenoxyacetic acid)

    94-75-7

    CHOXD; BIODG; or CMBST

    10 and meet Section 728.148 standards8

     

    D0179

    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 standards8

     

    D0189

    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 standards8

    10 and meet Section 728.148 standards8

     

    D0199

    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 standards8

    6.0 and meet Section 728.148 standards8

     

    D0209

    Wastes that are TC for Chlordane based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.

    Chlordane ( a and c isomers)

    57-74-9

    0.0033 and meet Section 728.148 standards8

    0.26 and meet Section 728.148 standards8

     

    D0219

    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 standards8

    6.0 and meet Section 728.148 standards8

     

    D0229

    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 standards8

    6.0 and meet Section 728.148 standards8

     

    D0239

    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 standards8

    5.6 and meet Section 728.148 standards8

     

    D0249

    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 standards8

    5.6 and meet Section 728.148 standards8

     

    D0259

    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 standards8

    5.6 and meet Section 728.148 standards8

     

    D0269

    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 standards8

    11.2 and meet Section 728.148 standards8

     

    D0279

    Wastes that are TC for p-Dichlorobenzene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.

    p-Dichlorobenzene (1,4-Dichlorobenzene)

    106-46-7

    0.090 and meet Section 728.148 standards8

    6.0 and meet Section 728.148 standards8

     

    D0289

    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 standards8

    6.0 and meet Section 728.148 standards8

     

    D0299

    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 standards8

    6.0 and meet Section 728.148 standards8

     

    D0309

    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 standards8

    140 and meet Section 728.148 standards8

     

    D0319

    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 standards8

    0.066 and meet Section 728.148 standards8

    Heptachlor epoxide

    1024-57-3

    0.016 and meet Section 728.148 standards8

    0.066 and meet Section 728.148 standards8

     

    D0329

    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 standards8

    10 and meet Section 728.148 standards8

     

    D0339

    Wastes that are TC for Hexachlorobutadiene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.

    Hexachlorobutadiene

    87-68-3

    0.055 and meet Section 728.148 standards8

    5.6 and meet Section 728.148 standards8

     

    D0349

    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 standards8

    30 and meet Section 728.148 standards8

     

    D0359

    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 standards8

    36 and meet Section 728.148 standards8

     

    D0369

    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 standards8

    14 and meet Section 728.148 standards8

     

    D0379

    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 standards8

    7.4 and meet Section 728.148 standards8

     

    D0389

    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 standards8

    16 and meet Section 728.148 standards8

     

    D0399

    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 standards8

    6.0 and meet Section 728.148 standards8

     

    D0409

    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 standards8

    6.0 and meet Section 728.148 standards8

     

    D0419

    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 standards8

    7.4 and meet Section 728.148 standards8

     

    D0429

    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 standards8

    7.4 and meet Section 728.148 standards8

     

    D0439

    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 standards8

    6.0 and meet Section 728.148 standards8

     

    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, cyclohexanone, o-dichlorobenzene, 2-ethoxyethanol, ethyl acetate, ethyl benzene, ethyl ether, isobutyl alcohol, methanol, methylene chloride, methyl ethyl ketone, methyl isobutyl ketone, nitrobenzene, 2-nitropropane, pyridine, tetrachloroethylene, toluene, 1,1,1-trichloroethane, 1,1,2-trichloroethane, 1,1,2-trichloro-1,2,2-trifluoroethane, trichloroethylene, trichloromonofluoromethane, or xylenes (except as specifically noted in other subcategories). See further details of these listings in 35 Ill. Adm. Code 721.131

    Acetone

    67-64-1

    0.28

    160

    Benzene

    71-43-2

    0.14

    10

    n-Butyl alcohol

    71-36-3

    5.6

    2.6

    Carbon disulfide

    75-15-0

    3.8

    NA

    Carbon tetrachloride

    56-23-5

    0.057

    6.0

    Chlorobenzene

    108-90-7

    0.057

    6.0

    o-Cresol

    95-48-7

    0.11

    5.6

    m-Cresol

    (difficult to distinguish from p-cresol)

    108-39-4

    0.77

    5.6

    p-Cresol

    (difficult to distinguish from m-cresol)

    106-44-5

    0.77

    5.6

    Cresol-mixed isomers (Cresylic acid)

    (sum of o-, m-, and p-cresol concentrations)

    1319-77-3

    0.88

    11.2

    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-trifluoroethane

    76-13-1

    0.057

    30

    Trichloroethylene

    79-01-6

    0.054

    6.0

    Trichloromonofluoromethane

    75-69-4

    0.020

    30

    Xylenes-mixed isomers

    (sum of o-, m-, and p-xylene concentrations)

    1330-20-7

    0.32

    30

     

    F001, F002, F003, F004 & F005

    F003 and F005 solvent wastes that contain any combination of one or more of the following three solvents as the only listed F001 through F005 solvents: carbon disulfide, cyclohexanone, or methanol. (Formerly Section 728.141(c))

    Carbon disulfide

    75-15-0

    3.8

    4.8 mg/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

    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 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 Hexachlorodibenzo-p-dioxins)

    NA

    0.000063

    0.001

    HxCDFs (All Hexachlorodibenzofurans)

    NA55684-94-1

    0.000063

    0.001

    PeCDDs (All Pentachlorodibenzo-p-dioxins)

    NA36088-22-9

    0.000063

    0.001

    PeCDFs (All Pentachlorodibenzofurans)

    NA30402-15-4

    0.000035

    0.001

    Pentachlorophenol

    87-86-5

    0.089

    7.4

    TCDDs (All Tetrachlorodibenzo-p-dioxins)

    NA41903-57-5

    0.000063

    0.001

    TCDFs (All Tetrachlorodibenzofurans)

    NA55722-27-5

    0.000063

    0.001

    2,4,5-Trichlorophenol

    95-95-4

    0.18

    7.4

    2,4,6-Trichlorophenol

    88-06-2

    0.035

    7.4

    2,3,4,6-Tetrachlorophenol

    58-90-2

    0.030

    7.4

     

    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

    CMBST11

    CMBST11

    2-Chloro-1,3-butadiene

    126-99-8

    0.057

    0.28

    3-Chloropropylene

    107-05-1

    0.036

    30

    1,1-Dichloroethane

    75-34-3

    0.059

    6.0

    1,2-Dichloroethane

    107-06-2

    0.21

    6.0

    1,2-Dichloropropane

    78-87-5

    0.85

    18

    cis-1,3-Dichloropropylene

    10061-01-5

    0.036

    18

    trans-1,3-Dichloropropylene

    10061-02-6

    0.036

    18

    bis(2-Ethylhexyl) phthalate

    117-81-7

    0.28

    28

    Hexachloroethane

    67-72-1

    0.055

    30

    Chromium (Total)

    7440-47-3

    2.77

    0.60 mg/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

    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-trichlorophenol as the sole component.)

    HxCDDs (All Hexachlorodibenzo-p-dioxins)

    NA

    0.000063

    0.001

    HxCDFs (All Hexachlorodibenzofurans)

    NA55684-94-1

    0.000063

    0.001

    PeCDDs (All Pentachlorodibenzo-p-dioxins)

    NA36088-22-9

    0.000063

    0.001

    PeCDFs (All Pentachlorodibenzofurans)

    NA30402-15-4

    0.000035

    0.001

    Pentachlorophenol

    87-86-5

    0.089

    7.4

    TCDDs (All Tetrachlorodibenzo-p-dioxins)

    NA41903-57-5

    0.000063

    0.001

    TCDFs (All Tetrachlorodibenzofurans)

    NA55722-27-5

    0.000063

    0.001

    2,4,5-Trichlorophenol

    95-95-4

    0.18

    7.4

    2,4,6-Trichlorophenol

    88-06-2

    0.035

    7.4

    2,3,4,6-Tetrachlorophenol

    58-90-2

    0.030

    7.4

     

    F028

    Residues resulting from the incineration or thermal treatment of soil contaminated with USEPA hazardous waste numbers F020, F021, F023, F026, and F027.

    HxCDDs (All Hexachlorodibenzo-p-dioxins)

    NA

    0.000063

    0.001

    HxCDFs (All Hexachlorodibenzofurans)

    NA55684-94-1

    0.000063

    0.001

    PeCDDs (All Pentachlorodibenzo-p-dioxins)

    NA36088-22-9

    0.000063

    0.001

    PeCDFs (All Pentachlorodibenzofurans)

    NA30402-15-4

    0.000035

    0.001

    Pentachlorophenol

    87-86-5

    0.089

    7.4

    TCDDs (All Tetrachlorodibenzo-p-dioxins)

    NA41903-57-5

    0.000063

    0.001

    TCDFs (All Tetrachlorodibenzofurans)

    NA55722-27-5

    0.000063

    0.001

    2,4,5-Trichlorophenol

    95-95-4

    0.18

    7.4

    2,4,6-Trichlorophenol

    88-06-2

    0.035

    7.4

    2,3,4,6-Tetrachlorophenol

    58-90-2

    0.030

    7.4

     

    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 CMBST11

    0.001 or CMBST11

    Hexachlorodibenzofurans

    NA

    0.000063 or CMBST11

    0.001 or CMBST11

    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 CMBST11

    0.001 or CMBST11

    Pentachlorodibenzofurans

    NA

    0.000035 or CMBST11

    0.001 or CMBST11

    Pentachlorophenol

    87-86-5

    0.089

    7.4

    Phenanthrene

    85-01-8

    0.059

    5.6

    Phenol

    108-95-2

    0.039

    6.2

    Pyrene

    129-00-0

    0.067

    8.2

    Tetrachlorodibenzo-p-dioxins

    NA

    0.000063 or CMBST11

    0.001 or CMBST11

    Tetrachlorodibenzofurans

    NA

    0.000063 or CMBST11

    0.001 or CMBST11

    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

     

    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 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

    a -BHC

    319-84-6

    0.00014

    0.066

    b -BHC

    319-85-7

    0.00014

    0.066

    d -BHC

    319-86-8

    0.023

    0.066

    c -BHC g -BHC

    58-89-9

    0.0017

    0.066

    Benzene

    71-43-2

    0.14

    10

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    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 (Bromomethane)

    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 ( a and c 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

    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-Dichlorophenoxyacetic 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 diphenylnitrosamine)

    122-39-4

    0.92

    NA

    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

    1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD)

    35822-46-9

    0.000035

    0.0025

    1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF)

    67562-39-4

    0.000035

    0.0025

    1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF)

    55673-89-7

    0.000035

    0.0025

    Heptachlor epoxide

    1024-57-3

    0.016

    0.066

    Hexachlorobenzene

    118-74-1

    0.055

    10

    Hexachlorobutadiene

    87-68-3

    0.055

    5.6

    Hexachlorocyclopentadiene

    77-47-4

    0.057

    2.4

    HxCDDs (All Hexachlorodibenzo-p-dioxins)

    NA

    0.000063

    0.001

    HxCDFs (All Hexachlorodibenzofurans)

    NA55684-94-1

    0.000063

    0.001

    Hexachloroethane

    67-72-1

    0.055

    30

    Hexachloropropylene

    1888-71-7

    0.035

    30

    Indeno (1,2,3-c,d) pyrene

    193-39-5

    0.0055

    3.4

    Iodomethane

    74-88-4

    0.19

    65

    Isobutyl alcohol

    78-83-1

    5.6

    170

    Isodrin

    465-73-6

    0.021

    0.066

    Isosafrole

    120-58-1

    0.081

    2.6

    Kepone

    143-50-8

    0.0011

    0.13

    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-chloroaniline)

    101-14-4

    0.50

    30

    Methylene chloride

    75-09-2

    0.089

    30

    Methyl ethyl ketone

    78-93-3

    0.28

    36

    Methyl isobutyl ketone

    108-10-1

    0.14

    33

    Methyl methacrylate

    80-62-6

    0.14

    160

    Methyl methansulfonate

    66-27-3

    0.018

    NA

    Methyl parathion

    298-00-0

    0.014

    4.6

    Naphthalene

    91-20-3

    0.059

    5.6

    2-Naphthylamine

    91-59-8

    0.52

    NA

    p-Nitroaniline

    100-01-6

    0.028

    28

    Nitrobenzene

    98-95-3

    0.068

    14

    5-Nitro-o-toluidine

    99-55-8

    0.32

    28

    p-Nitrophenol

    100-02-7

    0.12

    29

    N-Nitrosodiethylamine

    55-18-5

    0.40

    28

    N-Nitrosodimethylamine

    62-75-9

    0.40

    NA

    N-Nitroso-di-n-butylamine

    924-16-3

    0.40

    17

    N-Nitrosomethylethylamine

    10595-95-6

    0.40

    2.3

    N-Nitrosomorpholine

    59-89-2

    0.40

    2.3

    N-Nitrosopiperidine

    100-75-4

    0.013

    35

    N-Nitrosopyrrolidine

    930-55-2

    0.013

    35

    1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (1,2,3,4,6,7,8,9-OCDD)

    3268-87-9

    0.000063

    0.0025

    Parathion

    56-38-2

    0.014

    4.6

    Total PCBs

    (sum of all PCB isomers, or all Aroclors)

    1336-36-3

    0.10

    10

    Pentachlorobenzene

    608-93-5

    0.055

    10

    PeCDDs (All Pentachlorodibenzo-p-dioxins)

    NA36088-22-9

    0.000063

    0.001

    PeCDFs (All Pentachlorodibenzofurans)

    NA30402-15-4

    0.000035

    0.001

    Pentachloronitrobenzene

    82-68-8

    0.055

    4.8

    Pentachlorophenol

    87-86-5

    0.089

    7.4

    Phenacetin

    62-44-2

    0.081

    16

    Phenanthrene

    85-01-8

    0.059

    5.6

    Phenol

    108-95-2

    0.039

    6.2

    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 Tetrachlorodibenzo-p-dioxins)

    NA41903-57-5

    0.000063

    0.001

    TCDFs (All Tetrachlorodibenzofurans)

    NA55722-27-5

    0.000063

    0.001

    1,1,1,2-Tetrachloroethane

    630-20-6

    0.057

    6.0

    1,1,2,2-Tetrachloroethane

    79-34-6

    0.057

    6.0

    Tetrachloroethylene

    127-18-4

    0.056

    6.0

    2,3,4,6-Tetrachlorophenol

    58-90-2

    0.030

    7.4

    Toluene

    108-88-3

    0.080

    10

    Toxaphene

    8001-35-2

    0.0095

    2.6

    Bromoform (Tribromomethane)

    75-25-2

    0.63

    15

    1,2,4-Trichlorobenzene

    120-82-1

    0.055

    19

    1,1,1-Trichloroethane

    71-55-6

    0.054

    6.0

    1,1,2-Trichloroethane

    79-00-5

    0.054

    6.0

    Trichloroethylene

    79-01-6

    0.054

    6.0

    Trichloromonofluoromethane

    75-69-4

    0.020

    30

    2,4,5-Trichlorophenol

    95-95-4

    0.18

    7.4

    2,4,6-Trichlorophenol

    88-06-2

    0.035

    7.4

    1,2,3-Trichloropropane

    96-18-4

    0.85

    30

    1,1,2-Trichloro-1,2,2-trifluoroethane

    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

    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

     

    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

    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

    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 diphenylnitrosamine)

    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

    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 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

     

    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 ( a and c   g  isomers)

     

    57-74-9

    0.0033

    0.26

    Heptachlor

    76-44-8

    0.0012

    0.066

    Heptachlor epoxide

    1024-57-3

    0.016

    0.066

     

    K033

    Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane.

    Hexachlorocyclopentadiene

    77-47-4

    0.057

    2.4

     

    K034

    Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.

    Hexachlorocyclopentadiene

    77-47-4

    0.057

    2.4

     

    K035

    Wastewater treatment sludges generated in the production of creosote.

    Acenaphthene

    83-32-9

    NA

    3.4

    Anthracene

    120-12-7

    NA

    3.4

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    Benzo(a)pyrene

    50-32-8

    0.061

    3.4

    Chrysene

    218-01-9

    0.059

    3.4

    o-Cresol

    95-48-7

    0.11

    5.6

    m-Cresol

    (difficult to distinguish from p-cresol)

    108-39-4

    0.77

    5.6

    p-Cresol

    (difficult to distinguish from m-cresol)

    106-44-5

    0.77

    5.6

    Dibenz(a,h)anthracene

    53-70-3

    NA

    8.2

    Fluoranthene

    206-44-0

    0.068

    3.4

    Fluorene

    86-73-7

    NA

    3.4

    Indeno(1,2,3-cd)pyrene

    193-39-5

    NA

    3.4

    Naphthalene

    91-20-3

    0.059

    5.6

    Phenanthrene

    85-01-8

    0.059

    5.6

    Phenol

    108-95-2

    0.039

    6.2

    Pyrene

    129-00-0

    0.067

    8.2

     

    K036

    Still bottoms from toluene reclamation distillaiton in the production of disulfoton.

    Disulfoton

    298-04-4

    0.017

    6.2

     

    K037

    Wastewater treatment sludges from the production of disulfoton.

    Disulfoton

    298-04-4

    0.017

    6.2

    Toluene

    108-88-3

    0.080

    10

     

    K038

    Wastewater from the washing and stripping of phorate production.

    Phorate

    298-02-2

    0.021

    4.6

     

    K039

    Filter cake from the filtration of diethylphosphorodithioic acid in the production of phorate.

    NA

    NA

    CARBN; or CMBST

    CMBST

     

    K040

    Wastewater treatment sludge from the production of phorate.

    Phorate

    298-02-2

    0.021

    4.6

     

    K041

    Wastewater treatment sludge from the production of toxaphene.

    Toxaphene

    8001-35-2

    0.0095

    2.6

     

    K042

    Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5-T.

    o-Dichlorobenzene

    95-50-1

    0.088

    6.0

    p-Dichlorobenzene

    106-46-7

    0.090

    6.0

    Pentachlorobenzene

    608-93-5

    0.055

    10

    1,2,4,5-Tetrachlorobenzene

    95-94-3

    0.055

    14

    1,2,4-Trichlorobenzene

    120-82-1

    0.055

    19

     

    K043

    2,6-Dichlorophenol waste from the production of 2,4-D.

    2,4-Dichlorophenol

    120-83-2

    0.044

    14

    2,6-Dichlorophenol

    187-65-0

    0.044

    14

    2,4,5-Trichlorophenol

    95-95-4

    0.18

    7.4

    2,4,6-Trichlorophenol

    88-06-2

    0.035

    7.4

    2,3,4,6-Tetrachlorophenol

    58-90-2

    0.030

    7.4

    Pentachlorophenol

    87-86-5

    0.089

    7.4

    Tetrachloroethylene

    127-18-4

    0.056

    6.0

    HxCDDs (All Hexachlorodibenzo-p-dioxins)

    NA

    0.000063

    0.001

    HxCDFs (All Hexachlorodibenzofurans)

    NA55684-94-1

    0.000063

    0.001

    PeCDDs (All Pentachlorodibenzo-p-dioxins)

    NA36088-22-9

    0.000063

    0.001

    PeCDFs (All Pentachlorodibenzofurans)

    NA30402-15-4

    0.000035

    0.001

    TCDDs (All Tetrachlorodibenzo-p-dioxins)

    NA41903-57-5

    0.000063

    0.001

    TCDFs (All Tetrachlorodibenzofurans)

    NA55722-27-5

    0.000063

    0.001

     

    K044

    Wastewater treatment sludges from the manufacturing and processing of explosives.

    NA

    NA

    DEACT

    DEACT

     

    K045

    Spent carbon from the treatment of wastewater containing explosives.

    NA

    NA

    DEACT

    DEACT

     

    K046

    Wastewater treatment sludges from the manufacturing, formulation and loading of lead-based initiating compounds.

    Lead

    7439-92-1

    0.69

    0.75 mg/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

    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

    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

    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

    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

     

    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

    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

    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

    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

    NA

     

    K093

    Distillation light ends from the production of phthalic anhydride from ortho-xylene.

    Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

    100-21-0

    0.055

    28

    Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

    85-44-9

    0.055

    28

     

    K094

    Distillation bottoms from the production of phthalic anhydride from ortho-xylene.

    Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

    100-21-0

    0.055

    28

    Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

    85-44-9

    0.055

    28

     

    K095

    Distillation bottoms from the production of 1,1,1-trichloroethane.

    Hexachloroethane

    67-72-1

    0.055

    30

    Pentachloroethane

    76-01-7

    0.055

    6.0

    1,1,1,2-Tetrachloroethane

    630-20-6

    0.057

    6.0

    1,1,2,2-Tetrachloroethane

    79-34-6

    0.057

    6.0

    Tetrachloroethylene

    127-18-4

    0.056

    6.0

    1,1,2-Trichloroethane

    79-00-5

    0.054

    6.0

    Trichloroethylene

    79-01-6

    0.054

    6.0

     

    K096

    Heavy ends from the heavy ends column from the production of 1,1,1-trichloroethane.

    m-Dichlorobenzene

    541-73-1

    0.036

    6.0

    Pentachloroethane

    76-01-7

    0.055

    6.0

    1,1,1,2-Tetrachloroethane

    630-20-6

    0.057

    6.0

    1,1,2,2-Tetrachloroethane

    79-34-6

    0.057

    6.0

    Tetrachloroethylene

    127-18-4

    0.056

    6.0

    1,2,4-Trichlorobenzene

    120-82-1

    0.055

    19

    1,1,2-Trichloroethane

    79-00-5

    0.054

    6.0

    Trichloroethylene

    79-01-6

    0.054

    6.0

     

    K097

    Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.

    Chlordane ( a and c 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 Hexachlorodibenzo-p-dioxins)

    NA

    0.000063

    0.001

    HxCDFs (All Hexachlorodibenzofurans)

    NA55684-94-1

    0.000063

    0.001

    PeCDDs (All Pentachlorodibenzo-p-dioxins)

    NA36088-22-9

    0.000063

    0.001

    PeCDFs (All Pentachlorodibenzofurans)

    NA30402-15-4

    0.000035

    0.001

    TCDDs (All Tetrachlorodibenzo-p-dioxins)

    NA41903-57-5

    0.000063

    0.001

    TCDFs (All Tetrachlorodibenzofurans)

    NA55722-27-5

    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

     

    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 chlorobenzenes.

    Benzene

    71-43-2

    0.14

    10

    Chlorobenzene

    108-90-7

    0.057

    6.0

    2-Chlorophenol

    95-57-8

    0.044

    5.7

    o-Dichlorobenzene

    95-50-1

    0.088

    6.0

    p-Dichlorobenzene

    106-46-7

    0.090

    6.0

    Phenol

    108-95-2

    0.039

    6.2

    2,4,5-Trichlorophenol

    95-95-4

    0.18

    7.4

    2,4,6-Trichlorophenol

    88-06-2

    0.035

    7.4

     

    K106

    K106 (wastewater treatment sludge from the mercury cell process in chlorine production) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.

    Mercury

    7439-97-6

    NA

    RMERC

     

    K106

    K106 (wastewater treatment sludge from the mercury cell process in chlorine production) nonwastewaters that contain less than 260 mg/kg total mercury that are residues from RMERC.

    Mercury

    7439-97-6

    NA

    0.20 mg/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

     

    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 hydrogenation 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

     

    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 (Bromomethane)

    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 (Bromomethane)

    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

     

    K125

    Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic 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 (Bromomethane)

    74-83-9

    0.11

    15

     

    K132

    Spent absorbent and wastewater separator solids from the production of methyl bromide.

    Methyl bromide (Bromomethane)

    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 (Bromomethane)

    74-83-9

    0.11

    15

    Chloroform

    67-66-3

    0.046

    6.0

    Ethylene dibromide (1,2-Dibromoethane)

    106-93-4

    0.028

    15

     

    K141

    Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the production of coke or the recovery of coke by-products produced from coal. This listing does not include K087 (decanter tank tar sludge from coking operations).

    Benzene

    71-43-2

    0.14

    10

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    Benzo(a)pyrene

    50-2-8

    0.061

    3.4

    Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

    205-99-2

    0.11

    6.8

    Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

    207-08-9

    0.11

    6.8

    Chrysene

    218-01-9

    0.059

    3.4

    Dibenz(a,h)anthracene

    53-70-3

    0.055

    8.2

    Indeno(1,2,3-cd)pyrene

    193-39-5

    0.0055

    3.4

     

    K142

    Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal.

    Benzene

    71-43-2

    0.14

    10

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    Benzo(a)pyrene

    50-32-8

    0.061

    3.4

    Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

    205-99-2

    0.11

    6.8

    Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

    207-08-9

    0.11

    6.8

    Chrysene

    218-01-9

    0.059

    3.4

    Dibenz(a,h)anthracene

    53-70-3

    0.055

    8.2

    Indeno(1,2,3-cd)pyrene

    193-39-5

    0.0055

    3.4

     

    K143

    Process residues from the recovery of light oil, including, but not limited to, those generated in stills, decanters, and wash oil recovery units from the recovery of coke by-products produced from coal.

    Benzene

    71-43-2

    0.14

    10

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    Benzo(a)pyrene

    50-32-8

    0.061

    3.4

    Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

    205-99-2

    0.11

    6.8

    Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

    207-08-9

    0.11

    6.8

    Chrysene

    218-01-9

    0.059

    3.4

     

    K144

    Wastewater sump residues from light oil refining, including, but not limited to, intercepting or contamination sump sludges from the recovery of coke by-products produced from coal.

    Benzene

    71-43-2

    0.14

    10

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    Benzo(a)pyrene

    50-32-8

    0.061

    3.4

    Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

    205-99-2

    0.11

    6.8

    Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

    207-08-9

    0.11

    6.8

    Chrysene

    218-01-9

    0.059

    3.4

    Dibenz(a,h)anthracene

    53-70-3

    0.055

    8.2

     

    K145

    Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal.

    Benzene

    71-43-2

    0.14

    10

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    Benzo(a)pyrene

    50-32-8

    0.061

    3.4

    Chrysene

    218-01-9

    0.059

    3.4

    Dibenz(a,h)anthracene

    53-70-3

    0.055

    8.2

    Naphthalene

    91-20-3

    0.059

    5.6

     

    K147

    Tar storage tank residues from coal tar refining.

    Benzene

    71-43-2

    0.14

    10

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    Benzo(a)pyrene

    50-32-8

    0.061

    3.4

    Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

    205-99-2

    0.11

    6.8

    Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

    207-08-9

    0.11

    6.8

    Chrysene

    218-01-9

    0.059

    3.4

    Dibenz(a,h)anthracene

    53-70-3

    0.055

    8.2

    Indeno(1,2,3-cd)pyrene

    193-39-5

    0.0055

    3.4

     

    K148

    Residues from coal tar distillation, including, but not limited to, still bottoms.

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    Benzo(a)pyrene

    50-32-8

    0.061

    3.4

    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 a - (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 hydrochloric acid recovery processes associated with the production of a - (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.

    Carbon tetrachloride

    56-23-5

    0.057

    6.0

    Chloroform

    67-66-3

    0.046

    6.0

    Chloromethane

    74-87-3

    0.19

    30

    p-Dichlorobenzene

    106-46-7

    0.090

    6.0

    Hexachlorobenzene

    118-74-1

    0.055

    10

    Pentachlorobenzene

    608-93-5

    0.055

    10

    1,2,4,5-Tetrachlorobenzene

    95-94-3

    0.055

    14

    1,1,2,2- Tetrachloroethane

    79-34-5

    0.057

    6.0

    Tetrachloroethylene

    127-18-4

    0.056

    6.0

    1,2,4-Trichlorobenzene

    120-82-1

    0.055

    19

     

    K151

    Wastewater treatment sludges, excluding neutralization and biological sludges, generated during the treatment of wastewaters from the production of a - (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

    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

    1.1511

    Arsenic

    7440-38-2

    1.4

    5.011

    Carbon disulfide

    75-15-0

    3.8

    4.811

    Dithiocarbamates (total)

    137-30-4

    0.028

    28

    Lead

    7439-92-1

    0.69

    0.7511

    Nickel

    7440-02-0

    3.98

    1111

    Selenium

    7782-49-2

    0.82

    5.711

     

    K169

    Crude oil tank sediment from petroleum refining operations.

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    Benzene

    71-43-2

    0.14

    10

    Benzo(g,h,i)perylene

    191-24-2

    0.0055

    1.8

    Chrysene

    218-01-9

    0.059

    3.4

    Ethyl benzene

    100-41-4

    0.057

    10

    Fluorene

    86-73-7

    0.059

    3.4

    Naphthalene

    91-20-3

    0.059

    5.6

    Phenanthrene

    81-05-8

    0.059

    5.6

    Pyrene

    129-00-0

    0.067

    8.2

    Toluene (Methyl Benzene)

    108-88-3

    0.080

    10

    Xylenes (Total)

    1330-20-7

    0.32

    30

     

    K170

    Clarified slurry oil sediment from petroleum refining operations.

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    Benzene

    71-43-2

    0.14

    10

    Benzo(g,h,i)perylene

    191-24-2

    0.0055

    1.8

    Chrysene

    218-01-9

    0.059

    3.4

    Dibenz(a,h)anthracene

    53-70-3

    0.055

    8.2

    Ethyl benzene

    100-41-4

    0.057

    10

    Fluorene

    86-73-7

    0.059

    3.4

    Indeno(1,2,3,-cd)pyrene

    193-39-5

    0.0055

    3.4

    Naphthalene

    91-20-3

    0.059

    5.6

    Phenanthrene

    81-05-8

    0.059

    5.6

    Pyrene

    129-00-0

    0.067

    8.2

    Toluene (Methyl Benzene)

    108-88-3

    0.080

    10

    Xylenes (Total

    1330-20-7

    0.32

    30

     

    K171

    Spent hydrotreating catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors. (This listing does not include inert support media.)

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    Benzene

    71-43-2

    0.14

    10

    Chrysene

    218-01-9

    0.059

    3.4

    Ethyl benzene

    100-41-4

    0.057

    10

    Naphthalene

    91-20-3

    0.059

    5.6

    Phenanthrene

    81-05-8

    0.059

    5.6

    Pyrene

    129-00-0

    0.067

    8.2

    Toluene (Methyl Benzene)

    108-88-3

    0.080

    10

    Xylenes (Total)

    1330-20-7

    0.32

    30

    Arsenic

    7740-38-2

    1.4

    5 mg/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

    Xylenes (Total)

    1330-20-7

    0.32

    30

    Antimony

    7740-36-0

    1.9

    1.15 mg/l TCLP

    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

     

    K174

    Wastewater treatment sludge from the production of ethylene dicholoride or vinyl choloride monomer.

    1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD)

    35822-46-9

    0.000035 or CMBST11

    0.0025 or CMBST11

    1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF)

    67562-39-4

    0.000035 or CMBST11

    0.0025 or CMBST11

    1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF)

    55673-89-7

    0.000035 or CMBST11

    0.0025 or CMBST11

    All hexachlorodibenzo-p-dioxins (HxCDDs)

    34465-46-8

    0.000063 or CMBST11

    0.001 or CMBST11

    All hexachlorodibenzofurans (HxCDFs)

    55684-94-1

    0.000063 or CMBST11

    0.001 or CMBST11

    1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (1,2,3,4,6,7,8,9-OCDD)

    3268-87-9

    0.000063 or CMBST11

    0.005 or CMBST11

    1,2,3,4,6,7,8,9-Octachlorodibenzofuran (1,2,3,4,6,7,8,9-OCDF)

    39001-02-0

    0.000063 or CMBST11

    0.005 or CMBST11

    All pentachlorodibenzo-p-dioxins (PeCDDs)

    36088-22-9

    0.000063 or CMBST11

    0.001 or CMBST11

    All pentachlorodibenzofurans (PeCDFs)

    30402-15-4

    0.000035 or CMBST11

    0.001 or CMBST11

    All tetrachlorodibenzo-p-dioxins (TCDDs)

    41903-57-5

    0.000063 or CMBST11

    0.001 or CMBST11

    All tetrachlorodibenzofurans (TCDFs)

    55722-27-5

    0.000063 or CMBST11

    0.001 or CMBST11

    Arsenic

    7440-36-0

    1.4

    5.0 mg/L TCLP

     

    K175

    Wastewater treatment sludge from the production of vinyl choloride monomer using mercuric chloride catalyst in an acetylene-based process.

    Mercury12

    7438-97-6

    7439-97-6

    NA

    0.025 mg/L TCLP

    PH12

     

    NA

    pH £ 6.0

     

    K175

    All K175 wastewaters.

    Mercury

    7438-97-6

    7439-97-6

    0.15

    NA

     

    K176

    Baghouse filters from the production of antimony oxide, including filters from the production of intermediates e.g., antimony metal or crude antimony oxide).

    Antimony

    7440-36-0

    1.9

    1.15 mg/L TCLP

    Arsenic

    7440-38-2

    1.4

    5.0 mg/L TCLP

    Cadmium

    7440-43-9

    0.69

    0.11 mg/L TCLP

    Lead

    7439-92-1

    0.69

    0.75 mg/L TCLP

    Mercury

    7439-97-6

    0.15

    0.025 mg/L TCLP

     

    K177

    Slag from the production of antimony oxide that is speculatively accumulated or disposed, including slag from the production of intermediates (e.g., antimony metal or crude antimony oxide).

    Antimony

    7440-36-0

    1.9

    1.15 mg/L TCLP

    Arsenic

    7440-38-2

    1.4

    5.0 mg/L TCLP

    Lead

    7439-92-1

    0.69

    0.75 mg/L TCLP

     

    K178

    Residues from manufacturing and manufacturing-site storage of ferric chloride from acids formed during the production of titanium dioxide using the chloride-ilmenite process.

    1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD)

    35822-46-9

    0.000035 or CMBST11

    0.0025 or CMBST11

    1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF)

    67562-39-4

    0.000035 or CMBST11

    0.0025 or CMBST11

    1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF)

    55673-89-7

    0.000035 or CMBST11

    0.0025 or CMBST11

    HxCDDs (All Hexachlorodibenzo-p-dioxins)

    34465-46-8

    0.000063 or CMBST11

    0.001 or CMBST11

    HxCDFs (All Hexachlorodibenzofurans)

    55684-94-1

    0.000063 or CMBST11

    0.001 or CMBST11

    1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (1,2,3,4,6,7,8,9-OCDD)

    3268-87-9

    0.000063 or CMBST11

    0.005 or CMBST11

    1,2,3,4,6,7,8,9-Octachlorodibenzofuran (OCDF)

    39001-02-0

    0.000063 or CMBST11

    0.005 or CMBST11

    PeCDDs (All Pentachlorodibenzo-p-dioxins)

    36088-22-9

    0.000063 or CMBST11

    0.001 or CMBST11

    PeCDFs (All Pentachlorodibenzofurans)

    30402-15-4

    0.000035 or CMBST11

    0.001 or CMBST11

    TCDDs (All Tetrachlorodibenzo-p-dioxins)

    41903-57-5

    0.000063 or CMBST11

    0.001 or CMBST11

    TCDFs (All Tetrachlorodibenzofurans)

    55722-27-5

    0.000063 or CMBST11

    0.001 or CMBST11

    Thallium

    7440-28-0

    1.4

    0.20 mg/L TCLP

     

    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

     

    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

     

    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; alternate6 standard for nonwastewaters only

    75-15-0

    NA

    4.8 mg/l TCLP

     

    P023

    Chloroacetaldehyde

    Chloroacetaldehyde

    107-20-0

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    P024

    p-Chloroaniline

    p-Chloroaniline

    106-47-8

    0.46

    16

     

    P026

    1-(o-Chlorophenyl)thiourea

    1-(o-Chlorophenyl)thiourea

    5344-82-1

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    P027

    3-Chloropropionitrile

    3-Chloropropionitrile

    542-76-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    P028

    Benzyl chloride

    Benzyl chloride

    100-44-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    P029

    Copper cyanide

    Cyanides (Total)7

    57-12-5

    1.2

    590

    Cyanides (Amenable)7

    57-12-5

    0.86

    30

     

    P030

    Cyanides (soluble salts and complexes)

    Cyanides (Total)7

    57-12-5

    1.2

    590

    Cyanides (Amenable)7

    57-12-5

    0.86

    30

     

    P031

    Cyanogen

    Cyanogen

    460-19-5

    CHOXD; WETOX; or CMBST

    CHOXD; WETOX; or CMBST

     

    P033

    Cyanogen chloride

    Cyanogen chloride

    506-77-4

    CHOXD; WETOX; or CMBST

    CHOXD; WETOX; or CMBST

     

    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-pyrazinylphosphorothioate

    297-97-2

    CARBN; or CMBST

    CMBST

     

    P041

    Diethyl-p-nitrophenyl phosphate

    Diethyl-p-nitrophenyl phosphate

    311-45-5

    CARBN; or CMBST

    CMBST

     

    P042

    Epinephrine

    Epinephrine

    51-43-4

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    P043

    Diisopropylfluorophosphate (DFP)

    Diisopropylfluorophosphate (DFP)

    55-91-4

    CARBN; or CMBST

    CMBST

     

    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

    a , a -Dimethylphenethylamine

    a , a -Dimethylphenethylamine

    122-09-8

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    P047

    4,6-Dinitro-o-cresol

    4,6-Dinitro-o-cresol

    543-52-1

    0.28

    160

     

    P047

    4,6-Dinitro-o-cresol salts

    NA

    NA

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    P048

    2,4-Dinitrophenol

    2,4-Dinitrophenol

    51-28-5

    0.12

    160

     

    P049

    Dithiobiuret

    Dithiobiuret

    541-53-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    P050

    Endosulfan

    Endosulfan I

    939-98-8

    0.023

    0.066

    Endosulfan II

    33213-6-5

    0.029

    0.13

    Endosulfan sulfate

    1031-07-8

    0.029

    0.13

     

    P051

    Endrin

    Endrin

    72-20-8

    0.0028

    0.13

    Endrin aldehyde

    7421-93-4

    0.025

    0.13

     

    P054

    Aziridine

    Aziridine

    151-56-4

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    P056

    Fluorine

    Fluoride (measured in wastewaters only)

    16964-48-8

    35

    ADGAS fb NEUTR

     

    P057

    Fluoroacetamide

    Fluoroacetamide

    640-19-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    P058

    Fluoroacetic acid, sodium salt

    Fluoroacetic acid, sodium salt

    62-74-8

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    P059

    Heptachlor

    Heptachlor

    76-44-8

    0.0012

    0.066

    Heptachlor epoxide

    1024-57-3

    0.016

    0.066

     

    P060

    Isodrin

    Isodrin

    465-73-6

    0.021

    0.066

     

    P062

    Hexaethyl tetraphosphate

    Hexaethyl tetraphosphate

    757-58-4

    CARBN; or CMBST

    CMBST

     

    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

     

    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

     

    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

     

    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 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

     

    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

     

    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

     

    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 Zn3P2, when present at concentrations greater than 10 percent

    Zinc Phosphide

    1314-84-7

    CHOXD; CHRED; or CMBST

    CHOXD; CHRED; or CMBST

     

    P123

    Toxaphene

    Toxaphene

    8001-35-2

    0.0095

    2.6

     

    P127

    Carbofuran

    Carbofuran

    1563-66-2

    0.006

    0.14

     

    P128

    Mexacarbate

    Mexacarbate

    315-18-4

    0.056

    1.4

     

    P185

    Tirpate10

    Tirpate

    26419-73-8

    0.056

    0.28

     

    P188

    Physostigimine salicylate

    Physostigmine salicylate

    57-64-7

    0.056

    1.4

     

    P189

    Carbosulfan

    Carbosulfan

    55285-14-8

    0.028

    1.4

     

    P190

    Metolcarb

    Metolcarb

    1129-41-5

    0.056

    1.4

     

    P191

    Dimetilan10

    Dimetilan

    644-64-4

    0.056

    1.4

     

    P192

    Isolan10

    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

    Formparanate10

    Formparanate

    17702-57-7

    0.056

    1.4

     

    P198

    Formetanate hydrochloride

    Formetanate hydrochloride

    23422-53-9

    0.056

    1.4

     

    P199

    Methiocarb

    Methiocarb

    2032-65-7

    0.056

    1.4

     

    P201

    Promecarb

    Promecarb

    2631-37-0

    0.056

    1.4

     

    P202

    m-Cumenyl methylcarbamate

    m-Cumenyl methylcarbamate

    64-00-6

    0.056

    1.4

     

    P203

    Aldicarb sulfone

    Aldicarb sulfone

    1646-88-4

    0.056

    0.28

     

    P204

    Physostigmine

    Physostigmine

    57-47-6

    0.056

    1.4

     

    P205

    Ziram

    Dithiocarbamates (total)

    NA

    0.028

    28

     

    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; alternate6 standard for nonwastewaters only

    75-05-8

    NA

    38

     

    U004

    Acetophenone

    Acetophenone

    98-86-2

    0.010

    9.7

     

    U005

    2-Acetylaminofluorene

    2-Acetylaminofluorene

    53-96-3

    0.059

    140

     

    U006

    Acetyl chloride

    Acetyl chloride

    75-36-5

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U007

    Acrylamide

    Acrylamide

    79-06-1

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U008

    Acrylic acid

    Acrylic acid

    79-10-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U009

    Acrylonitrile

    Acrylonitrile

    107-13-1

    0.24

    84

     

    U010

    Mitomycin C

    Mitomycin C

    50-07-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U011

    Amitrole

    Amitrole

    61-82-5

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U012

    Aniline

    Aniline

    62-53-3

    0.81

    14

     

    U014

    Auramine

    Auramine

    492-80-8

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U015

    Azaserine

    Azaserine

    115-02-6

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U016

    Benz(c)acridine

    Benz(c)acridine

    225-51-4

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U017

    Benzal chloride

    Benzal chloride

    98-87-3

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U018

    Benz(a)anthracene

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

     

    U019

    Benzene

    Benzene

    71-43-2

    0.14

    10

     

    U020

    Benzenesulfonyl chloride

    Benzenesulfonyl chloride

    98-09-9

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U021

    Benzidine

    Benzidine

    92-87-5

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U022

    Benzo(a)pyrene

    Benzo(a)pyrene

    50-32-8

    0.061

    3.4

     

    U023

    Benzotrichloride

    Benzotrichloride

    98-07-7

    CHOXD; CHRED; CARBN; BIODG; or CMBST

    CHOXD; CHRED; or CMBST

     

    U024

    bis(2-Chloroethoxy)methane

    bis(2-Chloroethoxy)methane

    111-91-1

    0.036

    7.2

     

    U025

    bis(2-Chloroethyl)ether

    bis(2-Chloroethyl)ether

    111-44-4

    0.033

    6.0

     

    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 (Bromomethane)

    74-83-9

    0.11

    15

     

    U030

    4-Bromophenyl phenyl ether

    4-Bromophenyl phenyl ether

    101-55-3

    0.055

    15

     

    U031

    n-Butyl alcohol

    n-Butyl alcohol

    71-36-3

    5.6

    2.6

     

    U032

    Calcium chromate

    Chromium (Total)

    7440-47-3

    2.77

    0.60 mg/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 ( a and c isomers)

    57-74-9

    0.0033

    0.26

     

    U037

    Chlorobenzene

    Chlorobenzene

    108-90-7

    0.057

    6.0

     

    U038

    Chlorobenzilate

    Chlorobenzilate

    510-15-6

    0.10

    CMBST

     

    U039

    p-Chloro-m-cresol

    p-Chloro-m-cresol

    59-50-7

    0.018

    14

     

    U041

    Epichlorohydrin (1-Chloro-2,3-epoxypropane)

    Epichlorohydrin (1-Chloro-2,3-epoxypropane)

    106-89-8

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U042

    2-Chloroethyl vinyl ether

    2-Chloroethyl vinyl ether

    110-75-8

    0.062

    CMBST

     

    U043

    Vinyl chloride

    Vinyl chloride

    75-01-4

    0.27

    6.0

     

    U044

    Chloroform

    Chloroform

    67-66-3

    0.046

    6.0

     

    U045

    Chloromethane (Methyl chloride)

    Chloromethane (Methyl chloride)

    74-87-3

    0.19

    30

     

    U046

    Chloromethyl methyl ether

    Chloromethyl methyl ether

    107-30-2

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U047

    2-Chloronaphthalene

    2-Chloronaphthalene

    91-58-7

    0.055

    5.6

     

    U048

    2-Chlorophenol

    2-Chlorophenol

    95-57-8

    0.044

    5.7

     

    U049

    4-Chloro-o-toluidine hydrochloride

    4-Chloro-o-toluidine hydrochloride

    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

     

    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; alternate6 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

    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

     

    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

     

    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-methyldithiophosphate

    3288-58-2

    CARBN; or CMBST

    CMBST

     

    U088

    Diethyl phthalate

    Diethyl phthalate

    84-66-2

    0.20

    28

     

    U089

    Diethyl stilbestrol

    Diethyl stilbestrol

    56-53-1

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U090

    Dihydrosafrole

    Dihydrosafrole

    94-58-6

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U091

    3,3'-Dimethoxybenzidine

    3,3'-Dimethoxybenzidine

    119-90-4

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U092

    Dimethylamine

    Dimethylamine

    124-40-3

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U093

    p-Dimethylaminoazobenzene

    p-Dimethylaminoazobenzene

    60-11-7

    0.13

    CMBST

     

    U094

    7,12-Dimethylbenz(a)anthracene

    7,12-Dimethylbenz(a)anthracene

    57-97-6

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U095

    3,3'-Dimethylbenzidine

    3,3'-Dimethylbenzidine

    119-93-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U096

    a , a -Dimethyl benzyl hydroperoxide

    a , a -Dimethyl benzyl hydroperoxide

    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

     

    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; alternate6 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; alternate6 standard for wastewaters only

    122-66-7

    0.087

    NA

     

    U110

    Dipropylamine

    Dipropylamine

    142-84-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U111

    Di-n-propylnitrosamine

    Di-n-propylnitrosamine

    621-64-7

    0.40

    14

     

    U112

    Ethyl acetate

    Ethyl acetate

    141-78-6

    0.34

    33

     

    U113

    Ethyl acrylate

    Ethyl acrylate

    140-88-5

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U114

    Ethylenebisdithiocarbamic acid salts and esters

    Ethylenebisdithiocarbamic acid

    111-54-6

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U115

    Ethylene oxide

    Ethylene oxide

    75-21-8

    (WETOX or CHOXD) fb CARBN; or CMBST

    CHOXD; or CMBST

    Ethylene oxide; alternate6 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

     

    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

     

    U127

    Hexachlorobenzene

    Hexachlorobenzene

    118-74-1

    0.055

    10

     

    U128

    Hexachlorobutadiene

    Hexachlorobutadiene

    87-68-3

    0.055

    5.6

     

    U129

    Lindane

    a -BHC

    319-84-6

    0.00014

    0.066

    b -BHC

    319-85-7

    0.00014

    0.066

    d -BHC

    319-86-8

    0.023

    0.066

    c -BHC g -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

     

    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

     

    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

     

    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; alternate6 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

     

    U158

    4,4'-Methylene bis(2-chloroaniline)

    4,4'-Methylene bis(2-chloroaniline)

    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-nitrosoguanidine

    70-25-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U164

    Methylthiouracil

    Methylthiouracil

    56-04-2

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U165

    Naphthalene

    Naphthalene

    91-20-3

    0.059

    5.6

     

    U166

    1,4-Naphthoquinone

    1,4-Naphthoquinone

    130-15-4

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U167

    1-Naphthylamine

    1-Naphthylamine

    134-32-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U168

    2-Naphthylamine

    2-Naphthylamine

    91-59-8

    0.52

    CMBST

     

    U169

    Nitrobenzene

    Nitrobenzene

    98-95-3

    0.068

    14

     

    U170

    p-Nitrophenol

    p-Nitrophenol

    100-02-7

    0.12

    29

     

    U171

    2-Nitropropane

    2-Nitropropane

    79-46-9

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U172

    N-Nitrosodi-n-butylamine

    N-Nitrosodi-n-butylamine

    924-16-3

    0.40

    17

     

    U173

    N-Nitrosodiethanolamine

    N-Nitrosodiethanolamine

    1116-54-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U174

    N-Nitrosodiethylamine

    N-Nitrosodiethylamine

    55-18-5

    0.40

    28

     

    U176

    N-Nitroso-N-ethylurea

    N-Nitroso-N-ethylurea

    759-73-9

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U177

    N-Nitroso-N-methylurea

    N-Nitroso-N-methylurea

    684-93-5

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U178

    N-Nitroso-N-methylurethane

    N-Nitroso-N-methylurethane

    615-53-2

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U179

    N-Nitrosopiperidine

    N-Nitrosopiperidine

    100-75-4

    0.013

    35

     

    U180

    N-Nitrosopyrrolidine

    N-Nitrosopyrrolidine

    930-55-2

    0.013

    35

     

    U181

    5-Nitro-o-toluidine

    5-Nitro-o-toluidine

    99-55-8

    0.32

    28

     

    U182

    Paraldehyde

    Paraldehyde

    123-63-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

     

    U183

    Pentachlorobenzene

    Pentachlorobenzene

    608-93-5

    0.055

    10

     

    U184

    Pentachloroethane

    Pentachloroethane

    76-01-7

    (WETOX or CHOXD) fb CARBN; or CMBST

    CMBST

    Pentachloroethane; alternate6 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

    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

     

    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

     

    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

     

    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

     

    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

     

    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-Dichlorophenoxyacetic acid)

    94-75-7

    0.72

    10

    2,4-D (2,4-Dichlorophenoxyacetic 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

     

    U249

    Zinc phosphide, Zn3P2, when present at concentrations of 10 percent or less

    Zinc Phosphide

    1314-84-7

    CHOXD; CHRED; or CMBST

    CHOXD; CHRED; or CMBST

     

    U271

    Benomyl

    Benomyl

    17804-35-2

    0.056

    1.4

     

    U278

    Bendiocarb

    Bendiocarb

    22781-23-3

    0.056

    1.4

     

    U279

    Carbaryl

    Carbaryl

    63-25-2

    0.006

    0.14

     

    U280

    Barban

    Barban

    101-27-9

    0.056

    1.4

     

    U328

    o-Toluidine

    o-Toluidine

    95-53-4

    CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN

    CMBST

     

    U353

    p-Toluidine

    p-Toluidine

    106-49-0

    CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN

    CMBST

     

    U359

    2-Ethoxyethanol

    2-Ethoxyethanol

    110-80-5

    CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN

    CMBST

     

    U364

    Bendiocarb phenol10

    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

    A221310

    A2213

    30558-43-1

    0.042

    1.4

     

    U395

    Diethylene glycol, dicarbamate10

    Diethylene glycol, dicarbamate

    5952-26-1

    0.056

    1.4

     

    U404

    Triethylamine

    Triethylamine

    101-44-8

    0.081

    1.5

     

    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 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 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 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.
    12 Disposal of USEPA hazardous waste number K175 waste that has complied with all applicable Section 728.140 treatment standards must also be macroencapsulated in accordance with Table F of this Part unless the waste is placed in either of the following types of facilities:
      
    a) A RCRA Subtitle C monofill containing only K175 wastes that meet all applicable 40 CFR 268.40 treatment standards; or
    b) A dedicated RCRA Subtitle C landfill cell in which all other wastes being co-disposed are at pH6.0.

    BOARD NOTE: Derived from table to 40 CFR 268.40 (2000), as amended at 65 Fed. Reg. 67127 (November 8, 2000) and 66 Fed. Reg. 58258 (November 20, 2001).

     

     
    NA means not applicable.

    (Source: Amended at 26 Ill. Reg. ________, effective ______________________)

     

     
    Section 728.Table U
    Universal Treatment Standards (UTS)

     

     

     

     

    Regulated Constituent-Common Name

     

     

     

     

     

    CAS1 No.

     

     

    Wastewater Standard Concentration (in mg/l2)

    Nonwastewater Standard Concentration (in mg/kg3 unless noted as “mg/l TCLP”)

    Acenaphthylene

    208-96-8

    0.059

    3.4

    Acenaphthene

    83-32-9

    0.059

    3.4

    Acetone

    67-64-1

    0.28

    160

    Acetonitrile

    75-05-8

    5.6

    38

    Acetophenone

    96-86-2

    0.010

    9.7

    2-Acetylaminofluorene

    53-96-3

    0.059

    140

    Acrolein

    107-02-8

    0.29

    NA

    Acrylamide

    79-06-1

    19

    23

    Acrylonitrile

    107-13-1

    0.24

    84

    Aldicarb sulfone6

    1646-88-4

    0.056

    0.28

    Aldrin

    309-00-2

    0.021

    0.066

    4-Aminobiphenyl

    92-67-1

    0.13

    NA

    Aniline

    62-53-3

    0.81

    14

    Anthracene

    120-12-7

    0.059

    3.4

    Aramite

    140-57-8

    0.36

    NA

    a -BHC

    319-84-6

    0.00014

    0.066

    b -BHC

    319-85-7

    0.00014

    0.066

    d -BHC

    319-86-8

    0.023

    0.066

    c -BHC g -BHC

    58-89-9

    0.0017

    0.066

    Barban6

    101-27-9

    0.056

    1.4

    Bendiocarb6

    22781-23-3

    0.056

    1.4

    Benomyl6

    17804-35-2

    0.056

    1.4

    Benz(a)anthracene

    56-55-3

    0.059

    3.4

    Benzal chloride

    98-87-3

    0.055

    6.0

    Benzene

    71-43-2

    0.14

    10

    Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

    205-99-2

    0.11

    6.8

    Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

    207-08-9

    0.11

    6.8

    Benzo(g,h,i)perylene

    191-24-2

    0.0055

    1.8

    Benzo(a)pyrene

    50-32-8

    0.061

    3.4

    Bromodichloromethane

    75-27-4

    0.35

    15

    Methyl bromide (Bromomethane)

    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

    Butylate6

    2008-41-5

    0.042

    1.4

    Butyl benzyl phthalate

    85-68-7

    0.017

    28

    2-sec-Butyl-4,6-dinitrophenol (Dinoseb)

    88-85-7

    0.066

    2.5

    Carbaryl6

    63-25-2

    0.006

    0.14

    Carbenzadim6

    10605-21-7

    0.056

    1.4

    Carbofuran6

    1563-66-2

    0.006

    0.14

    Carbofuran phenol6

    1563-38-8

    0.056

    1.4

    Carbon disulfide

    75-15-0

    3.8

    4.8 mg/l TCLP

    Carbon tetrachloride

    56-23-5

    0.057

    6.0

    Carbosulfan6

    55285-14-8

    0.028

    1.4

    Chlordane ( a and c   g  isomers)

     

    57-74-9

    0.0033

    0.26

    p-Chloroaniline

    106-47-8

    0.46

    16

    Chlorobenzene

    108-90-7

    0.057

    6.0

    Chlorobenzilate

    510-15-6

    0.10

    NA

    2-Chloro-1,3-butadiene

    126-99-8

    0.057

    0.28

    p-Chloro-m-cresol

    59-50-7

    0.018

    14

    Chlorodibromomethane

    124-48-1

    0.057

    15

    Chloroethane

    75-00-3

    0.27

    6.0

    bis(2-Chloroethoxy)methane

    111-91-1

    0.036

    7.2

    bis(2-Chloroethyl)ether

    111-44-4

    0.033

    6.0

    2-Chloroethyl vinyl ether

    110-75-8

    0.062

    NA

    Chloroform

    67-66-3

    0.046

    6.0

    bis(2-Chloroisopropyl)ether

    39638-32-9

    0.055

    7.2

    Chloromethane (Methyl chloride)

    74-87-3

    0.19

    30

    2-Chloronaphthalene

    91-58-7

    0.055

    5.6

    2-Chlorophenol

    95-57-8

    0.044

    5.7

    3-Chloropropylene

    107-05-1

    0.036

    30

    Chrysene

    218-01-9

    0.059

    3.4

    o-Cresol

    95-48-7

    0.11

    5.6

    m-Cresol (difficult to distinguish from p-cresol)

    108-39-4

    0.77

    5.6

    p-Cresol (difficult to distinguish from m-cresol)

    106-44-5

    0.77

    5.6

    m-Cumenyl methylcarbamate6

    64-00-6

    0.056

    1.4

    Cyclohexanone

    108-94-1

    0.36

    0.75 mg/l TCLP

    o,p'-DDD

    53-19-0

    0.023

    0.087

    p,p'-DDD

    72-54-8

    0.023

    0.087

    o,p'-DDE

    3424-82-6

    0.031

    0.087

    p,p'-DDE

    72-55-9

    0.031

    0.087

    o,p'-DDT

    789-02-6

    0.0039

    0.087

    p,p'-DDT

    50-29-3

    0.0039

    0.087

    Dibenz(a,h)anthracene

    53-70-3

    0.055

    8.2

    Dibenz(a,e)pyrene

    192-65-4

    0.061

    NA

    1,2-Dibromo-3-chloropropane

    96-12-8

    0.11

    15

    1,2-Dibromoethane/Ethylene dibromide

    106-93-4

    0.028

    15

    Dibromomethane

    74-95-3

    0.11

    15

    m-Dichlorobenzene

    541-73-1

    0.036

    6.0

    o-Dichlorobenzene

    95-50-1

    0.088

    6.0

    p-Dichlorobenzene

    106-46-7

    0.090

    6.0

    Dichlorodifluoromethane

    75-71-8

    0.23

    7.2

    1,1-Dichloroethane

    75-34-3

    0.059

    6.0

    1,2-Dichloroethane

    107-06-2

    0.21

    6.0

    1,1-Dichloroethylene

    75-35-4

    0.025

    6.0

    trans-1,2-Dichloroethylene

    156-60-5

    0.054

    30

    2,4-Dichlorophenol

    120-83-2

    0.044

    14

    2,6-Dichlorophenol

    87-65-0

    0.044

    14

    2,4-Dichlorophenoxyacetic acid/2,4-D

    94-75-7

    0.72

    10

    1,2-Dichloropropane

    78-87-5

    0.85

    18

    cis-1,3-Dichloropropylene

    10061-01-5

    0.036

    18

    trans-1,3-Dichloropropylene

    10061-02-6

    0.036

    18

    Dieldrin

    60-57-1

    0.017

    0.13

    Diethyl phthalate

    84-66-2

    0.20

    28

    p-Dimethylaminoazobenzene

    60-11-7

    0.13

    NA

    2,4-Dimethyl phenol

    105-67-9

    0.036

    14

    Dimethyl phthalate

    131-11-3

    0.047

    28

    Di-n-butyl phthalate

    84-74-2

    0.057

    28

    1,4-Dinitrobenzene

    100-25-4

    0.32

    2.3

    4,6-Dinitro-o-cresol

    534-52-1

    0.28

    160

    2,4-Dinitrophenol

    51-28-5

    0.12

    160

    2,4-Dinitrotoluene

    121-14-2

    0.32

    140

    2,6-Dinitrotoluene

    606-20-2

    0.55

    28

    Di-n-octyl phthalate

    117-84-0

    0.017

    28

    Di-n-propylnitrosamine

    621-64-7

    0.40

    14

    1,4-Dioxane

    123-91-1

    12.0

    170

    Diphenylamine (difficult to distinguish from diphenylnitrosamine)

    122-39-4

    0.92

    13

    Diphenylnitrosamine (difficult to distinguish from diphenylamine)

    86-30-6

    0.92

    13

    1,2-Diphenylhydrazine

    122-66-7

    0.087

    NA

    Disulfoton

    298-04-4

    0.017

    6.2

    Dithiocarbamates (total)6

    137-30-4

    0.028

    28

    Endosulfan I

    959-98-8

    0.023

    0.066

    Endosulfan II

    33213-65-9

    0.029

    0.13

    Endosulfan sulfate

    1031-07-8

    0.029

    0.13

    Endrin

    72-20-8

    0.0028

    0.13

    Endrin aldehyde

    7421-93-4

    0.025

    0.13

    EPTC6

    759-94-4

    0.042

    1.4

    Ethyl acetate

    141-78-6

    0.34

    33

    Ethyl benzene

    100-41-4

    0.057

    10

    Ethyl cyanide (Propanenitrile)

    107-12-0

    0.24

    360

    Ethylene oxide

    75-21-8

    0.12

    NA

    Ethyl ether

    60-29-7

    0.12

    160

    bis(2-Ethylhexyl) phthalate

    117-81-7

    0.28

    28

    Ethyl methacrylate

    97-63-2

    0.14

    160

    Famphur

    52-85-7

    0.017

    15

    Fluoranthene

    206-44-0

    0.068

    3.4

    Fluorene

    86-73-7

    0.059

    3.4

    Formetanate hydrochloride6

    23422-53-9

    0.056

    1.4

    Heptachlor

    76-44-8

    0.0012

    0.066

    1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD)

    35822-46-9

    0.000035

    0.0025

    1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF)

    67562-39-4

    0.000035

    0.0025

    1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF)

    55673-89-7

    0.000035

    0.0025

    Heptachlor epoxide

    1024-57-3

    0.016

    0.066

    Hexachlorobenzene

    118-74-1

    0.055

    10

    Hexachlorobutadiene

    87-68-3

    0.055

    5.6

    Hexachlorocyclopentadiene

    77-47-4

    0.057

    2.4

    HxCDDs (All Hexachlorodibenzo-p-dioxins)

    NA

    0.000063

    0.001

    HxCDFs (All Hexachlorodibenzofurans)

    NA55684-94-1

    0.000063

    0.001

    Hexachloroethane

    67-72-1

    0.055

    30

    Hexachloropropylene

    1888-71-7

    0.035

    30

    Indeno (1,2,3-c,d) pyrene

    193-39-5

    0.0055

    3.4

    Iodomethane

    74-88-4

    0.19

    65

    Isobutyl alcohol

    78-83-1

    5.6

    170

    Isodrin

    465-73-6

    0.021

    0.066

    Isosafrole

    120-58-1

    0.081

    2.6

    Kepone

    143-50-0

    0.0011

    0.13

    Methacrylonitrile

    126-98-7

    0.24

    84

    Methanol

    67-56-1

    5.6

    0.75 mg/l TCLP

    Methapyrilene

    91-80-5

    0.081

    1.5

    Methiocarb6

    2032-65-7

    0.056

    1.4

    Methomyl6

    16752-77-5

    0.028

    0.14

    Methoxychlor

    72-43-5

    0.25

    0.18

    3-Methylcholanthrene

    56-49-5

    0.0055

    15

    4,4-Methylene bis(2-chloroaniline)

    101-14-4

    0.50

    30

    Methylene chloride

    75-09-2

    0.089

    30

    Methyl ethyl ketone

    78-93-3

    0.28

    36

    Methyl isobutyl ketone

    108-10-1

    0.14

    33

    Methyl methacrylate

    80-62-6

    0.14

    160

    Methyl methansulfonate

    66-27-3

    0.018

    NA

    Methyl parathion

    298-00-0

    0.014

    4.6

    Metolcarb6

    1129-41-5

    0.056

    1.4

    Mexacarbate6

    315-18-4

    0.056

    1.4

    Molinate6

    2212-67-1

    0.042

    1.4

    Naphthalene

    91-20-3

    0.059

    5.6

    2-Naphthylamine

    91-59-8

    0.52

    NA

    o-Nitroaniline

    88-74-4

    0.27

    14

    p-Nitroaniline

    100-01-6

    0.028

    28

    Nitrobenzene

    98-95-3

    0.068

    14

    5-Nitro-o-toluidine

    99-55-8

    0.32

    28

    o-Nitrophenol

    88-75-5

    0.028

    13

    p-Nitrophenol

    100-02-7

    0.12

    29

    N-Nitrosodiethylamine

    55-18-5

    0.40

    28

    N-Nitrosodimethylamine

    62-75-9

    0.40

    2.3

    N-Nitroso-di-n-butylamine

    924-16-3

    0.40

    17

    N-Nitrosomethylethylamine

    10595-95-6

    0.40

    2.3

    N-Nitrosomorpholine

    59-89-2

    0.40

    2.3

    N-Nitrosopiperidine

    100-75-4

    0.013

    35

    N-Nitrosopyrrolidine

    930-55-2

    0.013

    35

    1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (1,2,3,4,6,7,8,9-OCDD)

    3268-87-9

    0.000063

    0.005

    1,2,3,4,6,7,8,9-Octachlorodibenzofuran (1,2,3,4,6,7,8,9-OCDF)

    39001-02-0

    0.000063

    0.005

    Oxamyl6

    23135-22-0

    0.056

    0.28

    Parathion

    56-38-2

    0.014

    4.6

    Total PCBs (sum of all PCB isomers, or all Aroclors)8

    1336-36-3

    0.10

    10

    Pebulate6

    1114-71-2

    0.042

    1.4

    Pentachlorobenzene

    608-93-5

    0.055

    10

    PeCDDs (All Pentachlorodibenzo-p-dioxins)

    NA36088-22-9

    0.000063

    0.001

    PeCDFs (All Pentachlorodibenzofurans)

    NA30402-15-4

    0.000035

    0.001

    Pentachloroethane

    76-01-7

    0.055

    6.0

    Pentachloronitrobenzene

    82-68-8

    0.055

    4.8

    Pentachlorophenol

    87-86-5

    0.089

    7.4

    Phenacetin

    62-44-2

    0.081

    16

    Phenanthrene

    85-01-8

    0.059

    5.6

    Phenol

    108-95-2

    0.039

    6.2

    Phorate

    298-02-2

    0.021

    4.6

    Phthalic acid

    100-21-0

    0.055

    28

    Phthalic anhydride

    85-44-9

    0.055

    28

    Physostigmine6

    57-47-6

    0.056

    1.4

    Physostigmine salicylate6

    57-64-7

    0.056

    1.4

    Promecarb6

    2631-37-0

    0.056

    1.4

    Pronamide

    23950-58-5

    0.093

    1.5

    Propham6

    122-42-9

    0.056

    1.4

    Propoxur6

    114-26-1

    0.056

    1.4

    Prosulfocarb6

    52888-80-9

    0.042

    1.4

    Pyrene

    129-00-0

    0.067

    8.2

    Pyridine

    110-86-1

    0.014

    16

    Safrole

    94-59-7

    0.081

    22

    Silvex (2,4,5-TP)

    93-72-1

    0.72

    7.9

    1,2,4,5-Tetrachlorobenzene

    95-94-3

    0.055

    14

    TCDDs (All Tetrachlorodibenzo-p-dioxins)

    NA41903-57-5

    0.000063

    0.001

    TCDFs (All Tetrachlorodibenzofurans)

    NA55722-27-5

    0.000063

    0.001

    1,1,1,2-Tetrachloroethane

    630-20-6

    0.057

    6.0

    1,1,2,2-Tetrachloroethane

    79-34-5

    0.057

    6.0

    Tetrachloroethylene

    127-18-4

    0.056

    6.0

    2,3,4,6-Tetrachlorophenol

    58-90-2

    0.030

    7.4

    Thiodicarb6

    59669-26-0

    0.019

    1.4

    Thiophanate-methyl6

    23564-05-8

    0.056

    1.4

    Toluene

    108-88-3

    0.080

    10

    Toxaphene

    8001-35-2

    0.0095

    2.6

    Triallate6

    2303-17-5

    0.042

    1.4

    Tribromomethane (Bromoform)

    75-25-2

    0.63

    15

    1,2,4-Trichlorobenzene

    120-82-1

    0.055

    19

    1,1,1-Trichloroethane

    71-55-6

    0.054

    6.0

    1,1,2-Trichloroethane

    79-00-5

    0.054

    6.0

    Trichloroethylene

    79-01-6

    0.054

    6.0

    Trichloromonofluoromethane

    75-69-4

    0.020

    30

    2,4,5-Trichlorophenol

    95-95-4

    0.18

    7.4

    2,4,6-Trichlorophenol

    88-06-2

    0.035

    7.4

    2,4,5-Trichlorophenoxyacetic acid/2,4,5-T

    93-76-5

    0.72

    7.9

    1,2,3-Trichloropropane

    96-18-4

    0.85

    30

    1,1,2-Trichloro-1,2,2-trifluoroethane

    76-13-1

    0.057

    30

    Triethylamine6

    101-44-8

    0.081

    1.5

    tris-(2,3-Dibromopropyl) phosphate

    126-72-7

    0.11

    0.10

    Vernolate6

    1929-77-7

    0.042

    1.4

    Vinyl chloride

    75-01-4

    0.27

    6.0

    Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

    1330-20-7

    0.32

    30

    Antimony

    7440-36-0

    1.9

    1.15 mg/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

    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

    Cyanides (Total)4

    57-12-5

    1.2

    590

    Cyanides (Amenable)4

    57-12-5

    0.86

    30

    Fluoride5

    16984-48-8

    35

    NA

    Lead

    7439-92-1

    0.69

    0.75 mg/l TCLP

    Mercury-Nonwastewater from Retort

    7439-97-6

    NA

    0.20 mg/l TCLP

    Mercury-All Others

    7439-97-6

    0.15

    0.025 mg/l TCLP

    Nickel

    7440-02-0

    3.98

    11 mg/l TCLP

    Selenium7

    7782-49-2

    0.82

    5.7 mg/l TCLP

    Silver

    7440-22-4

    0.43

    0.14 mg/l TCLP

    Sulfide

    18496-25-8

    14

    NA

    Thallium

    7440-28-0

    1.4

    0.20 mg/l TCLP

    Vanadium5

    7440-62-2

    4.3

    1.6 mg/l TCLP

    Zinc5

    7440-66-6

    2.61

    4.3 mg/l TCLP

     

            
    1 CAS means Chemical Abstract Services. When the waste code or regulated constituents are described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only.
    2 Concentration standards for wastewaters are expressed in mg/l are based on analysis of composite samples.
    3 Except for metals (EP or TCLP) and cyanides (total and amenable), the nonwastewater treatment standards expressed as a concentration were established, in part, based on incineration in units operated in accordance with the technical requirements of 35 Ill. Adm. Code 724.Subpart O or 35 Ill. Adm. Code 725.Subpart O or on combustion in fuel substitution units operating in accordance with applicable technical requirements. A facility may comply with these treatment standards according to provisions in Section 728.140(d). All concentration standards for nonwastewaters are based on analysis of grab samples.
    4 Both Cyanides (Total) and Cyanides (Amenable) for nonwastewaters are to be analyzed using Method 9010 or 9012, found in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA Publication SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111, with a sample size of 10 grams and a distillation time of one hour and 15 minutes.
    5 These constituents are not “underlying hazardous constituents” in characteristic wastes, according to the definition at Section 728.102(i).
    6 This footnote corresponds with footnote 6 to the table to 40 CFR 268.48(a), which has already expired by its own terms. This statement maintains structural consistency with the federal regulations.
    7 This constituent is not an underlying hazardous constituent, as defined at Section 728.102(i), because its UTS level is greater than its TC level. Thus, a treated selenium waste would always be characteristically hazardous unless it is treated to below its characteristic level.
    8 This standard is temporarily deferred for soil exhibiting a hazardous characteristic due to USEPA hazardous waste numbers D004 through D011 only.

    Note: NA means not applicable.

     

    BOARD NOTE: Derived from table to 40 CFR 268.48(a) (2000), as amended at 65 Fed. Reg. 81381 (December 26, 2000).

     

    (Source: Amended at 26 Ill. Reg. ________, effective ______________________)

     

     

    TITLE 35: ENVIRONMENTAL PROTECTION

    SUBTITLE G: WASTE DISPOSAL

    CHAPTER I: POLLUTION CONTROL BOARD

    SUBCHAPTER d: UNDERGROUND INJECTION CONTROL AND UNDERGROUND STORAGE TANK PROGRAMS

     

    PART 738

    HAZARDOUS WASTE INJECTION RESTRICTIONS

     

    SUBPART A: GENERAL

    Section

     
    738.101 Purpose, Scope, and Applicability
    738.102 Definitions
    738.103 Dilution Prohibited as a Substitute for Treatment
    738.104 Case-by-Case Extensions of an Effective Date
    738.105 Waste Analysis

    SUBPART B: PROHIBITIONS ON INJECTION

    Section

     
    738.110 Waste Specific Prohibitions - Solvent Wastes
    738.111 Waste Specific Prohibitions - Dioxin-Containing Wastes
    738.112 Waste Specific Prohibitions - California List Wastes
    738.114 Waste Specific Prohibitions - First Third Wastes
    738.115 Waste Specific Prohibitions - Second Third Wastes
    738.116 Waste Specific Prohibitions - Third Third Wastes
    738.117 Waste-Specific Prohibitions - Newly-Listed Wastes
    738.118 Waste-Specific Prohibitions - Newly-Listed and Identified Wastes

    SUBPART C: PETITION STANDARDS AND PROCEDURES

    Section

     
    738.120 Petitions to Allow Injection of a Prohibited Waste
    738.121 Required Information to Support Petitions
    738.122 Submission, Review and Approval or Denial of Petitions
    738.123 Review of Adjusted Standards
    738.124 Termination of Adjusted Standards Approved Petition

    AUTHORITY: Implementing Sections 7.2, 13, and 22.4 and authorized by Section 27 of the Environmental Protection Act [415 ILCS 5/7.2, 13, 22.4, and 27].

     

    SOURCE: Adopted in R89-2 at 14 Ill. Reg. 3059, effective February 20, 1990; amended in R89-11 at 14 Ill. Reg. 11948, effective July 9, 1990; amended in R90-14 at 15 Ill. Reg. 11425, effective July 24, 1991; amended in R92-13 at 17 Ill. Reg. 6190, effective April 5, 1993; amended in R93-6 at 17 Ill. Reg. 15641, effective September 14, 1993; amended in R95-4 at 19 Ill. Reg. 9501, effective June 27, 1995; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 238, effective December 16, 1997; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17486, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1695, effective January 19, 1999; amended in R00-11/R01-1 at 24 Ill. Reg. 18576, effective December 7, 2000; amended in R01-21/R01-23 at 25 Ill. Reg. 9161, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. ________, effective ______________________.

     

     

    SUBPART B: PROHIBITIONS ON INJECTION

     

               
    Section 738.118
    Waste-Specific Prohibitions - Newly-Listed and Identified Wastes
    a) All newly identified D004 through D011 wastes and characteristic mineral processing wastes, except those identified in subsection (b) of this Section, are prohibited from underground injection.
    b) Characteristic hazardous wastes from titanium dioxide mineral processing, and radioactive wastes mixed with newly identified D004 through D011 or mixed with newly identified characteristic mineral processing wastes, are prohibited from underground injection.
    c) The wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous waste numbers F032, F034, F035 are prohibited from underground injection.
    d) The wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous waste numbers F032, F034, F035 that are mixed with radioactive wastes are prohibited from underground injection.
    e) The wastes specified in 35 Ill. Adm. Code 721.132 as having the following USEPA hazardous waste numbers are prohibited from underground injection: K156, K157, K158, K159, K160, K161, P127, P128, P185, P188, P189, P190, P191, P192, P194, P196, P197, P198, P199, P201, P202, P203, P204, P205, U271, U277, U278, U279, U280, U364, U365, U366, U367, U372, U373, U375, U376, U377, U378, U379, U381, U382, U383, U384, U385, U386, U387, U389, U390, U391, U392, U393, U394, U395, U396, U400, U401, U402, U403, U404, U407, U409, U410, and U411.
    f) The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste number K088 is prohibited from underground injection.
    g) The wastes specified in 35 Ill. Adm. Code 721 as having the following USEPA hazardous waste numbers and Mixed TC/Radioactive wastes are prohibited from underground injection: D018, D019, D020, D021, D022, D023, D024, D025, D026, D027, D028, D029, D030, D031, D032, D033, D034, D035, D036, D037, D038, D039, D040, D041, D042, and D043.
    h) This subsection corresponds with 40 CFR 148.18(h), which USEPA has removed and marked “reserved.” This statement maintains structural consistency with the federal regulations.
    i) The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste numbers K169 through K172 are prohibited from underground injection.
    j) The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste numbers K174 and K175 are prohibited from underground injection.
     
    k) Effective May 20, 2002, the wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste numbers K176, K177, and K178 are prohibited from underground injection.
     
    kl) The requirements of subsections (a) through (j) (k) of this Section do not apply under any of the following circumstances:
       
    1) If the wastes meet or are treated to meet the applicable standards specified in Subpart D of 35 Ill. Adm. Code 728; or
    2) If an exemption from a prohibition has been granted in response to a petition under Subpart C of this Part; or
    3) During the period of extension of the applicable effective date, if an extension has been granted under Section 738.104.

    (Source: Amended at 26 Ill. Reg. ________, effective ______________________)

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