1. SUBPART A:  GENERAL
      2. SUBPART B:  SCHEDULE FOR LAND DISPOSAL PROHIBITION AND ESTABLISHMENT OF TREATMENT STANDARDS
      3. SUBPART C:  PROHIBITION ON LAND DISPOSAL
        1. 728.120 Waste-Specific Prohibitions: Dyes and Pigments Production Wastes
      4. SUBPART D:  TREATMENT STANDARDS
      5. SUBPART E:  PROHIBITIONS ON STORAGE
      6. SUBPART A: GENERAL
        1. Section 728.101 Purpose, Scope, and Applicability
        2. Section 728.102 Definitions
        3. Section 728.103 Dilution Prohibited as a Substitute for Treatment
        4. Section 728.104 Treatment Surface Impoundment Exemption
        5. Section 728.105 Procedures for Case-by-Case Extensions to an Effective Date
        6. Section 728.106 Petitions to Allow Land Disposal of a Waste Prohibited Pursuant to Subpart C
        7. Section 728.107 Testing, Tracking, and Recordkeeping Requirements for Generators, Reverse Distributors, Treaters, and Disposal Facilities
        8. Section 728.108 Landfill and Surface Impoundment Disposal Restrictions (Repealed)
        9. Section 728.109 Special Rules for Characteristic Wastes
      7. SUBPART B: SCHEDULE FOR LAND DISPOSAL PROHIBITION AND ESTABLISHMENT OF TREATMENT STANDARDS
        1. Section 728.110 First Third (Repealed)
        2. Section 728.111 Second Third (Repealed)
        3. Section 728.112 Third Third (Repealed)
        4. Section 728.113 Newly Listed Wastes
        5. Section 728.114 Surface Impoundment Exemptions
        6. Section 728.120 Waste-Specific Prohibitions: Dyes and Pigments Production Wastes
        7. Section 728.130 Waste-Specific Prohibitions: Wood Preserving Wastes
        8. Section 728.131 Waste-Specific Prohibitions: Dioxin-Containing Wastes
        9. Section 728.132 Waste-Specific Prohibitions: Soils Exhibiting the Toxicity Characteristic for Metals and Containing PCBs
        10. Section 728.133 Waste-Specific Prohibitions: Chlorinated Aliphatic Wastes
        11. Section 728.134 Waste-Specific Prohibitions: Toxicity Characteristic Metal Wastes
        12. Section 728.135 Waste-Specific Prohibitions: Petroleum Refining Wastes
        13. Section 728.136 Waste-Specific Prohibitions: Inorganic Chemical Wastes
        14. Section 728.137 Waste-Specific Prohibitions: Ignitable and Corrosive Characteristic Wastes Whose Treatment Standards Were Vacated
        15. Section 728.138 Waste-Specific Prohibitions: Newly-Identified Organic Toxicity Characteristic Wastes and Newly-Listed Coke By-Product and Chlorotoluene Production Wastes
        16. Section 728.139 Waste-Specific Prohibitions: Spent Aluminum Potliners and Carbamate Wastes
      8. SUBPART D:  TREATMENT STANDARDS
        1. Section 728.140 Applicability of Treatment Standards
        2. Section 728.141 Treatment Standards Expressed as Concentrations in Waste Extract
        3. Section 728.142 Treatment Standards Expressed as Specified Technologies
        4. Section 728.143 Treatment Standards Expressed as Waste Concentrations
        5. Section 728.144 USEPA Variance from a Treatment Standard
        6. Section 728.145 Treatment Standards for Hazardous Debris
        7. Section 728.146 Alternative Treatment Standards Based on HTMR
        8. Section 728.148 Universal Treatment Standards
        9. Section 728.149 Alternative LDR Treatment Standards for Contaminated Soil
        10. Section 728.APPENDIX G Federal Effective Dates
        11. Section 728.APPENDIX H National Capacity LDR Variances for UIC Wastes
        12. Section 728.APPENDIX I EP Toxicity Test Method and Structural Integrity Test
        13. Section 728.Appendix J Recordkeeping, Notification, and Certification Requirements (Repealed)
        14. Section 728.APPENDIX K Metal-Bearing Wastes Prohibited from Dilution in a Combustion Unit According to Section 728.103(c)
        15. Section 728.TABLE A Constituent Concentrations in Waste Extract (CCWE)
        16. Section 728.TABLE B Constituent Concentrations in Wastes (CCW)
        17. Section 728.TABLE C Technology Codes and Description of Technology-Based Standards
        18. Section 728.TABLE D Technology-Based Standards by USEPA Hazardous Waste Number
        19. Section 728.TABLE E Standards for Radioactive Mixed Waste
        20. Section 728.TABLE F Alternative Treatment Standards For Hazardous Debris
        21. Section 728.TABLE G Alternative Treatment Standards Based on HTMR
        22. Section 728.TABLE H Wastes Excluded from CCW Treatment Standards
        23. Section 728.TABLE I Generator Paperwork Requirements
        24. Section 728.TABLE T Treatment Standards for Hazardous Wastes
        25. Section 728.TABLE U Universal Treatment Standards (UTS)

 

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 Pursuant to Subpart C
728.107  Testing, Tracking, and Recordkeeping Requirements for Generators, Reverse Distributors, Treaters, and Disposal Facilities
728.108  Landfill and Surface Impoundment Disposal Restrictions (Repealed)

728.109  Special Rules for Characteristic Wastes


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


Section
728.110  First Third (Repealed)
728.111  Second Third (Repealed)
728.112  Third Third (Repealed)
728.113  Newly Listed Wastes

728.114  Surface Impoundment Exemptions


SUBPART C:  PROHIBITION ON LAND DISPOSAL


Section



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

728.139  Waste-Specific Prohibitions:  Spent Aluminum Potliners and Carbamate Wastes


SUBPART D:  TREATMENT STANDARDS


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

728.149  Alternative LDR Treatment Standards for Contaminated Soil


SUBPART E:  PROHIBITIONS ON STORAGE


Section

728.150  Prohibitions on Storage of Restricted Wastes

728.APPENDIX A  Toxicity Characteristic Leaching Procedure (TCLP) (Repealed)
728.APPENDIX B  Treatment Standards (As concentrations in the Treatment Residual Extract) (Repealed)
728.APPENDIX C  List of Halogenated Organic Compounds Regulated under Section 728.132
728.APPENDIX D  Wastes Excluded from Lab Packs
728.APPENDIX E  Organic Lab Packs (Repealed)
728.APPENDIX F  Technologies to Achieve Deactivation of Characteristics
728.APPENDIX G  Federal Effective Dates
728.APPENDIX H  National Capacity LDR Variances for UIC Wastes
728.APPENDIX I  EP Toxicity Test Method and Structural Integrity Test
728.APPENDIX J  Recordkeeping, Notification, and Certification Requirements (Repealed)
728.APPENDIX K  Metal-Bearing Wastes Prohibited from Dilution in a Combustion Unit According to Section 728.103(c)
728.TABLE A  Constituent Concentrations in Waste Extract (CCWE)
728.TABLE B  Constituent Concentrations in Wastes (CCW)
728.TABLE C  Technology Codes and Description of Technology-Based Standards
728.TABLE D  Technology-Based Standards by USEPA Hazardous Waste Number
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 in R90-11 at 15 Ill. Reg. 11937, effective August 12, 1991; amendment withdrawn at 15 Ill. Reg. 14716, October 11, 1991; amended in R91-13 at 16 Ill. Reg. 9619, effective June 9, 1992; amended in R92-10 at 17 Ill. Reg. 5727, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20692, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6799, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12203, effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17563, effective November 23, 1994; amended in R95-6 at 19 Ill. Reg. 9660, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 11100, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 783, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7685, effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17706, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1964, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9204, effective July 26, 1999; amended in R00-13 at 24 Ill. Reg. 9623, effective June 20, 2000; amended in R01-3 at 25 Ill. Reg. 1296, effective January 11, 2001; amended in R01-21/R01-23 at 25 Ill. Reg. 9181, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. 6687, effective April 22, 2002; amended in R03-18 at 27 Ill. Reg. 13045, effective July 17, 2003; amended in R05-8 at 29 Ill. Reg. 6049, effective April 13, 2005; amended in R06-5/R06-6/R06-7 at 30 Ill. Reg. 3800, effective February 23, 2006; amended in R06-16/R06-17/R06-18 at 31 Ill. Reg. 1254, effective December 20, 2006; amended in R07-5/R07-14 at 32 Ill. Reg. 12840, effective July 14, 2008; amended in R09-3 at 33 Ill. Reg. 1186, effective December 30, 2008; amended in R11-2/R11-16 at 35 Ill. Reg. 18131, effective October 14, 2011; amended in R12-7 at 36 Ill. Reg. 8790, effective June 4, 2012; amended in R13-15 at 37 Ill. Reg. 17951, effective October 24, 2013; amended in R16-7 at 40 Ill. Reg. 12052, effective August 9, 2016; amended in R17-14/R17-15/R18-12/R18-31 at 42 Ill. Reg. 24924, effective November 19, 2018; amended in R20-8/R20-16 at 44 Ill. Reg. 15055, effective September 3, 2020.

 


SUBPART A: GENERAL


Section 728.101 Purpose, Scope, and Applicability

a)  This Part identifies hazardous wastes that are restricted from land disposal and defines those limited circumstances under which an otherwise prohibited waste may continue to be land disposed.

b)  Except as specifically provided otherwise in this Part or 35 Ill. Adm. Code 721, the requirements of this Part apply to persons that generate or transport hazardous waste and to owners and operators of hazardous waste treatment, storage, and disposal facilities.

c)  Restricted wastes may continue to be land disposed as follows:

1)  If a person has been granted an extension to the effective date of a prohibition under Subpart C or under Section 728.105, with respect to those wastes covered by the extension;

2)  If a person has been granted an exemption from a prohibition under a petition under Section 728.106, with respect to those wastes and units covered by the petition;

3)  A waste that is hazardous only because it exhibits a characteristic of hazardous waste and that is otherwise prohibited under this Part is not prohibited if the following is true of the waste:

A)  The waste is disposed into a non-hazardous or hazardous waste injection well, as defined in 35 Ill. Adm. Code 704.106(a); and

B)  The waste does not exhibit any prohibited characteristic of hazardous waste identified in Subpart C of 35 Ill. Adm. Code 721 at the point of injection.

4)  A waste that is hazardous only because it exhibits a characteristic of hazardous waste and that is otherwise prohibited under this Part is not prohibited if the waste meets any of the following criteria, unless the waste is subject to a specified method of treatment other than DEACT in Section 728.140 or is D003 reactive cyanide:

A)  Any of the following is true of either treatment or management of the waste:

i)  The waste is managed in a treatment system that subsequently discharges to waters of the United States under a permit issued under 35 Ill. Adm. Code 309;

ii)  The waste is treated for purposes of the pretreatment requirements of 35 Ill. Adm. Code 307 and 310; or

iii)  The waste is managed in a zero discharge system engaged in Clean Water Act (CWA)-equivalent treatment, as defined in Section 728.137(a); and

B)  The waste no longer exhibits a prohibited characteristic of hazardous waste at the point of land disposal (i.e., placement in a surface impoundment).

d)  This Part does not affect the availability of a waiver under Section 121(d)(4) of the federal Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (CERCLA) (42 USC 9621(d)(4)).

e)  The following hazardous wastes are not subject to any provision of this Part:

1)  Waste generated by a VSQG, as defined in 35 Ill. Adm. Code 720.110;

2)  Waste pesticide that a farmer disposes of under 35 Ill. Adm. Code 722.170;

3)  Waste identified or listed as hazardous after November 8, 1984, for which USEPA has not promulgated a land disposal prohibition or treatment standard; and

4)  De minimis losses of waste that exhibits a characteristic of hazardous waste to wastewaters are not considered to be prohibited waste and are defined as losses from normal material handling operations (e.g., spills from the unloading or transfer of materials from bins or other containers or leaks from pipes, valves, or other devices used to transfer materials); minor leaks of process equipment, storage tanks, or containers; leaks from well-maintained pump packings and seals; sample purgings; relief device discharges; discharges from safety showers and rinsing and cleaning of personal safety equipment; rinsate from empty containers or from containers that are rendered empty by that rinsing; and laboratory waste that does not exceed one percent of the total flow of wastewater into the facility’s headworks on an annual basis, or with a combined annualized average concentration not exceeding one part per million (ppm) in the headworks of the facility’s wastewater treatment or pretreatment facility.

f)  A universal waste handler or universal waste transporter (as defined in 35 Ill. Adm. Code 720.110) is exempt from Sections 728.107 and 728.150 for the hazardous wastes listed below. Such a handler or transporter is subject to regulation under 35 Ill. Adm. Code 733.

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

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

3)  Mercury-containing equipment, as described in 35 Ill. Adm. Code 733.104;

4)  Lamps, as described in 35 Ill. Adm. Code 733.105; and
5)  Aerosol cans, as described in 35 Ill. Adm. Code 733.106.

g)  This Part is cumulative with the land disposal restrictions of 35 Ill. Adm. Code 729. The Environmental Protection Agency (Agency) must not issue a wastestream authorization under 35 Ill. Adm. Code 709 or Section 22.6 or 39(h) of the Act unless the waste meets the requirements of this Part as well as 35 Ill. Adm. Code 729.

h)  Electronic Reporting. The filing of any document under any provision of this Part as an electronic document is subject to 35 Ill. Adm. Code 720.104.

BOARD NOTE: Subsection (h) is derived from 40 CFR 3, 271.10(b), 271.11(b), and 271.12(h).

(Source: Amended at 44 Ill. Reg. 15495, effective September 3, 2020)


Section 728.102 Definitions

When used in this Part, the following terms have the meanings given below.  All other terms have the meanings given under 35 Ill. Adm. Code 702.110, 720.110, or 721.102 through 721.104.

“Agency” means the Illinois Environmental Protection Agency.

“Board” means the Illinois Pollution Control Board.

“CERCLA” means the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (42 USC 9601 et seq.)

“Debris” means solid material exceeding a 60 mm particle size that is intended for disposal and that is a manufactured object; plant or animal matter; or natural geologic material.  However, the following materials are not debris:  any material for which a specific treatment standard is provided in Subpart D, namely lead acid batteries, cadmium batteries, and radioactive lead solids; process residuals, such as smelter slag and residues from the treatment of waste, wastewater, sludges, or air emission residues; and intact containers of hazardous waste that are not ruptured and that retain at least 75 percent of their original volume.  A mixture of debris that has not been treated to the standards provided by Section 728.145 and other material is subject to regulation as debris if the mixture is comprised primarily of debris, by volume, based on visual inspection.

“Halogenated organic compounds” or “HOCs” means those compounds having a carbon-halogen bond that are listed under Appendix C.

“Hazardous constituent” or “hazardous constituents” means those constituents listed in Appendix H to 35 Ill. Adm. Code 721.

“Hazardous debris” means debris that contains a hazardous waste listed in Subpart D of 35 Ill. Adm. Code 721 or that exhibits a characteristic of hazardous waste identified in Subpart C of 35 Ill. Adm. Code 721. Any deliberate mixing of prohibited waste with debris that changes its treatment classification (i.e., from waste to hazardous debris) is not allowed under the dilution prohibition in Section 728.103.

“Inorganic metal-bearing waste” is one for which USEPA has established treatment standards for metal hazardous constituents that does not otherwise contain significant organic or cyanide content, as described in Section 728.103(b)(1), and which is specifically listed in Appendix K.

“Land disposal” means placement in or on the land, except in a corrective action management unit or staging pile, and “land disposal” includes, but is not limited to, placement in a landfill, surface impoundment, waste pile, injection well, land treatment facility, salt dome formation, salt bed formation, underground mine or cave, or placement in a concrete vault or bunker intended for disposal purposes.

“Land disposal restriction” or “LDR” is a restriction imposed on the land disposal of a hazardous waste pursuant to this Part or 35 Ill. Adm. Code 738. The land disposal of hazardous waste is generally prohibited, except where the activity constituting land disposal is specifically allowed, pursuant to this Part or 35 Ill. Adm. Code 738.

BOARD NOTE: The Board added this definition based on the preamble discussions at 51 Fed. Reg. 40572, 40573-74 (November 7, 1986) and 53 Fed. Reg. 28118, 28119-20 (July 26, 1988). The USEPA publication “Terms of Environment Glossary, Abbreviations, and Acronyms” (December 1997), USEPA, Communications, Education, and Public Affairs, EPA 175/B-97-001, defines “land disposal restrictions” as follows: “Rules that require hazardous wastes to be treated before disposal on land to destroy or immobilize hazardous constituents that might migrate into soil and ground water.”

“Nonwastewaters” are wastes that do not meet the criteria for “wastewaters” in this Section.

“Polychlorinated biphenyls” or “PCBs” are halogenated organic compounds defined in accordance with federal 40 CFR 761.3 (Definitions), incorporated by reference in 35 Ill. Adm. Code 720.111(b).

“ppm” means parts per million.

“RCRA corrective action” means corrective action taken under 35 Ill. Adm. Code 724.200 or 725.193, federal 40 CFR 264.100 or 265.93, or similar regulations in other states with RCRA programs authorized by USEPA pursuant to 40 CFR 271.

“Soil” means unconsolidated earth material composing the superficial geologic strata (material overlying bedrock), consisting of clay, silt, sand, or gravel size particles, as classified by the United States Natural Resources Conservation Service, or a mixture of such materials with liquids, sludges, or solids that is inseparable by simple mechanical removal processes and which is made up primarily of soil by volume based on visual inspection. Any deliberate mixing of prohibited waste with debris that changes its treatment classification (i.e., from waste to hazardous debris) is not allowed under the dilution prohibition in Section 728.103.

“Underlying hazardous constituent” means any constituent listed in Table U, “Universal Treatment Standards (UTS)”, except fluoride, selenium, sulfides, vanadium, and zinc, that can reasonably be expected to be present at the point of generation of the hazardous waste at a concentration above the constituent-specific UTS treatment standard.

“USEPA” or “U.S. EPA” means the United States Environmental Protection Agency.

“Wastewaters” are wastes that contain less than one percent by weight total organic carbon (TOC) and less than one percent by weight total suspended solids (TSS).

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.103 Dilution Prohibited as a Substitute for Treatment

a)  Except as provided in subsection (b), no generator, transporter, handler, or owner or operator of a treatment, storage, or disposal facility must in any way dilute a restricted waste or the residual from treatment of a restricted waste as a substitute for adequate treatment to achieve compliance with Subpart D, to circumvent the effective date of a prohibition in Subpart C, to otherwise avoid a prohibition in Subpart C, or to circumvent a land disposal restriction imposed by RCRA section 3004 (42 USC 6924).

b)  Dilution of waste that is hazardous only because it exhibits a characteristic of hazardous waste in a treatment system that treats wastes subsequently discharged to a water of the State pursuant to an NPDES permit issued under 35 Ill. Adm. Code 309, that treats wastes in a CWA-equivalent treatment system, or that treats wastes for purposes of pretreatment requirements under 35 Ill. Adm. Code 310 is not impermissible dilution for purposes of this Section, unless a method other than DEACT has been specified in Section 728.140 as the treatment standard or unless the waste is a D003 reactive cyanide wastewater or nonwastewater.

c)  Combustion of waste designated by any of the USEPA hazardous waste numbers listed in Appendix J is prohibited, unless the waste can be demonstrated to comply with one or more of the following criteria at the point of generation or after any bona fide treatment, such as cyanide destruction prior to combustion (unless otherwise specifically prohibited from combustion):

1)  The waste contains hazardous organic constituents or cyanide at levels exceeding the constituent-specific treatment standard found in Section 728.148;

2)  The waste consists of organic, debris-like materials (e.g., wood, paper, plastic, or cloth) contaminated with an inorganic metal-bearing hazardous waste;

3)  The waste has reasonable heating value, such as greater than or equal to 5,000 Btu per pound, at the point of generation;

4)  The waste is co-generated with wastes for which combustion is a required method of treatment;

5)  The waste is subject to any federal or state requirements necessitating reduction of organics (including biological agents); or

6)  The waste contains greater than one percent Total Organic Carbon (TOC).

d)  It is a form of impermissible dilution, and therefore prohibited, to add iron filings or other metallic forms of iron to lead-containing hazardous wastes in order to achieve any land disposal restriction treatment standard for lead.  Lead-containing wastes include D008 wastes (wastes exhibiting a characteristic due to the presence of lead), all characteristic wastes containing lead as an underlying hazardous constituent, listed wastes containing lead as a regulated constituent, and hazardous media containing any of the aforementioned lead-containing wastes.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.104 Treatment Surface Impoundment Exemption

a)  Wastes that are otherwise prohibited from land disposal under this Part may be treated in a surface impoundment or series of impoundments provided that all of the following conditions are fulfilled:

1)  Treatment of such wastes occurs in the impoundments;

2)  The following conditions are met:

A)  Sampling and Testing.  For wastes with treatment standards in Subpart D or prohibition levels in Subpart C, the residues from treatment are analyzed, as specified in Section 728.107 or 728.132, to determine if they meet the applicable treatment standards or, where no treatment standards have been established for the waste, the applicable prohibition levels.  The sampling method, specified in the waste analysis plan under 35 Ill. Adm. Code 724.113 or 725.113, must be designed such that representative samples of the sludge and the supernatant are tested separately rather than mixed to form homogeneous samples.

B)  Removal.  The following treatment residues (including any liquid waste) must be removed at least annually:  residues that do not meet the treatment standards promulgated under Subpart D; residues that do not meet the prohibition levels established under Subpart C or imposed by federal statute (where no treatment standards have been established); residues that are from the treatment of wastes prohibited from land disposal under Subpart C (where no treatment standards have been established and no prohibition levels apply); or residues from managing listed wastes that are not delisted under 35 Ill. Adm. Code 720.122.  If the volume of liquid flowing through the impoundment or series of impoundments annually is greater than the volume of the impoundment or impoundments, this flow-through constitutes removal of the supernatant for the purpose of this requirement.

C)  Subsequent Management.  Treatment residues must not be placed in any other surface impoundment for subsequent management.

D)  Recordkeeping.  Sampling, testing, and recordkeeping provisions of 35 Ill. Adm. Code 724.113 or 725.113 apply;

3)  The impoundment meets the design requirements of 35 Ill. Adm. Code 724.321(c) or 725.321(a) even though the unit may not be new, expanded or a replacement, and must be in compliance with applicable groundwater monitoring requirements of Subpart F of 35 Ill. Adm. Code 724 or Subpart F of 35 Ill. Adm. Code 725, unless any of the following conditions is fulfilled:

A)  The impoundment is exempted pursuant to 35 Ill. Adm. Code 724.321(d) or (e), or to 35 Ill. Adm. Code 725.321(c) or (d);

B)  Upon application by the owner or operator, the Agency has by permit provided that the requirements of this Part do not apply on the basis that the surface impoundment fulfills all of the following conditions:

i)  The impoundment has at least one liner, for which there is no evidence that such liner is leaking;

ii)  The impoundment is located more than one-quarter mile from an underground source of drinking water; and

iii)  The impoundment is in compliance with generally applicable groundwater monitoring requirements for facilities with permits; or

C)  Upon application by the owner or operator, the Board has, pursuant to Subpart D of 35 Ill. Adm. Code 104, granted an adjusted standard from the requirements of this Part.  The justification for such an adjusted standard must be a demonstration that the surface impoundment is located, designed, and operated so as to assure that there will be no migration of any hazardous constituent into groundwater or surface water at any future time; and

4)  The owner or operator submits to the Agency a written certification that the requirements of subsection (a)(3) have been met.  The following certification is required:

I certify under penalty of law that the requirements of 35 Ill. Adm. Code 728.104(a)(3) have been met for all surface impoundments being used to treat restricted wastes.  I believe that the submitted information is true, accurate, and complete.  I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment.

b)  Evaporation of hazardous constituents as the principal means of treatment is not considered to be a treatment for purposes of an exemption under this Section.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.105 Procedures for Case-by-Case Extensions to an Effective Date

Any person may apply to USEPA for an extension of an effective date pursuant to 40 CFR 268.5. Any extension that is granted by USEPA will be deemed an extension of the effective date of the derivative Board rule.

(Source: Amended at 30 Ill. Reg. 3800, effective February 23, 2006)


Section 728.106 Petitions to Allow Land Disposal of a Waste Prohibited Pursuant to Subpart C

a)  Any person seeking an exemption from a prohibition pursuant to Subpart C for the disposal of a restricted hazardous waste in a particular unit or units must submit a petition to the Board demonstrating, to a reasonable degree of certainty, that there will be no migration of hazardous constituents from the disposal unit or injection zone for as long as the wastes remain hazardous. The demonstration must include the following components:

1)  An identification of the specific waste and the specific unit for which the demonstration will be made;

2)  A waste analysis to describe fully the chemical and physical characteristics of the subject waste;

3)  A comprehensive characterization of the disposal unit site including an analysis of background air, soil, and water quality;

4)  A monitoring plan that detects migration at the earliest practical time;

5)  Sufficient information to assure the Agency that the owner or operator of a land disposal unit receiving restricted wastes will comply with other applicable federal, State, and local laws;

6)  Whether the facility is in interim status, or, if a RCRA permit has been issued, the term of the permit.

b)  The demonstration referred to in subsection (a) must meet the following criteria:

1)  All waste and environmental sampling, test and analysis data must be accurate and reproducible to the extent that state-of-the-art techniques allow;

2)  All sampling, testing and estimation techniques for chemical and physical properties of the waste and all environmental parameters must conform with “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, and with “Generic Quality Assurance Project Plan for Land Disposal Restrictions Program”, USEPA publication number EPA-530/SW-87-011, each incorporated by reference in 35 Ill. Adm. Code 720.111.

3)  Simulation models must be calibrated for the specific waste and site conditions, and verified for accuracy by comparison with actual measurements;

4)  A quality assurance and quality control plan that addresses all aspects of the demonstration and conforms with “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, and with “Generic Quality Assurance Project Plan for Land Disposal Restrictions Program”, USEPA publication number EPA-530/SW-87-011; and

5)  An analysis must be performed to identify and quantify any aspects of the demonstration that contribute significantly to uncertainty. This analysis must include an evaluation of the consequences of predictable future events, including, but not limited to, earthquakes, floods, severe storm events, droughts, or other natural phenomena.

c)  Each petition referred to in subsection (a) must include the following:

1)  A monitoring plan that describes the monitoring program installed at or around the unit to verify continued compliance with the conditions of the adjusted standard. This monitoring plan must provide information on the monitoring of the unit or the environment around the unit. The following specific information must be included in the plan:

A)  The media monitored in the cases where monitoring of the environment around the unit is required;

B)  The type of monitoring conducted at the unit, in the cases where monitoring of the unit is required;

C)  The location of the monitoring stations;

D)  The monitoring interval (frequency of monitoring at each station);

E)  The specific hazardous constituents to be monitored;

F)  The implementation schedule for the monitoring program;

G)  The equipment used at the monitoring stations;

H)  The sampling and analytical techniques employed; and

I)  The data recording and reporting procedures.

2)  Where applicable, the monitoring program described in subsection (c)(1) must be in place for a period of time specified by the Board, as part of its approval of the petition, prior to receipt of prohibited waste at the unit.

3)  The monitoring data collected according to the monitoring plan specified pursuant to subsection (c)(1) must be sent to the Agency according to a format and schedule specified and approved in the monitoring plan.

4)  A copy of the monitoring data collected under the monitoring plan specified pursuant to subsection (c)(1) must be kept on-site at the facility in the operating record.

5)  The monitoring program specified pursuant to subsection (c)(1) must meet the following criteria:

A)  All sampling, testing, and analytical data must be approved by the Board and must provide data that is accurate and reproducible;

B)  All estimation and monitoring techniques must be approved by the Board; and

C)  A quality assurance and quality control plan addressing all aspects of the monitoring program must be provided to and approved by the Board.

d)  Each petition must be submitted to the Board as provided in Subpart D of 35 Ill. Adm. Code 104.

e)  After a petition has been approved, the owner or operator must report any changes in conditions at the unit or the environment around the unit that significantly depart from the conditions described in the petition and affect the potential for migration of hazardous constituents from the units as follows:

1)  If the owner or operator plans to make changes to the unit design, construction, or operation, the owner or operator must do the following at least 90 days prior to making the change:

A)  File a petition for modification of or a new petition to amend an adjusted standard with the Board reflecting the changes; or

B)  Demonstrate to the Agency that the change can be made consistent with the conditions of the existing adjusted standard.

2)  If the owner or operator discovers that a condition at the site that was modeled or predicted in the petition does not occur as predicted, this change must be reported, in writing, to the Agency within 10 days after discovering the change. The Agency must determine whether the reported change from the terms of the petition requires further action, which may include termination of waste acceptance, a petition for modification of or a new petition for an adjusted standard.

f)  If there is migration of hazardous constituents from the unit, as determined by the owner or operator, the owner or operator must do the following:

1)  It must immediately suspend receipt of prohibited waste at the unit, and

2)  It must notify the Agency, in writing, within 10 days after the determination that a release has occurred.

3)  Following receipt of the notification, the Agency must do the following within 60 days after receiving notification:

A)  It must determine whether the owner or operator can continue to receive prohibited waste in the unit under the conditions of the adjusted standard.

B)  If modification or vacation of the adjusted standard is necessary, it must file a motion to modify or vacate the adjusted standard with the Board.

C)  It must determine whether further examination of any migration is required pursuant to the applicable provisions of 35 Ill. Adm. Code 724 or 725.

g)  Each petition must include the following statement signed by the petitioner or an authorized representative:

I certify under penalty of law that I have personally examined and am familiar with the information submitted in this petition and all attached documents, and that, based on my inquiry of those individuals immediately responsible for obtaining the information. I believe that submitted information is true, accurate, and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment.

h)  After receiving a petition, the Board may request any additional information that may be required to evaluate the demonstration.

i)  If approved, the petition will apply to land disposal of the specific restricted waste at the individual disposal unit described in the demonstration and will not apply to any other restricted waste at that disposal unit, or to that specific restricted waste at any other disposal unit.

j)  The Board will give public notice and provide an opportunity for public comment, as provided in Subpart D of 35 Ill. Adm. Code 104. Notice of a final decision on a petition will be published in the Environmental Register.

k)  The term of a petition granted pursuant to this Section will be no longer than the term of the RCRA permit if the disposal unit is operating pursuant to a RCRA permit, or up to a maximum of 10 years from the date of approval provided pursuant to subsection (g) if the unit is operating under interim status. In either case, the term of the granted petition expires upon the termination or denial of a RCRA permit, or upon the termination of interim status or when the volume limit of waste to be land disposed during the term of petition is reached.

l)  Prior to the Board’s decision, the applicant must comply with all restrictions on land disposal pursuant to this Part once the effective date for the waste has been reached.

m)  The petition granted by the Board does not relieve the petitioner of responsibilities in the management of hazardous waste pursuant to 35 Ill. Adm. Code 702, 703, 720 through 728, and 738.

n)  Liquid hazardous wastes containing PCBs at concentrations greater than or equal to 500 ppm are not eligible for an adjusted standard pursuant to this Section.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.107 Testing, Tracking, and Recordkeeping Requirements for Generators, Reverse Distributors, Treaters, and Disposal Facilities

a)  Requirements for Generators and Reverse Distributors

1)  A generator of a hazardous waste must determine if the waste has to be treated before it can be land disposed.  This is done by determining if the hazardous waste meets the treatment standards in Section 728.140, 728.145, or 728.149.  This determination can be made concurrently with the hazardous waste determination required in 35 Ill. Adm. Code 722.111, in either of two ways:  testing the waste or using knowledge of the waste.  If the generator tests the waste, testing determines the total concentration of hazardous constituents or the concentration of hazardous constituents in an extract of the waste obtained using Method 1311 (Toxicity Characteristic Leaching Procedure) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a), depending on whether the treatment standard for the waste is expressed as a total concentration or concentration of hazardous constituent in the waste extract.  (Alternatively, the generator must send the waste to a RCRA-permitted hazardous waste treatment facility, if the waste treatment facility must comply with the requirements of 35 Ill. Adm. Code 724.113 and subsection (b).) In addition, some hazardous wastes must be treated by particular treatment methods before they can be land disposed and some soils are contaminated by such hazardous wastes.  These treatment standards are also found in Section 728.140 and Table T, and are described in detail in Table C.  These wastes and soils contaminated with such wastes do not need to be tested (however, if they are in a waste mixture, other wastes with concentration level treatment standards must be tested).  If a generator determines that it is managing a waste or soil contaminated with a waste that displays a hazardous characteristic of ignitability, corrosivity, reactivity, or toxicity, the generator must comply with the special requirements of Section 728.109 in addition to any applicable requirements in this Section.

2)  If the waste or contaminated soil does not meet the treatment standard or if the generator chooses not to make the determination of whether its waste must be treated, the generator must send a one-time written notice to each treatment or storage facility receiving the waste with the initial shipment of waste to each treatment or storage facility, and the generator must place a copy of the one-time notice in the file.  The notice must include the information in column “728.107(a)(2)” of the Generator Paperwork Requirements Table in Table I.  (Alternatively, if the generator chooses not to make the determination of whether the waste must be treated, the notification must include the USEPA hazardous waste numbers and manifest number of the first shipment, and it must include the following statement: “This hazardous waste may or may not be subject to the LDR treatment standards. The treatment facility must make the determination.”) No further notification is necessary until such time that the waste or facility changes, in which case a new notification must be sent and a copy placed in the generator’s file.

3)  If the waste or contaminated soil meets the treatment standard at the original point of generation, the waste generator must do the following:

A)  With the initial shipment of waste to each treatment, storage, or disposal facility, the generator must send a one-time written notice to each treatment, storage, or disposal facility receiving the waste, and place a copy in its own file.  The notice must include the information indicated in column “728.107(a)(3)” of the Generator Paperwork Requirements Table in Table I and the following certification statement, signed by an authorized representative:

I certify under penalty of law that I personally have examined and am familiar with the waste through analysis and testing or through knowledge of the waste to support this certification that the waste complies with the treatment standards specified in Subpart D of 35 Ill. Adm. Code 728.  I believe that the information I submitted is true, accurate, and complete.  I am aware that there are significant penalties for submitting a false certification, including the possibility of a fine and imprisonment.

B)  For contaminated soil, with the initial shipment of wastes to each treatment, storage, or disposal facility, the generator must send a one-time written notice to each facility receiving the waste and place a copy in the file.  The notice must include the information in the column headed “(a)(3)” in Table I.

C)  If the waste changes, the generator must send a new notice and certification to the receiving facility and place a copy in its files. A generator of hazardous debris excluded from the definition of hazardous waste under 35 Ill. Adm. Code 721.103(f) is not subject to these requirements.

4)  For reporting, tracking and recordkeeping when exceptions allow certain wastes or contaminated soil that do not meet the treatment standards to be land disposed, there are certain exemptions from the requirement that hazardous wastes or contaminated soil meet treatment standards before they can be land disposed.  These include, but are not limited to, case-by-case extensions under Section 728.105, disposal in a no-migration unit under Section 728.106, or a national capacity variance or case-by-case capacity variance under Subpart C.  If a generator’s waste is so exempt, then with the initial shipment of waste, the generator must send a one-time written notice to each land disposal facility receiving the waste.  The notice must include the information indicated in column “728.107(a)(4)” of the Generator Paperwork Requirements Table in Table I.  If the waste changes, the generator must send a new notice to the receiving facility, and place a copy in its file.

5)  If a generator is managing and treating prohibited waste or contaminated soil in tanks, containers, or containment buildings regulated under 35 Ill. Adm. Code 722.115, 722.116, and 722.117 to meet applicable LDR treatment standards found at Section 728.140, the generator must develop and follow a written waste analysis plan that describes the procedures it will carry out to comply with the treatment standards.  (Generators treating hazardous debris under the alternative treatment standards of Table F, however, are not subject to these waste analysis requirements.)  The plan must be kept on site in the generator’s records, and the following requirements must be met:

A)  The waste analysis plan must be based on a detailed chemical and physical analysis of a representative sample of the prohibited wastes being treated, and contain all information necessary to treat the wastes in accordance with the requirements of this Part, including the selected testing frequency;

B)  Such plan must be kept in the facility’s on-site files and made available to inspectors; and

C)  Wastes shipped off-site under this subsection (a)(5) must comply with the notification requirements of subsection (a)(3).

6)  If a generator determines that the waste or contaminated soil is restricted based solely on its knowledge of the waste, all supporting data used to make this determination must be retained on-site in the generator’s files.  If a generator determines that the waste is restricted based on testing this waste or an extract developed using Method 1311 (Toxicity Characteristic Leaching Procedure) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, all waste analysis data must be retained on-site in the generator’s files.

7)  If a generator determines that it is managing a prohibited waste that is excluded from the definition of hazardous or solid waste or that is exempt from Subtitle C regulation under 35 Ill. Adm. Code 721.102 through 721.106 subsequent to the point of generation (including deactivated characteristic hazardous wastes that are managed in wastewater treatment systems subject to the CWA, as specified at 35 Ill. Adm. Code 721.104(a)(2); that are CWA-equivalent; or that are managed in an underground injection well regulated under 35 Ill. Adm. Code 730), the generator must place a one-time notice stating such generation, subsequent exclusion from the definition of hazardous or solid waste or exemption from RCRA Subtitle C regulation, and the disposition of the waste in the generating facility’s on-site file.

8)  A generator must retain a copy of all notices, certifications, waste analysis data, and other documentation produced under this Section on-site for at least three years from the date that the waste that is the subject of such documentation was last sent to on-site or off-site treatment, storage, or disposal.  The three-year record retention period is automatically extended during the course of any unresolved enforcement action regarding the regulated activity or as requested in writing by the Agency.  The requirements of this subsection (a)(8) apply to solid wastes even when the hazardous characteristic is removed prior to disposal, or when the waste is excluded from the definition of hazardous or solid waste under 35 Ill. Adm. Code 721.102 through 721.106, or exempted from RCRA Subtitle C regulation, subsequent to the point of generation.

BOARD NOTE: Any Agency request for extended records retention under this subsection (a)(8) is subject to Board review under Section 40 of the Act.

9)  If a generator is managing a lab pack containing hazardous wastes and wishes to use the alternative treatment standard for lab packs found at Section 728.142(c), the generator must fulfill the following conditions:

A)  With the initial shipment of waste to a treatment facility, the generator must submit a notice that provides the information in column “Section 728.107(a)(9)” in the Generator Paperwork Requirements Table of Table I and the following certification.  The certification, which must be signed by an authorized representative and must be placed in the generator’s files, must say the following:

I certify under penalty of law that I personally have examined and am familiar with the waste and that the lab pack contains only wastes that have not been excluded under Appendix D to 35 Ill. Adm. Code 728 and that this lab pack will be sent to a combustion facility in compliance with the alternative treatment standards for lab packs at 35 Ill. Adm. Code 728.142(c).  I am aware that there are significant penalties for submitting a false certification, including the possibility of fine or imprisonment.

B)  No further notification is necessary until such time as the wastes in the lab pack change, or the receiving facility changes, in which case a new notice and certification must be sent and a copy placed in the generator’s file.

C)  If the lab pack contains characteristic hazardous wastes (D001-D043), underlying hazardous constituents (as defined in Section 728.102(i)) need not be determined.

D)  The generator must also comply with the requirements in subsections (a)(6) and (a)(7).

10)  An SQG with tolling agreements under 35 Ill. Adm. Code 722.120(e) must comply with the applicable notification and certification requirements of subsection (a) for the initial shipment of the waste subject to the agreement.  Such generators must retain on-site a copy of the notification and certification, together with the tolling agreement, for at least three years after termination or expiration of the agreement.  The three-year record retention period is automatically extended during the course of any unresolved enforcement action regarding the regulated activity or as requested in writing by the Agency.

BOARD NOTE: Any Agency request for extended records retention under this subsection (a)(10) is subject to Board review under Section 40 of the Act.

b)  The owner or operator of a treatment facility must test its wastes according to the frequency specified in its waste analysis plan, as required by 35 Ill. Adm. Code 724.113 (for permitted TSDs) or 725.113 (for interim status facilities).  Such testing must be performed as provided in subsections (b)(1), (b)(2), and (b)(3).

1)  For wastes or contaminated soil with treatment standards expressed in the waste extract (TCLP), the owner or operator of the treatment facility must test an extract of the treatment residues using Method 1311 (Toxicity Characteristic Leaching Procedure) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, to assure that the treatment residues extract meets the applicable treatment standards.

2)  For wastes or contaminated soil with treatment standards expressed as concentrations in the waste, the owner or operator of the treatment facility must test the treatment residues (not an extract of such residues) to assure that the treatment residues meet the applicable treatment standards.

3)  A one-time notice must be sent with the initial shipment of waste or contaminated soil to the land disposal facility.  A copy of the notice must be placed in the treatment facility’s file.

A)  No further notification is necessary until such time that the waste or receiving facility changes, in which case a new notice must be sent and a copy placed in the treatment facility’s file.

B)  The one-time notice must include the following requirements:

i)  USEPA hazardous waste number and manifest number of first shipment;

ii)  The waste is subject to the LDRs.  The constituents of concern for F001 through F005 and F039 waste and underlying hazardous constituents in characteristic wastes, unless the waste will be treated and monitored for all constituents.  If all constituents will be treated and monitored, there is no need to put them all on the LDR notice;

iii)  The notice must include the applicable wastewater/ nonwastewater category (see Section 728.102(d) and (f)) and subdivisions made within a USEPA hazardous waste numbers based on waste-specific criteria (such as D003 reactive cyanide);

iv)  Waste analysis data (when available);

v)  For contaminated soil subject to LDRs as provided in Section 728.149(a), the constituents subject to treatment as described in Section 728.149(d) and the following statement, “this contaminated soil (does/does not) contain listed hazardous waste and (does/does not) exhibit a characteristic of hazardous waste and (is subject to/complies with) the soil treatment standards as provided by Section 728.149(c)”; and

vi)  A certification is needed (see applicable Section for exact wording).

4)  The owner or operator of a treatment facility must submit a certification signed by an authorized representative with the initial shipment of waste or treatment residue of a restricted waste to the land disposal facility.  The certification must state as follows:

I certify under penalty of law that I have personally examined and am familiar with the treatment technology and operation of the treatment process used to support this certification.  Based on my inquiry of those individuals immediately responsible for obtaining this information, I believe that the treatment process has been operated and maintained properly so as to comply with the treatment standards specified in 35 Ill. Adm. Code 728.140 without impermissible dilution of the prohibited waste.  I am aware there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.

A certification is also necessary for contaminated soil and it must state as follows:

I certify under penalty of law that I have personally examined and am familiar with the treatment technology and operation of the treatment process used to support this certification and believe that it has been maintained and operated properly so as to comply with treatment standards specified in 35 Ill. Adm. Code 728.149 without impermissible dilution of the prohibited wastes.  I am aware there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.

A)  A copy of the certification must be placed in the treatment facility’s on-site files.  If the waste or treatment residue changes, or the receiving facility changes, a new certification must be sent to the receiving facility, and a copy placed in the treatment facility’s file.

B)  Debris excluded from the definition of hazardous waste under 35 Ill. Adm. Code 721.103(f) (i.e., debris treated by an extraction or destruction technology listed in Table F and debris that the Agency has determined does not contain hazardous waste) is subject to the notification and certification requirements of subsection (d) rather than the certification requirements of this subsection (b)(4).

C)  For wastes with organic constituents having treatment standards expressed as concentration levels, if compliance with the treatment standards is based in part or in whole on the analytical detection limit alternative specified in Section 728.140(d), the certification must be signed by an authorized representative and must state as follows:

I certify under penalty of law that I have personally examined and am familiar with the treatment technology and operation of the treatment process used to support this certification.  Based on my inquiry of those individuals immediately responsible for obtaining this information, I believe that the nonwastewater organic constituents have been treated by combustion units as specified in Table C to 35 Ill. Adm. Code 728.  I have been unable to detect the nonwastewater organic constituents, despite having used best good faith efforts to analyze for such constituents.  I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.

D)  For characteristic wastes that are subject to the treatment standards in Section 728.140 and Table T (other than those expressed as a required method of treatment) or Section 728.149 and that contain underlying hazardous constituents, as defined in Section 728.102(i); if these wastes are treated on-site to remove the hazardous characteristic; and that are then sent off-site for treatment of underlying hazardous constituents, the certification must state as follows:

I certify under penalty of law that the waste has been treated in accordance with the requirements of 35 Ill. Adm. Code 728.140 and Table T of Section 728.149 of that Part to remove the hazardous characteristic.  This decharacterized waste contains underlying hazardous constituents that require further treatment to meet treatment standards.  I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.

E)  For characteristic wastes that contain underlying hazardous constituents, as defined in Section 728.102(i), that are treated on-site to remove the hazardous characteristic and to treat underlying hazardous constituents to levels in Section 728.148 and Table U universal treatment standards, the certification must state as follows:

I certify under penalty of law that the waste has been treated in accordance with the requirements of 35 Ill. Adm. Code 728.140 and Table T of that Part to remove the hazardous characteristic and that underlying hazardous constituents, as defined in 35 Ill. Adm. Code 728.102(i), have been treated on-site to meet the universal treatment standards of 35 Ill. Adm. Code 728.148 and Table U of that Part.  I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.

5)  If the waste or treatment residue will be further managed at a different treatment, storage, or disposal facility, the treatment, storage, or disposal facility that sends the waste or treatment residue off-site must comply with the notice and certification requirements applicable to generators under this Section.

6)  If the wastes are recyclable materials used in a manner constituting disposal subject to the provisions of 35 Ill. Adm. Code 726.120(b), regarding treatment standards and prohibition levels, the owner or operator of a treatment facility (i.e., the recycler) must, for the initial shipment of waste, prepare a one-time certification described in subsection (b)(4) and a notice that includes the information listed in subsection (b)(3) (except the manifest number).  The certification and notification must be placed in the facility’s on-site files. If the waste or the receiving facility changes, a new certification and notification must be prepared and placed in the on-site files. In addition, the owner or operator of the recycling facility also must keep records of the name and location of each entity receiving the hazardous waste-derived product.

c)  Except if the owner or operator is disposing of any waste that is a recyclable material used in a manner constituting disposal under 35 Ill. Adm. Code 726.120(b), the owner or operator of any land disposal facility disposing any waste subject to restrictions under this Part must do the following:

1)  Maintain in its files copies of the notice and certifications specified in subsection (a) or (b).

2)  Test the waste or an extract of the waste or treatment residue developed using Method 1311 (Toxicity Characteristic Leaching Procedure in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846) to assure that the waste or treatment residue is in compliance with the applicable treatment standards set forth in Subpart D.  Such testing must be performed according to the frequency specified in the facility’s waste analysis plan as required by 35 Ill. Adm. Code 724.113 or 35 Ill. Adm. Code 725.113.

3)  If the owner or operator is disposing of any waste that is subject to the prohibitions under Section 728.133(f) but not subject to the prohibitions set forth in Section 728.132, the owner or operator must ensure that such waste is the subject of a certification according to the requirements of Section 728.108 prior to disposal in a landfill or surface impoundment unit, and that such disposal is in accordance with the requirements of Section 728.105(h)(2).  The same requirement applies to any waste that is subject to the prohibitions under Section 728.133(f) and also is subject to the statutory prohibitions in the codified prohibitions in Section 728.139 or Section 728.132.

4)  If the owner or operator is disposing of any waste that is a recyclable material used in a manner constituting disposal subject to the provisions of 35 Ill. Adm. Code 726.120(b), the owner or operator is not subject to subsections (c)(1) through (c)(3) with respect to such waste.

d)  A generator or treater that first claims that hazardous debris is excluded from the definition of hazardous waste under 35 Ill. Adm. Code 721.103(f) (i.e., debris treated by an extraction or destruction technology provided by Table F, and debris that has been delisted) is subject to the following notification and certification requirements:

1)  A one-time notification must be submitted to the Agency including the following information:

A)  The name and address of the RCRA Subtitle D (municipal solid waste landfill) facility receiving the treated debris;

B)  A description of the hazardous debris as initially generated, including the applicable USEPA hazardous waste numbers; and

C)  For debris excluded under 35 Ill. Adm. Code 721.103(f)(1), the technology from Table F used to treat the debris.

2)  The notification must be updated if the debris is shipped to a different facility and, for debris excluded under 35 Ill. Adm. Code 721.103(f)(1), if a different type of debris is treated or if a different technology is used to treat the debris.

3)  For debris excluded under 35 Ill. Adm. Code 721.103(f)(1), the owner or operator of the treatment facility must document and certify compliance with the treatment standards of Table F, as follows:

A)  Records must be kept of all inspections, evaluations, and analyses of treated debris that are made to determine compliance with the treatment standards;

B)  Records must be kept of any data or information the treater obtains during treatment of the debris that identifies key operating parameters of the treatment unit; and

C)  For each shipment of treated debris, a certification of compliance with the treatment standards must be signed by an authorized representative and placed in the facility’s files.  The certification must state as follows:

I certify under penalty of law that the debris has been treated in accordance with the requirements of 35 Ill. Adm. Code 728.145.  I am aware that there are significant penalties for making a false certification, including the possibility of fine and imprisonment.

e)  A generator or treater that first receives a determination from USEPA or the Agency that a given contaminated soil subject to LDRs, as provided in Section 728.149(a), no longer contains a listed hazardous waste and a generator or treater that first determines that a contaminated soil subject to LDRs, as provided in Section 728.149(a), no longer exhibits a characteristic of hazardous waste must do the following:

1)  Prepare a one-time only documentation of these determinations including all supporting information; and

2)  Maintain that information in the facility files and other records for a minimum of three years.

(Source: Amended at 44 Ill. Reg. 15495, effective September 3, 2020)

 


Section 728.108 Landfill and Surface Impoundment Disposal Restrictions (Repealed)

(Source: Repealed at 15 Ill. Reg. 9462, effective June 17, 1991)


Section 728.109 Special Rules for Characteristic Wastes

a)  The initial generator of a solid waste must determine each USEPA hazardous waste number applicable to the waste in order to determine the applicable treatment standards under Subpart D.  This determination may be made concurrently with the hazardous waste determination required in Section 722.111. For purposes of this Part, the waste must carry the USEPA hazardous waste number for any applicable listing under Subpart D of 35 Ill. Adm. Code 721.  In addition, the waste must carry one or more of the USEPA hazardous waste numbers under Subpart C of 35 Ill. Adm. Code 721 where the waste exhibits a characteristic, except in the case when the treatment standard for the listed waste operates in lieu of the treatment standard for the characteristic waste, as specified in subsection (b).  If the generator determines that its waste displays a characteristic of hazardous waste (and the waste is not D001 nonwastewaters treated by CMBST, RORGS, or POLYM of Table C), the generator must determine the underlying hazardous constituents (as defined at Section 728.102(i)) in the characteristic waste.

b)  Where a prohibited waste is both listed under Subpart D of 35 Ill. Adm. Code 721 and exhibits a characteristic of hazardous waste under Subpart C of 35 Ill. Adm. Code 721, the treatment standard for the USEPA hazardous waste number listed in Subpart D of 35 Ill. Adm. Code 721 will operate in lieu of the standard for the USEPA hazardous waste number under Subpart C of 35 Ill. Adm. Code 721, provided that the treatment standard for the listed waste includes a treatment standard for the constituent that causes the waste to exhibit the characteristic.  Otherwise, the waste must meet the treatment standards for all applicable listed and characteristic USEPA hazardous waste numbers.

c)  In addition to any applicable standards determined from the initial point of generation, no prohibited waste that exhibits a characteristic under Subpart C of 35 Ill. Adm. Code 721 must be land disposed, unless the waste complies with the treatment standards under Subpart D.

d)  A waste that exhibits a characteristic of hazardous waste under Subpart C of 35 Ill. Adm. Code 721 is also subject to Section 728.107 requirements, except that once the waste is no longer hazardous, a one-time notification and certification must be placed in the generator’s or treater’s on-site files.  The notification and certification that is placed in the generator’s or treater’s files must be updated if the process or operation generating the waste changes or if the RCRA Subtitle D (municipal solid waste landfill) facility receiving the waste changes.

1)  The notification must include the following information:

A)  The name and address of the RCRA Subtitle D (municipal solid waste landfill) facility receiving the waste shipment; and

B)  A description of the waste as initially generated, including the applicable USEPA hazardous waste numbers, the treatability groups, and the underlying hazardous constituents (as defined in Section 728.102(i)), unless the waste will be treated and monitored for all underlying hazardous constituents.  If all underlying hazardous constituents will be treated and monitored, there is no requirement to list any of the underlying hazardous constituents on the notice.

2)  The certification must be signed by an authorized representative and must state the language found in Section 728.107(b)(4). If treatment removes the characteristic but does not meet standards applicable to underlying hazardous constituents, then the certification found in Section 728.107(b)(4)(D) applies.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


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


Section 728.110 First Third (Repealed)

 
(Source: Repealed at 22 Ill. Reg. 783, effective December 16, 1997)


Section 728.111 Second Third (Repealed)

 
(Source: Repealed at 22 Ill. Reg. 783, effective December 16, 1997)


Section 728.112 Third Third (Repealed)

 
(Source: Repealed at 22 Ill. Reg. 783, effective December 16, 1997)


Section 728.113 Newly Listed Wastes

In corresponding 40 CFR 268.13, USEPA stated that it would make a land disposal prohibition determination for any hazardous waste identified or listed after November 8, 1984 within six months after the date of identification or listing. This statement maintains structural consistency with the corresponding federal regulations.

(Source: Amended at 27 Ill. Reg. 13045, effective July 17, 2003)


Section 728.114 Surface Impoundment Exemptions

a)  This Section defines additional circumstances under which an otherwise prohibited waste may continue to be placed in a surface impoundment.

b)  Wastes that are newly identified or listed by USEPA persuant to Section 3001 of RCRA (42 USC 6921) after November 8, 1984 and which are stored in a surface impoundment that is newly subject to subtitle C of RCRA (42 USC 6921 et seq.) as a result of the additional identification or listing may continue to be stored in the surface impoundment for 48 months after the promulgation of the additional listing or characteristic, notwithstanding the fact that the waste is otherwise prohibited from land disposal, provided that the surface impoundment is in compliance with the requirements of Subpart F of 35 Ill. Adm. Code 725 within 12 months after promulgation of the new listing or characteristic.

c)  Wastes that are newly identified or listed by USEPA under Section 3001 of RCRA (42 USC 6921) after November 8, 1984 and which are treated in a surface impoundment that is newly subject to Subtitle C of RCRA (42 USC 6921 et seq.) as a result of the additional identification or listing may continue to be treated in that surface impoundment, notwithstanding the fact that the waste is otherwise prohibited from land disposal, provided that the surface impoundment is in compliance with the requirements of Subpart F of 35 Ill. Adm. Code 725 within 12 months after the promulgation of the new listing or characteristic. In addition, if the surface impoundment continues to treat hazardous waste after 48 months from promulgation of the additional listing or characteristic, it must then be in compliance with Section 728.104.

(Source: Amended at 30 Ill. Reg. 3800, effective February 23, 2006)

SUBPART C:  PROHIBITION ON LAND DISPOSAL


Section 728.120 Waste-Specific Prohibitions: Dyes and Pigments Production Wastes

a)  The waste specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste number K181, soil and debris contaminated with this waste, radioactive wastes mixed with this waste, and soil and debris contaminated with radioactive wastes mixed with this waste are prohibited from land disposal.

b)  The requirements of subsection (a) do not apply if any of the following conditions are fulfilled:

1)  The wastes meet the applicable treatment standards specified in Subpart D;

2)  A no-migration exemption has been granted from a prohibition pursuant to a petition under Section 728.106, in which case the requirements of subsection (a) do not apply with respect to those wastes and units covered by the petition;

3)  The wastes meet the applicable treatment standards established pursuant to a petition granted under Section 728.144;

4)  Hazardous debris has met the treatment standards in Section 728.140 or the alternative treatment standards in Section 728.145; or

5)  USEPA has granted an extension to the effective date of a prohibition pursuant to 40 CFR 268.5, in which case the requirements of subsection (a) do not apply with respect to these wastes covered by the extension.

c)  To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards specified in Section 728.140, the initial generator must test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract of the waste, or the generator may use knowledge of the waste. If the waste contains regulated constituents in excess of the applicable levels set forth in Subpart D, the waste is prohibited from land disposal, and all requirements of this Part apply, except as otherwise specified.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.130 Waste-Specific Prohibitions: Wood Preserving Wastes

a)  The following wastes are prohibited from land disposal:  the wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous waste numbers F032, F034, and F035.

b)  The following wastes are prohibited from land disposal:  soil and debris contaminated with the wastes specified in 35 Ill. Adm. Code 721 as F032, F034, F035; and radioactive wastes mixed with USEPA hazardous waste numbers F032, F034, and F035.

c)  This subsection (c) corresponds with 40 CFR 268.30(c), which expired by its own terms on May 12, 1999. This statement maintains structural consistency with the corresponding federal regulations.

d)  The requirements of subsections (a) and (b) do not apply if any of the following conditions is fulfilled:

1)  The wastes meet the applicable treatment standards specified in Subpart D;

2)  A person has been granted an exemption from a prohibition pursuant to a petition under Section 728.106, with respect to those wastes and units covered by the petition;

3)  The wastes meet the applicable alternate treatment standards established pursuant to a petition granted under Section 728.144; or

4)  A person has been granted an extension to the effective date of a prohibition by USEPA pursuant to federal 40 CFR 268.5 (see Section 728.105), with respect to those wastes covered by the extension.

e)  To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards specified in Section 728.140 and Table T, the initial generator must test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or the waste, or the generator may use knowledge of the waste.  If the waste contains constituents in excess of the applicable universal treatment standard levels of Section 728.148 and Table U, the waste is prohibited from land disposal and all requirements of Part 728 are applicable, except as otherwise specified.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.131 Waste-Specific Prohibitions: Dioxin-Containing Wastes

a)  The dioxin-containing wastes specified in 35 Ill. Adm. Code 721.131 as USEPA Hazardous Waste Numbers F020, F021, F022, F023, F026, F027, and F028 are prohibited from land disposal, unless the following condition applies: the dioxin-containing waste is contaminated soil and debris resulting from a CERCLA response or a RCRA corrective action.

b)  USEPA Hazardous Waste Numbers F020, F021, F022, F023, F026, F027, and F028, and dioxin-containing waste that is contaminated soil and debris resulting from a CERCLA response or a RCRA corrective action listed in subsection (a) are prohibited from land disposal.

c)  This subsection (c) corresponds with 40 CFR 268.31(c), which expired by its own terms on November 8, 1990. This statement maintains structural consistency with the corresponding federal regulations.

d)  The requirements of subsections (a) and (b) do not apply if any of the following conditions is fulfilled:

1)  The wastes meet the standards of Subpart D; or

2)  A person has been granted an exemption from a prohibition pursuant to a petition under Section 728.106, with respect to those wastes and units covered by the petition; or

3)  A person has been granted an extension from the effective date of a prohibition pursuant to Section 728.105, with respect to those wastes and units covered by the extension.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.132 Waste-Specific Prohibitions: Soils Exhibiting the Toxicity Characteristic for Metals and Containing PCBs

a)  The following wastes are prohibited from land disposal: any volumes of soil exhibiting the toxicity characteristic solely because of the presence of metals (USEPA hazardous waste numbers D004 through D011) and containing PCBs.

b)  The requirements of subsection (a) do not apply if any of the following conditions is fulfilled:

1)  Low-Halogenated Organics Waste Meeting the Treatment Standards of Subpart D

A)  The wastes contain halogenated organic compounds in total concentration less than 1,000 mg/kg; and

B)  The wastes meet the treatment standards specified in Subpart D for USEPA hazardous waste numbers D004 through D011, as applicable; or

2)  Low-Halogenated Organics Waste Meeting Alternative Treatment Standards for Contaminated Soil

A)  The wastes contain halogenated organic compounds in total concentration less than 1,000 mg/kg; and

B)  The wastes meet the alternative treatment standards specified in Section 728.149 for contaminated soil; or

3)  A person has been granted an exemption from a prohibition pursuant to a petition under Section 728.106, with respect to those wastes and units covered by the petition; or

4)  The wastes meet applicable alternative treatment standards established pursuant to a petition granted under Section 728.144.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.133 Waste-Specific Prohibitions: Chlorinated Aliphatic Wastes

a)  The wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous wastes numbers K174 and K175, 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) do not apply if any of the following conditions is fulfilled:

1)  The wastes meet the applicable treatment standards specified in Subpart D;

2)  A person has been granted an exemption from a prohibition pursuant to a petition under Section 728.106, with respect to those wastes and units covered by the petition;

3)  The wastes meet the applicable treatment standards established pursuant to a petition granted under Section 728.144;

4)  Hazardous debris has met the treatment standards in Section 728.140 or the alternative treatment standards in Section 728.145; or

5)  A person has been granted an extension to the effective date of a prohibition pursuant to Section 728.105, with respect to those wastes covered by the extension.

c)  To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards specified in Section 728.140, the initial generator must test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or the waste, or the generator may use knowledge of the waste. If the waste contains regulated constituents in excess of the applicable levels of Subpart D, the waste is prohibited from land disposal, and all requirements of this Part 728 are applicable, except as otherwise specified.

d)  Disposal of USEPA hazardous waste number K175 wastes that have complied with all applicable Section 728.140 treatment standards must also be macroencapsulated in accordance with Table F, unless the waste is placed in one of the following:

1)  A RCRA Subtitle C monofill containing only K175 wastes that meet all applicable Section 728.140 treatment standards; or

2)  A dedicated RCRA Subtitle C landfill cell in which all other wastes being co-disposed are at pH £ 6.0.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


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)  The following wastes are prohibited from land disposal:  newly identified characteristic wastes from elemental phosphorus processing; radioactive wastes mixed with USEPA hazardous waste numbers D004 through D011 wastes that are newly identified (i.e., wastes, soil, or debris identified as hazardous by the Toxic Characteristic Leaching Procedure but not the Extraction Procedure); or mixed with newly identified characteristic mineral processing wastes, soil, or debris.

d)  This subsection (d) corresponds with 40 CFR 269.34(d), which expired by its own terms on May 26, 2000. This statement maintains structural consistency with the corresponding federal regulations.

e)  The requirements of subsections (a) and (b) do not apply if any of the following applies to the waste:

1)  The wastes meet the applicable treatment standards specified in Subpart D;

2)  The Board has granted an exemption from a prohibition pursuant to a petition under Section 728.106, with respect to those wastes and units covered by the petition;

3)  The wastes meet the applicable alternate treatment standards established pursuant to a petition granted under Section 728.144; or

4)  USEPA has granted an extension to the effective date of a prohibition pursuant to federal 40 CFR 268.5, with respect to those wastes covered by the extension.

f)  To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards specified in Section 728.140 and Table T, 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, the waste is prohibited from land disposal, and all requirements of this Part are applicable, except as otherwise specified.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.135 Waste-Specific Prohibitions: Petroleum Refining Wastes

a)  The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous wastes numbers K169, K170, K171, and K172; soils and debris contaminated with these wastes; radioactive wastes mixed with these hazardous wastes; and soils and debris contaminated with these radioactive mixed wastes are prohibited from land disposal.

b)  The requirements of subsection (a) do not apply if any of the following applies to the waste:

1)  The wastes meet the applicable treatment standards specified in Subpart D;

2)  The Board has granted an adjusted standard that exempts waste from a prohibition pursuant to Section 728.106, with respect to those wastes and units covered by the adjusted standard;

3)  The wastes meet an adjusted standard from an applicable treatment standard granted under Section 728.144;

4)  The waste is hazardous debris that has met the treatment standards set forth in Section 728.140 and Table T or the alternative treatment standards in Section 728.145; or

5)  USEPA has granted an extension to the effective date of a prohibition pursuant to federal 40 CFR 268.5, with respect to these wastes covered by the extension.

c)  To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards specified in Section 728.140, the initial generator must test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or the waste, or the generator may use knowledge of the waste. If the waste contains constituents in excess of the applicable universal treatment standard levels of Section 728.148 and Table U, the waste is prohibited from land disposal, and all requirements of this Part are applicable, except as otherwise specified.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.136 Waste-Specific Prohibitions: Inorganic Chemical Wastes

a)  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) do not apply if any of the following applies to the waste:

1)  The wastes meet the applicable treatment standards specified in Subpart D;

2)  A person has been granted an exemption from a prohibition pursuant to a petition under Section 728.106, with respect to those wastes and units covered by the petition;

3)  The wastes meet the applicable treatment standards established pursuant to a petition granted under Section 728.144;

4)  Hazardous debris has met the treatment standards in Section 728.140 and Table T or the alternative treatment standards in Section 728.145; or

5)  A person has 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 Section 728.140 and 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 levels of Subpart D, the waste is prohibited from land disposal, and all requirements of this part are applicable, except as otherwise specified.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.137 Waste-Specific Prohibitions: Ignitable and Corrosive Characteristic Wastes Whose Treatment Standards Were Vacated

a)  The wastes specified in 35 Ill. Adm. Code 721.121 as D001 (and is not in the High TOC Ignitable Liquids Subcategory), and specified in 35 Ill. Adm. Code 721.122 as D002, that are managed in systems other than those whose discharge is regulated under the Clean Water Act (CWA), or that inject in Class I deep wells regulated under the Safe Drinking Water Act (SDWA), or that are zero dischargers that engage in CWA-equivalent treatment before ultimate land disposal, are prohibited from land disposal. CWA-equivalent treatment means biological treatment for organics, alkaline chlorination or ferrous sulfate precipitation for cyanide, precipitation/sedimentation for metals, reduction of hexavalent chromium, or other treatment technology that can be demonstrated to perform equally or greater than these technologies.

b)  The wastes specified in 35 Ill. Adm. Code 721.121 as D001 (and is not in the High TOC Ignitable Liquids Subcategory), and specified in 35 Ill. Adm. Code 721.122 as D002, that are managed in systems defined in 35 Ill. Adm. Code 704 and 730 as Class V injection wells, that do not engage in CWA-equivalent treatment before injection, are prohibited from land disposal.

(Source: Amended at 27 Ill. Reg. 13045, effective July 17, 2003)


Section 728.138 Waste-Specific Prohibitions: Newly-Identified Organic Toxicity Characteristic Wastes and Newly-Listed Coke By-Product and Chlorotoluene Production Wastes

a)  The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste numbers K141, K142, K143, K144, K145, K147, K148, K149, K150, and K151 are prohibited from land disposal. In addition, debris contaminated with USEPA hazardous waste numbers F037, F038, K107 through K112, K117, K118, K123 through K126, K131, K132, K136, U328, U353, U359 and soil and debris contaminated with D012 through D043, K141 through K145, and K147 through K151 are prohibited from land disposal. The following wastes that are specified in the table at 35 Ill. Adm. Code 721.124(b) as USEPA hazardous waste numbers D012, D013, D014, D015, D016, D017, 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 that are not radioactive, that are managed in systems other than those whose discharge is regulated under the federal Clean Water Act (CWA; 33 U.S.C. 1251 et seq.), that are zero dischargers that do not engage in CWA-equivalent treatment before ultimate land disposal, or that are injected in Class I deep wells regulated under the Safe Drinking Water Act (SDWA) are prohibited from land disposal. “CWA-equivalent treatment”, as used in this Section, means biological treatment for organics, alkaline chlorination or ferrous sulfate precipitation for cyanide, precipitation and sedimentation for metals, reduction for hexavalent chromium, or another treatment technology that can be demonstrated to perform equally to or better than these technologies.

b)  Radioactive wastes that are mixed with any of USEPA hazardous waste numbers D018 through D043 waste that are managed in systems other than those whose discharge is regulated under the Clean Water Act (CWA), in systems that inject in Class I deep wells regulated under the Safe Drinking Water Act (SDWA), or in systems that are zero dischargers that engage in CWA-equivalent treatment, as defined in subsection (a), before ultimate land disposal are prohibited from land disposal. Radioactive wastes mixed with any of USEPA hazardous waste numbers K141 through K145 and K147 through K151 are also prohibited from land disposal. In addition, soil and debris contaminated with these radioactive mixed wastes are prohibited from land disposal.

c)  This subsection (c) corresponds with 40 CFR 268.38(c), which expired by its own terms on September 19, 1996. This statement maintains structural consistency with the corresponding federal regulations.

d)  The requirements of subsections (a), (b), and (c) do not apply if any of the following applies to the waste:

1)  The wastes meet the applicable treatment standards specified in Subpart D;

2)  A person has been granted an exemption from a prohibition pursuant to a petition under Section 728.106, with respect to those wastes and units covered by the petition;

3)  The wastes meet the applicable alternate treatment standards established pursuant to a petition granted under Section 728.144;

4)  A person has 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.

e)  To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards specified in Section 728.140 and 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 constituents in excess of the applicable levels of Subpart D, the waste is prohibited from land disposal and all requirements of this Part are applicable, except as otherwise specified.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.139 Waste-Specific Prohibitions: Spent Aluminum Potliners and Carbamate Wastes

a)  The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste numbers K156-K159 and K161; and in 35 Ill. Adm. Code 721.133 as USEPA hazardous waste numbers P127, P128, P185, P188 through P192, P194, P196 through P199, P201 through P205, U271, U278 through U280, U364, U367, U372, U373, U387, U389, U394, U395, U404, and U409 through U411 are prohibited from land disposal. In addition, soil and debris contaminated with these wastes are prohibited from land disposal.

b)  The wastes identified in 35 Ill. Adm. Code 721.123 as USEPA hazardous waste number D003 are prohibited from land disposal, other than those that are managed in a system whose discharge is regulated under 35 Ill. Adm. Code:Subtitle C, one that injects hazardous waste in Class I waste injection well regulated under 35 Ill. Adm. Code 702, 704, and 730, or one that is a zero discharger that engages in federal Clean Water Act (CWA)-equivalent treatment before ultimate land disposal. This prohibition does not apply to unexploded ordnance and other explosive devices that have been the subject of an emergency response. (Such D003 wastes are prohibited unless they meet the treatment standard of DEACT before land disposal (see Section 728.140)).

c)  The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste number K088 are prohibited from land disposal. In addition, soil and debris contaminated with these wastes are prohibited from land disposal.

d)  Radioactive wastes mixed with waste designated by any of USEPA hazardous waste numbers K088, K156 through K159, K161, P127, P128, P185, P188 through P192, P194, P196 through P199, P201 through P205, U271, U278 through U280, U364, U367, U372, U373, U387, U389, U394, U395, U404, and U409 through U411 are prohibited from land disposal. In addition, soil and debris contaminated with these radioactive mixed wastes are prohibited from land disposal.

e)  This subsection corresponds with 40 CFR 268.39(e), which expired by its own terms after April 8, 1998. This statement maintains structural consistency with the corresponding federal regulations.

f)  The requirements of subsections (a), (b), (c), and (d) do not apply if any of the following applies to the waste:

1)  The wastes meet the applicable treatment standards specified in Subpart D;

2)  The person conducting the disposal has been granted an exemption from a prohibition under a petition pursuant to Section 728.106, with respect to those wastes and units covered by the petition;

3)  The wastes meet the applicable alternative treatment standards established pursuant to a petition granted under Section 728.144; or

4)  The person conducting the disposal has been granted an extension to the effective date of a prohibition pursuant to Section 728.105, with respect to those wastes covered by the extension.

g)  To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards set forth in Section 728.140, the initial generator must test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or in the waste, or the generator may use knowledge of the waste. If a waste contains constituents in excess of the applicable levels of Subpart D, the waste is prohibited from land disposal and all requirements of this Part are applicable to the waste, except as otherwise specified.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


SUBPART D:  TREATMENT STANDARDS


Section 728.140 Applicability of Treatment Standards

a)  A prohibited waste identified in Table T, “Treatment Standards for Hazardous Wastes”, may be land disposed only if it meets the requirements found in that Table.  For each waste, Table T identifies one of three types of treatment standard requirements:

1)  All hazardous constituents in the waste or in the treatment residue must be at or below the values found in Table T for that waste (total waste standards);

2)  The hazardous constituents in the extract of the waste or in the extract of the treatment residue must be at or below the values found in Table T (waste extract standards); or

3)  The waste must be treated using the technology specified in Table T (technology standard), which is described in detail in Table C, “Technology Codes and Description of Technology-Based Standards”.

b)  For wastewaters, compliance with concentration level standards is based on maximums for any one day, except for D004 through D011 wastes for which the previously promulgated treatment standards based on grab samples remain in effect.  For all nonwastewaters, compliance with concentration level standards is based on grab sampling.  For wastes covered by the waste extract standards, the test Method 1311 (Toxicity Characteristic Leaching Procedure) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a), must be used to measure compliance.  An exception is made for D004 and D008, for which either of two test methods may be used:  Method 1311 or Method 1310B (Extraction Procedure Toxicity Test) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846. For wastes covered by a technology standard, the wastes may be land disposed after being treated using that specified technology or an equivalent treatment technology approved by the Agency pursuant to Section 728.142(b).

c)  When wastes with differing treatment standards for a constituent of concern are combined for purposes of treatment, the treatment residue must meet the lowest treatment standard for the constituent of concern.

d)  Notwithstanding the prohibitions specified in subsection (a), treatment and disposal facilities may demonstrate (and certify pursuant to Section 728.107(b)(5)) compliance with the treatment standards for organic constituents specified by a footnote in Table T, provided the following conditions are satisfied:

1)  The treatment standards for the organic constituents were established based on incineration in units operated in accordance with the technical requirements of Subpart O of 35 Ill. Adm. Code 724, or based on combustion in fuel substitution units operating in accordance with applicable technical requirements;

2)  The treatment or disposal facility has used the methods referenced in subsection (d)(1) to treat the organic constituents; and

3)  The treatment or disposal facility may demonstrate compliance with organic constituents if good-faith analytical efforts achieve detection limits for the regulated organic constituents that do not exceed the treatment standards specified in this Section and Table T by an order of magnitude.

e)  For a characteristic waste (USEPA hazardous waste number D001 through D043) that is subject to treatment standards set forth in Table T, “Treatment Standards for Hazardous Wastes”, and the waste is not managed in a wastewater treatment system that is either regulated under the Clean Water Act (CWA) or one that is CWA-equivalent or the waste is injected into a Class I non-hazardous deep injection well, all underlying hazardous constituents (as defined in Section 728.102) must meet the universal treatment standards, set forth in Table U prior to land disposal, as defined in Section 728.102.

f)  The treatment standards for USEPA hazardous waste numbers F001 through F005 nonwastewater constituents carbon disulfide, cyclohexanone, or methanol apply to wastes that contain only one, two, or three of these constituents.  Compliance is measured for these constituents in the waste extract from test Method 1311 (Toxicity Characteristic Leaching Procedure) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).  If the waste contains any of these three constituents along with any of the other 25 constituents found in USEPA hazardous waste numbers F001 through F005, then compliance with treatment standards for carbon disulfide, cyclohexanone, or methanol are not required.

g)  This subsection (g) corresponds with 40 CFR 268.40(g), which expired by its own terms on March 4, 1999.  This statement maintains structural consistency with the corresponding federal rules.

h)  Prohibited USEPA hazardous waste numbers D004 through D011, mixed radioactive wastes, and mixed radioactive listed wastes containing metal constituents that were previously treated by stabilization to the treatment standards in effect at that time and then put into storage do not have to be re-treated to meet treatment standards in this Section prior to land disposal.

i)  This subsection (i) corresponds with 40 CFR 268.40(i), which USEPA has removed and marked “reserved”. This statement maintains structural consistency with the corresponding federal regulations.

j)  The treatment standards for the wastes specified in 35 Ill. Adm. Code 721.133 as USEPA hazardous waste numbers P185, P191, P192, P197, U364, U394, and U395 may be satisfied by either meeting the constituent concentrations presented in Table T, “Treatment Standards for Hazardous Wastes”, or by treating the waste by the following technologies: combustion, as defined by the technology code CMBST at Table C, for nonwastewaters; biodegradation, as defined by the technology code BIODG; carbon adsorption, as defined by the technology code CARBN; chemical oxidation, as defined by the technology code CHOXD; or combustion, as defined as technology code CMBST at Table C, for wastewaters.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.141 Treatment Standards Expressed as Concentrations in Waste Extract

For the requirements previously found in this Section and for treatment standards in Table A, “Table CCWE-Constituent Concentrations in Waste Extracts”, refer to Section 728.140 and Table T, “Treatment Standards for Hazardous Wastes”.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.142 Treatment Standards Expressed as Specified Technologies

a)  The following wastes listed in Table T, “Treatment Standards for Hazardous Wastes”, for which standards are expressed as a treatment method rather than as a concentration level, must be treated using the technology or technologies specified in Table C.

1)  Liquid hazardous wastes containing PCBs at concentrations greater than or equal to 50 ppm but less than 500 ppm must be incinerated in accordance with the technical requirements of 40 CFR 761.70 (Incineration), incorporated by reference in 35 Ill. Adm. Code 720.111(b), or burned in high efficiency boilers in accordance with the technical requirements of 40 CFR 761.60 (Disposal Requirements), incorporated by reference in 35 Ill. Adm. Code 720.111(b).  Liquid hazardous wastes containing PCBs at concentrations greater than or equal to 500 ppm must be incinerated in accordance with the technical requirements of 40 CFR 761.70.  Thermal treatment in accordance with this Section must be in compliance with applicable regulations in 35 Ill. Adm. Code 724, 725, and 726.

2)  Nonliquid hazardous wastes containing halogenated organic compounds (HOCs) in total concentrations greater than or equal to 1,000 mg/kg and liquid HOC-containing wastes that are prohibited pursuant to Section 728.132(e)(1) must be incinerated in accordance with the requirements of Subpart O of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725.  These treatment standards do not apply where the waste is subject to a treatment standard codified in Subpart C for a specific HOC (such as a hazardous waste chlorinated solvent for which a treatment standard is established pursuant to Section 728.141(a)).

3)  A mixture consisting of wastewater, the discharge of which is subject to regulation pursuant to 35 Ill. Adm. Code 309 or 310, and de minimis losses of materials from manufacturing operations in which these materials are used as raw materials or are produced as products in the manufacturing process that meet the criteria of the D001 ignitable liquids containing greater than 10 percent total organic constituents (TOC) subcategory are subject to the DEACT treatment standard described in Table C.  For purposes of this subsection (a)(3), “de minimis losses” include the following:

A)  Those from normal material handling operations (e.g., spills from the unloading or transfer of materials from bins or other containers, or leaks from pipes, valves, or other devices used to transfer materials);

B)  Minor leaks from process equipment, storage tanks, or containers;

C)  Leaks from well-maintained pump packings and seals;

D)  Sample purgings; and

E)  Relief device discharges.

b)  Any person may submit an application to the Agency demonstrating that an alternative treatment method can achieve a level of performance equivalent to that achievable by methods specified in subsections (a), (c), and (d) for wastes or specified in Table F for hazardous debris.  The applicant must submit information demonstrating that the applicant’s treatment method is in compliance with federal and state requirements, including this Part; 35 Ill. Adm. Code 709, 724, 725, 726, and 729; and Sections 22.6 and 39(h) of the Environmental Protection Act and that the treatment method adequately protects human health and the environment.  On the basis of such information and any other available information, the Agency must approve the use of the alternative treatment method if the Agency finds that the alternative treatment method provides a measure of performance equivalent to that achieved by methods specified in subsections (a), (c), and (d) and in Table F, for hazardous debris.  Any approval must be stated in writing and may contain such provisions and conditions as the Agency determines to be appropriate.  The person to whom such approval is issued must comply with all limitations contained in such determination.

c)  As an alternative to the otherwise applicable treatment standards of Subpart D, lab packs are eligible for land disposal provided the following requirements are met:

1)  The lab packs comply with the applicable provisions of 35 Ill. Adm. Code 724.416 and 725.416;

BOARD NOTE:  35 Ill. Adm. Code 729.301 and 729.312 include additional restrictions on the use of lab packs.

2)  The lab pack does not contain any of the wastes listed in Appendix D;

3)  The lab packs are incinerated in accordance with the requirements of Subpart O of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725; and

4)  Any incinerator residues from lab packs containing D004, D005, D006, D007, D008, D010, and D011 are treated in compliance with the applicable treatment standards specified for such wastes in Subpart D.

d)  Radioactive hazardous mixed wastes are subject to the treatment standards in Section 728.140 and Table T.  Where treatment standards are specified for radioactive mixed wastes in Table T, “Table of Treatment Standards”, those treatment standards will govern.  Where there is no specific treatment standard for radioactive mixed waste, the treatment standard for the hazardous waste (as designated by USEPA hazardous waste number) applies.  Hazardous debris containing radioactive waste is subject to the treatment standards specified in Section 728.145.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.143 Treatment Standards Expressed as Waste Concentrations

For the requirements previously found in this Section and for treatment standards in Table A, “CCW-Constituent Concentrations in Wastes”, refer to Section 728.140 and Table T, “Treatment Standards for Hazardous Wastes”.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.144 USEPA Variance from a Treatment Standard

a)  Based on a petition filed by a generator or treater of hazardous waste, USEPA has stated that it may approve a variance from an applicable treatment standard if the petitioner can demonstrate that either of the following applies to treatment of the waste:

1)  It is not physically possible to treat the waste to the level specified in the treatment standard, or by the method specified as the treatment standard.  To show that this is the case, the petitioner must demonstrate that because the physical or chemical properties of the waste differ significantly from waste analyzed in developing the treatment standard, the waste cannot be treated to the specified level or by the specified method; or

2)  It is inappropriate to require the waste to be treated to the level specified in the treatment standard or by the method specified as the treatment standard, even though such treatment is technically possible.  To show that this is the case, the petitioner must demonstrate that either of the following applies to treatment of the waste:

A)  Treatment to the specified level or by the specified method is technically inappropriate (for example, resulting in combustion of large amounts of mildly contaminated environmental media); or

B)  For remediation waste only, treatment to the specified level or by the specified method is environmentally inappropriate because it would likely discourage aggressive remediation.

BOARD NOTE:  A variance from a treatment standard is available only from USEPA. USEPA has reserved to itself the authority to grant a variance from a treatment standard.

b)  Each petition must be submitted in accordance with the procedures in 40 CFR 260.20.

c)  Each petition must include the following statement signed by the petitioner or an authorized representative:

I certify under penalty of law that I have personally examined and am familiar with the information submitted in this petition and all attached documents, and that, based on my inquiry of those individuals immediately responsible for obtaining the information, I believe that the submitted information is true, accurate and complete.  I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment.

d)  After receiving a petition for an adjusted treatment standard, USEPA has stated that it may request any additional information or samples that are necessary to evaluate the petition. Additional copies of the complete petition may be requested as needed to send to affected states and Regional Offices.

e)  USEPA has stated that it will give public notice in the Federal Register of the intent to approve or deny a petition and provide an opportunity for public comment.  USEPA has stated that the final decision on a variance from a treatment standard will be published in the Federal Register.

f)  A generator, treatment facility or disposal facility that is managing a waste covered by an adjusted treatment standard must comply with the waste analysis requirements for restricted wastes found under Section 728.107.

g)  During the petition review process, the applicant is required to comply with all restrictions on land disposal under this Part once the effective date for the waste has been reached.

h)  Based on a petition filed by a generator or treater of hazardous waste, USEPA has stated that it may approve a site-specific variance from an applicable treatment standard if the petitioner can demonstrate that either of the following applies to treatment of the waste:

1)  It is not physically possible to treat the waste to the level specified in the treatment standard, or by the method specified as the treatment standard.  To show that this is the case, the petitioner must demonstrate that because the physical or chemical properties of the waste differ significantly from waste analyzed in developing the treatment standard, the waste cannot be treated to the specified level or by the specified method; or

2)  It is inappropriate to require the waste to be treated to the level specified in the treatment standard or by the method specified as the treatment standard, even though such treatment is technically possible.  To show that this is the case, the petitioner must demonstrate that either of the following applies to treatment of the waste:

A)  Treatment to the specified level or by the specified method is technically inappropriate (for example, resulting in combustion of large amounts of mildly contaminated environmental media where the treatment standard is not based on combustion of such media); or

B)  For remediation waste only, treatment to the specified level or by the specified method is environmentally inappropriate because it would likely discourage aggressive remediation.

3)  For contaminated soil only, treatment to the level or by the method specified in the soil treatment standards would result in concentrations of hazardous constituents that are below (i.e., lower than) the concentrations necessary to minimize short- and long-term threats to human health and the environment.  USEPA has stated that a treatment variance granted under 40 CFR 268.44(h)(3) will include the following features:

A)  At a minimum, USEPA has stated that a treatment variance approved under 40 CFR 268.44(h)(3) will impose an alternative land disposal restriction treatment standard that will achieve the following, using a reasonable maximum exposure scenario:

i)  For carcinogens, it will achieve constituent concentrations that result in the total excess risk to an individual exposed over a lifetime, generally falling within a range from 104 to 106; and

ii)  For constituents with non-carcinogenic effects, it will achieve constituent concentrations that an individual could be exposed to on a daily basis without appreciable risk of deleterious effect during a lifetime.

B)  USEPA has stated that a treatment variance approved under 40 CFR 268.44(h)(3) will not consider post-land-disposal controls.

4)  For contaminated soil only, treatment to the level or by the method specified in the soil treatment standards would result in concentrations of hazardous constituents that are below (i.e., lower than) natural background concentrations at the site where the contaminated soil will be land disposed.

5)  USEPA has stated that public notice and a reasonable opportunity for public comment must be provided before granting or denying a petition.

i)  Each petition for a site-specific variance from a treatment standard must include the information in 40 CFR 260.20(b)(1) through (b)(4).

j)  After receiving an application for a site-specific variance from a treatment standard, USEPA may request any additional information or samples that USEPA determines are necessary to evaluate the petition.

k)  A generator, treatment facility, or disposal facility that is managing a waste covered by a site-specific variance from a treatment standard must comply with the waste analysis requirements for restricted wastes in Section 728.107.

l)  During the petition review process, the petitioner for a site-specific variance must comply with all restrictions on land disposal under this Part once the effective date for the waste has been reached.

m)  For any variance from a treatment standard, the petitioner must also demonstrate that compliance with the requested variance is sufficient to minimize threats to human health and the environment posed by land disposal of the waste.  In evaluating this demonstration, USEPA has stated that it will take into account whether the treatment variance should be granted if the subject waste is to be used in a manner constituting disposal pursuant to 40 CFR 266.20 through 266.23.

n)  This subsection (n) corresponds with 40 CFR 268.44(n), marked “reserved” by USEPA. This statement maintains structural consistency with corresponding federal regulations.

o)  The facilities listed in Table H are excluded from the treatment standards under Section 728.143(a) and Table B, and are subject to the constituent concentrations listed in Table H.

p)  After USEPA grants a treatability exception by regulatory action pursuant to 40 CFR 268.44 and a person demonstrates that the treatability exception needs to be adopted as part of the Illinois RCRA program because the waste is generated or managed in Illinois, the Board will adopt the treatability exception by identical in substance rulemaking pursuant to Section 22.4(a) of the Environmental Protection Act.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.145 Treatment Standards for Hazardous Debris

a)  Treatment Standards.  Hazardous debris must be treated prior to land disposal as follows, unless the Agency has determined, under 35 Ill. Adm. Code 721.103(f)(2), that the debris is no longer contaminated with hazardous waste or the debris is treated to the waste-specific treatment standard provided in this Subpart D for the waste contaminating the debris:

1)  General.  Hazardous debris must be treated for each “contaminant subject to treatment”, defined by subsection (b), using the technology or technologies identified in Table F.

2)  Characteristic Debris.  Hazardous debris that exhibits the characteristic of ignitability, corrosivity, or reactivity identified under 35 Ill. Adm. Code 721.121, 721.122, or 721.123, respectively, must be deactivated by treatment using one of the technologies identified in Table F.

3)  Mixtures of Debris Types.  The treatment standards of Table F must be achieved for each type of debris contained in a mixture of debris types.  If an immobilization technology is used in a treatment train, it must be the last treatment technology used.

4)  Mixtures of Contaminant Types.  Debris that is contaminated with two or more contaminants subject to treatment identified under subsection (b) must be treated for each contaminant using one or more treatment technologies identified in Table F.  If an immobilization technology is used in a treatment train, it must be the last treatment technology used.

5)  Waste PCBs.  Hazardous debris that is also a waste PCB under 40 CFR 761 (Polychlorinated Biphenyls (PCBs) Manufacturing, Processing, Distribution in Commerce, and Use Prohibitions), incorporated by reference in 35 Ill. Adm. Code 720.111(b), is subject to the requirements of either 40 CFR 761 or the requirements of this Section, whichever are more stringent.

b)  Contaminants Subject to Treatment.  Hazardous debris must be treated for each “contaminant subject to treatment”.  The contaminants subject to treatment must be determined as follows:

1)  Toxicity Characteristic Debris.  The contaminants subject to treatment for debris that exhibits the Toxicity Characteristic (TC) by 35 Ill. Adm. Code 721.124 are those EP constituents for which the debris exhibits the TC toxicity characteristic.

2)  Debris Contaminated with Listed Waste.  The contaminants subject to treatment for debris that is contaminated with a prohibited listed hazardous waste are those constituents or wastes for which treatment standards are established for the waste under Section 728.140 and Table T.

3)  Cyanide Reactive Debris.  Hazardous debris that is reactive because of cyanide must be treated for cyanide.

c)  Conditioned Exclusion of Treated Debris.  Hazardous debris that has been treated using one of the specified extraction or destruction technologies in Table F and that does not exhibit a characteristic of hazardous waste identified under Subpart C of 35 Ill. Adm. Code 721 after treatment is not a hazardous waste and need not be managed in a subtitle C facility.  Hazardous debris contaminated with a listed waste that is treated by an immobilization technology specified in Table F is a hazardous waste and must be managed in a RCRA Subtitle C treatment, storage, or disposal facility.

d)  Treatment Residuals

1)  General Requirements.  Except as provided by subsections (d)(2) and (d)(4):

A)  Residue from the treatment of hazardous debris must be separated from the treated debris using simple physical or mechanical means; and

B)  Residue from the treatment of hazardous debris is subject to the waste-specific treatment standards provided by Subpart D for the waste contaminating the debris.

2)  Nontoxic Debris.  Residue from the deactivation of ignitable, corrosive, or reactive characteristic hazardous debris (other than cyanide-reactive) that is not contaminated with a contaminant subject to treatment defined by subsection (b), must be deactivated prior to land disposal and is not subject to the waste-specific treatment standards of Subpart D.

3)  Cyanide-Reactive Debris.  Residue from the treatment of debris that is reactive because of cyanide must meet the standards for USEPA hazardous waste number D003 under Section 728.140 and Table T.

4)  Ignitable Nonwastewater Residue.  Ignitable nonwastewater residue containing equal to or greater than 10 percent total organic carbon is subject to the technology specified in the treatment standard for USEPA hazardous waste number D001:  Ignitable Liquids.

5)  Residue from Spalling.  Layers of debris removed by spalling are hazardous debris that remains subject to the treatment standards of this Section.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.146 Alternative Treatment Standards Based on HTMR

For the treatment standards previously found in Table G, as formerly referenced in this Section, refer to Section 728.140 and Table T, “Treatment Standards for Hazardous Wastes”.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.148 Universal Treatment Standards

Table U, “Universal Treatment Standards (UTS)”, identifies the hazardous constituents, along with the nonwastewater and wastewater treatment standard levels, that are used to regulate most prohibited hazardous wastes with numerical limits. For determining compliance with treatment standards for underlying hazardous constituents, as defined in Section 728.102(i), these treatment standards may not be exceeded. Compliance with these treatment standards is measured by an analysis of grab samples, unless otherwise noted in Table U.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


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.  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) as needing to comply with LDRs must be treated according to the applicable treatment standards specified in subsection (c) or according to the universal treatment standards specified in Section 728.148 and Table U 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) 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) as needing to comply with LDRs must be treated according to all the standards specified in this subsection (c) or according to the universal treatment standards specified in Section 728.148 and Table U.

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).

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).

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.

2)  Soils That Exhibit the Characteristic of Ignitability, Corrosivity or Reactivity.  In addition to the treatment required by subsection (c)(1), 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), 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); 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), constituents subject to treatment are any constituents listed in Table U, 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) as needing to comply with LDRs must be managed as follows:

1)  Soil residuals are subject to the treatment standards of this Section;

2)  Non-soil residuals are subject to the following requirements:

A)  For soils contaminated by listed hazardous waste, the RCRA Subtitle C standards applicable to the listed hazardous waste; and

B)  For soils that exhibit a characteristic of hazardous waste, if the non-soil residual also exhibits a characteristic of hazardous waste, the treatment standards applicable to the characteristic hazardous waste.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)

SUBPART E: PROHIBITIONS ON STORAGE

Section 728.150 Prohibitions on Storage of Restricted Wastes

a)  Except as provided in this Section, the storage of hazardous wastes restricted from land disposal under Subpart C is prohibited, unless the following conditions are met:

1)  A generator stores such wastes in tanks, containers, or containment buildings on-site solely for the purpose of the accumulation of such quantities of hazardous waste as necessary to facilitate proper recovery, treatment, or disposal and the generator complies with the requirements in 35 Ill. Adm. Code 722.116 and 722.117 and 35 Ill. Adm. Code 724 and 725. (A generator that is in existence on the effective date of a regulation under this Part and that must store hazardous wastes for longer than 90 days due to the regulations under this Part becomes an owner or operator of a storage facility and must obtain a RCRA permit, as required by 35 Ill. Adm. Code 703. Such a facility may qualify for interim status upon compliance with the regulations governing interim status under 35 Ill. Adm. Code 703.153.)

2)  An owner or operator of a hazardous waste treatment, storage, or disposal facility stores such wastes in tanks, containers, or containment buildings solely for the purpose of the accumulation of such quantities of hazardous waste as necessary to facilitate proper recovery, treatment, or disposal and each of the following conditions are fulfilled:

A)  Each container is clearly marked with the following to identify:

i)  The words “Hazardous Waste”;

ii)  The applicable USEPA hazardous waste numbers in Subparts C and D of 35 Ill. Adm. Code 721; or use a nationally recognized electronic system, such as bar coding, to identify the USEPA hazardous waste numbers;

iii)  An indication of the hazards of the contents (examples include, but are not limited to, the applicable hazardous waste characteristics (i.e., ignitable, corrosive, reactive, toxic); hazard communication consistent with subpart E (Labeling) or subpart F (Placarding) of 49 CFR 172, incorporated by reference in 35 Ill. Adm. Code 720.111; a hazard statement or pictogram consistent with 29 CFR 1910.1200, incorporated by reference in 35 Ill. Adm. Code 720.111; or a chemical hazard label consistent with NFPA 704, incorporated by reference in 35 Ill. Adm. Code 720.111); and

iv)  The date each period of accumulation begins.

B)  Each tank is clearly marked with a description of its contents, the quantity of each hazardous waste received and the date each period of accumulation begins, or such information is recorded and maintained in the operating record at the facility. Regardless of whether the tank itself is marked, the owner and operator must comply with the operating record requirements of 35 Ill. Adm. Code 724.173 or 725.173.

3)  A transporter stores manifested shipments of such wastes at a transfer facility for 10 days or less.

4)  A healthcare facility accumulates such wastes in containers on site solely for the purpose of accumulating the quantities of hazardous waste pharmaceuticals as necessary to facilitate proper recovery, treatment, or disposal, and the healthcare facility complies with the applicable requirements in 35 Ill. Adm. Code 726.602 and 726.603.

5)  A reverse distributor accumulates such wastes in containers on site solely for the purpose of accumulating the quantities of hazardous waste pharmaceuticals as necessary to facilitate proper recovery, treatment, or disposal, and the reverse distributor complies with 35 Ill. Adm. Code 726.610.

b)  An owner or operator of a treatment, storage, or disposal facility may store such wastes for up to one year unless the Agency can demonstrate that such storage was not solely for the purpose of accumulation of such quantities of hazardous waste as are necessary to facilitate proper recovery, treatment, or disposal.

c)  An owner or operator of a treatment, storage, or disposal facility may store wastes beyond one year; however, the owner or operator bears the burden of proving that such storage was solely for the purpose of accumulation of such quantities of hazardous waste as are necessary to facilitate proper recovery, treatment, or disposal.

d)  If a generator’s waste is exempt from a prohibition on the type of land disposal utilized for the waste (for example, because of an approved case-by-case extension granted by USEPA under 40 CFR 268.5, an approved Section 728.106 petition or a national capacity variance granted by USEPA under subpart C of 40 CFR 268), the prohibition in subsection (a) does not apply during the period of such exemption.

e)  The prohibition in subsection (a) does not apply to hazardous wastes that meet the treatment standards specified under Sections 728.141, 728.142, and 728.143 or the adjusted treatment standards specified under Section 728.144, or, if treatment standards have not been specified, the waste is in compliance with the applicable prohibitions specified in Section 728.132 or 728.139.

f)  Liquid hazardous wastes containing PCBs at concentrations greater than or equal to 50 ppm must be stored at a facility that meets the requirements of federal 40 CFR 761.65(b) (Storage for Disposal), incorporated by reference in 35 Ill. Adm. Code 720.111(b), and must be removed from storage and treated or disposed as required by the Part within one year of the date when such wastes are first placed into storage. The provisions of subsection (c) do not apply to such PCB wastes prohibited under Section 728.132.

g)  The prohibition and requirements in this Section do not apply to hazardous remediation wastes stored in a staging pile approved under 35 Ill. Adm. Code 724.654.

(Source: Amended at 44 Ill. Reg. 15495, effective September 3, 2020)

Section 728.Appendix A Toxicity Characteristic Leaching Procedure (TCLP) (Repealed)

 

(Source:  Repealed at 22 Ill. Reg. 17706, effective September 28, 1998)

Section 728.Appendix B Treatment Standards (As concentrations in the Treatment Residual Extract) (Repealed)

 

(Source:  Repealed at 22 Ill. Reg. 17706, effective September 28, 1998)

Section 728.APPENDIX C List of Halogenated Organic Compounds Regulated under Section 728.132

In determining the concentration of halogenated organic compounds (HOCs) in a hazardous waste for purposes of the Section 728.132 land disposal prohibition, USEPA has defined the HOCs that must be included in a calculation as any compounds having a carbon-halogen bond that are listed in this Appendix (see Section 728.102). This Appendix C to Part 728 consists of the following compounds:

I. Volatiles

1.  Bromodichloromethane (CAS No. 75-27-4)
2.  Bromomethane (CAS No. 74-83-9)
3.  Carbon Tetrachloride (tetrachloromethane) (CAS No. 56-23-5)
4.  Chlorobenzene (CAS No. 108-90-7)
5.  2-Chloro-1,3-butadiene (CAS No. 126-99-8)
6.  Chlorodibromomethane (CAS No. 124-48-1)
7.  Chloroethane (CAS No. 75-00-3)
8.  2-Chloroethyl vinyl ether ((2-chloroethoxy)ethene) (CAS No. 110-75-8)
9.  Chloroform (trichloromethane) (CAS No. 67-66-3)
10.  Chloromethane (CAS No. 74-87-3)
11.  3-Chloropropene (3-chloroprop-1-ene) (CAS No. 107-05-1)
12.  1,2-Dibromo-3-chloropropane (CAS No. 96-12-8)
13.  1,2-Dibromoethane (CAS No. 106-93-4)
14.  Dibromomethane (CAS No. 74-95-3)
15.  Trans-1,4-Dichloro-2-butene ((2E)-1,4-dichloro-2-butene) (CAS No. 110-57-6)
16.  Dichlorodifluoromethane (CAS No. 75-71-8)
17.  1,1-Dichloroethane (CAS No. 75-34-3)
18.  1,2-Dichloroethane (CAS No. 107-06-2)
19.  1,1-Dichloroethylene (1,1-dichloroethene) (CAS No. 75-35-4)
20.  Trans-1,2-Dichloroethene ((1E)-1,2-dichloroethene) (CAS No. 156-60-5)
21.  1,2-Dichloropropane (CAS No. 78-87-5)
22.  Trans-1,3-Dichloropropene ((1E)-1,3-dichloroprop-1-ene) (CAS No. 10061-02-6)
23.  cis-1,3-Dichloropropene ((1Z)-1,3-dichloroprop-1-ene) (CAS No. 10061-01-5)
24.  Iodomethane (CAS No. 74-88-4)
25.  Methylene chloride (dichloromethane) (CAS No. 75-09-2)
26.  1,1,1,2-Tetrachloroethane (CAS No. 630-20-6)
27.  1,1,2,2-Tetrachloroethane (CAS No. 79-34-5)
28.  Tetrachloroethene (CAS No. 127-18-4)
29.  Tribromomethane (CAS No. 75-25-2)
30.  1,1,1-Trichloroethane (CAS No. 71-55-6)
31.  1,1,2-Trichloroethane (CAS No. 79-00-5)
32.  Trichloroethene (CAS No. 79-01-6)
33.  Trichloromonofluoromethane (trichlorofluoromethane) (CAS No. 75-69-4)
34.  1,2,3-trichloropropane (CAS No. 96-18-4)

35.  Vinyl Chloride (chloroethene) (CAS No. 75-01-4)

II. Semivolatiles

1.  Bis(2-chloroethoxy)ethane (1,2-bis(2-chlorethoxy)ethane) (CAS No. 112-26-5)
2.  Bis(2-chloroethyl) ether (1,1'-oxybis(2-chloroethane)) (CAS No. 111-44-4)
3.  Bis(2-chloroisopropyl)ether (2,2'-oxybis(2-chloropropane)) (CAS No. 39638-32-9)
4.  p-Chloroaniline (4-chlorobenzeneamine) (CAS No. 106-47-8)
5.  Chlorobenzilate (ethyl 2,2-bis(4-chlorophenyl)-2-hydroxyacetate) (CAS No. 510-15-6)
6.  p-Chloro-m-cresol (4-chloro-3-methylphenol) (CAS No. 59-50-7)
7.  2-Chloronaphthalene (CAS No. 91-58-7)
8.  2-Chlorophenol (CAS No. 95-57-8)
9.  3-Chloropropionitrile (3-chloropronanenitrile) (CAS No. 542-76-7)
10.  m-Dichlorobenzene (1,3-dichlorobenzene) (CAS No. 541-73-1)
11.  o-Dichlorobenzene (1,2-dichlorobenzene) (CAS No. 95-50-1)
12.  p-Dichlorobenzene (1,4-dichlorobenzene) (CAS No. 106-46-7)
13.  3,3'-Dichlorobenzidine (4-(4-amino-3-chlorophenyl)-2-chloroaniline) (CAS No. 91-94-1)
14.  2,4-Dichlorophenol (CAS No. 120-83-2)
15.  2,6-Dichlorophenol (CAS No. 87-65-0)
16.  Hexachlorobenzene (CAS No. 118-74-1)
17.  Hexachlorobutadiene (hexachlorobuta-1,3-diene) (CAS No. 87-68-3)
18.  Hexachlorocyclopentadiene (CAS No. 77-47-4)
19.  Hexachloroethane (CAS No. 67-72-1)
20.  Hexachlorophene (2,2'-methylenebis(3,4,6-trichlorophenol)) (CAS No. 70-30-4)
21.  Hexachloropropene (CAS No. 1888-71-7)
22.  4,4'-Methylenebis(2-chloroanaline) (4-[(4-amino-3-chlorophenyl)methyl]-2-chloroaniline) (CAS No. 101-14-4)
23.  Pentachlorobenzene (CAS No. 608-93-5)
24.  Pentachloroethane (CAS No. 76-01-7)
25.  Pentachloronitrobenzene (CAS No. 82-68-8)
26.  Pentachlorophenol (CAS No. 87-86-5)
27.  Pronamide (3,5-dichloro-N-(1,1-dimethylprop-2-ynyl)benzamide) (CAS No. 23950-58-5)
28.  1,2,4,5-Tetrachlorobenzene (CAS No. 95-94-3)
29.  2,3,4,6-Tetrachlorophenol (CAS No. 58-90-2)
30.  1,2,4-Trichlorobenzene (CAS No. 120-82-1)
31.  2,4,5-Trichlorophenol (CAS No. 95-95-4)
32.  2,4,6-Trichlorophenol (CAS No. 88-06-2)

33.  Tris(2,3-dibromopropyl) phosphate (CAS No. 126-72-7)

III. Organochlorine Pesticides

1.  Aldrin ((1R,4S,4aS,5S,8R,8aR)-1,2,3,4,10,10-hexachloro-1,2,4a,5,8,8a-hexahydro-1,4:5,8-dimethanonaphthlene) (CAS No. 309-00-2)
2.  alpha-BHC (α-1,2,3,4,5,6-hexachlorocyclohexane) (CAS No. 319-84-6)
3.  beta-BHC (β-1,2,3,4,5,6-hexachlorocyclohexane) (CAS No. 319-85-7)
4.  delta-BHC (δ-1,2,3,4,5,6-hexachlorocyclohexane) (CAS No. 58-89-9)
5.  gamma-BHC (γ-1,2,3,4,5,6-hexachlorocyclohexane) (CAS No. 319-86-8)
6.  Chlordane (1,2,4,5,6,7,8,8-octachloro-3a,4,5,5a-tetrahydro-4,7-methanoindane) (CAS No. 57-74-9)
7.  DDD (1,1-bis(4-chlorophenyl)-2,2-dichloroethane) (CAS No. 72-54-8)
8.  DDE (1,1-bis(4-chlorophenyl)-2,2-dichloroethene) (CAS No. 72-55-9)
9.  DDT (1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane) (CAS No. 50-29-3)
10.  Dieldrin ((1aR,2R,2aS,3S,6R,7S,7aS)-3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-2,7:3,6-dimethanonaphtho[2,3-b]oxirene) (CAS No. 60-57-1)
11.  Endosulfan I ((3α,5aβ,6α,9α,9aβ)-6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-6,9-methano-2,4,3-benzodioxathiepine-3-oxide) (CAS No. 959-98-8)
12.  Endosulfan II ((3α,5aβ,6β,9β,9aα)-6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-6,9-methano-2,4,3-benzodioxathiepine-3-oxide) (CAS No. 33213-65-9)
13.  Endrin (1aα,2β,2aβ,3aα,6α,6aβ,7β,7aα)-3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-2,7:3,6-dimethanonaphth(2,3-b)oxirene) (CAS No. 72-20-8)
14.  Endrin aldehyde (1α,2β,2aβ,4β,4aβ,5β,6aβ,6bβ,7R*)-2,2a,3,3,4,7-hexachlorodecahydro-1,2,4-methenocyclopenta(c,d)pentalene-5-carboxaldehyde) (CAS No. 7421-93-4)
15.  Heptachlor (1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro-4,7-methano-1H-indene) (CAS No. 76-44-8)
16.  Heptachlor epoxide ((1aR,1bS,2R,5S,5aR,6S,6aR)-2,3,4,5,6,7,7-heptachloro-1a,1b,5,5a,6,6a-hexahydro-2,5-methano-2H-indeno(1,2b)oxirene) (CAS No. 1024-57-3)
17.  Isodrin ((1R,4S,4aS,5R,8S,8aR)-rel-1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-1,4:5,8-dimethanonaphthalene) (CAS No. 465-73-6)
18.  Kepone (1,1a,3,3a,4,5,5,5a,5b,6-decachlorooctahydro-1,3,4-metheno-2H-cyclobuta(cd)pentalen-2-one) (CAS No. 143-50-0)
19.  Methoxychlor (1,1'-(2,2,2-trichloroethylidene)bis(4-methoxybenzene)) (CAS No. 72-43-5)

20.  Toxaphene (CAS No. 8001-35-2)

IV. Phenoxyacetic Acid Herbicides

1.  2,4-Dichlorophenoxyacetic acid (CAS No. 94-75-7)
2.  Silvex (2-(2,4,5-trichlorophenoxy)propionic acid) (CAS No. 93-72-1)

3.  2,4,5-T (2,4,5-trichlorophenoxyacetic acid) (CAS No. 93-76-5)

V. PCBs

1.  Aroclor 1016 (CAS No. 12674-11-2)
2.  Aroclor 1221 (CAS No. 11104-28-2)
3.  Aroclor 1232 (CAS No. 11141-16-5)
4.  Aroclor 1242 (CAS No. 53469-21-9)
5.  Aroclor 1248 (CAS No. 12672-29-6)
6.  Aroclor 1254 (CAS No. 11097-69-1)
7.  Aroclor 1260 (CAS No. 11096-82-5)

8.  PCBs not otherwise specified (CAS No. 1336-36-3)

VI. Dioxins and Furans

1.  Hexachlorodibenzo-p-dioxins (CAS No. 34465-46-8)
2.  Hexachlorodibenzofuran (CAS No. 55684-94-1)
3.  Pentachlorodibenzo-p-dioxins (CAS No. 36088-22-9)
4.  Pentachlorodibenzofuran (CAS No. 30402-15-4)
5.  Tetrachlorodibenzo-p-dioxins (CAS No. 41903-57-5)
6.  Tetrachlorodibenzofuran (CAS No. 30402-14-3; 55722-27-5)

7.  2,3,7,8-Tetrachlorodibenzo-p-dioxin (2,3,7,8-tetrachlorodibenzo[b,e][1,4]dioxin) (CAS No. 1746-01-6)

BOARD NOTE: Derived from appendix III to 40 CFR 268 (2015).

(Source: Amended at 40 Ill. Reg. 12052, effective August 9, 2016)

Section 728.APPENDIX D Wastes Excluded from Lab Packs

Hazardous waste with the following USEPA hazardous waste numbers may not be placed in lab packs under the alternative lab pack treatment standards of Section 728.142(c): D009, F019, K003, K004, K005, K006, K062, K071, K100, K106, P010, P011, P012, P076, P078, U134, and U151.

BOARD NOTE: 35 Ill. Adm. Code 729.301 and 729.312 include additional limitations on the use of lab packs.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)

Section 728.Appendix E Organic Lab Packs (Repealed)

 

(Source: Repealed at 19 Ill. Reg. 9660, effective June 27, 1995)

Section 728.APPENDIX F Technologies to Achieve Deactivation of Characteristics

The treatment standard for many characteristic wastes is stated in Table T, entitled “Treatment Standards for Hazardous Wastes”, as “DEACT and meet Section 728.148 standards”.  USEPA has determined that many technologies, when used alone or in combination, can achieve the deactivation portion of the treatment standard.  Characteristic wastes that are not managed in a facility regulated by the CWA or in a CWA-equivalent facility, and that also contain underlying hazardous constituents (see Section 728.102(i)) must be treated not only by a “deactivating” technology to remove the characteristic, but also to achieve the universal treatment standards (UTS) for underlying hazardous constituents.  This Appendix F presents a partial list of technologies, utilizing the five letter technology codes established in Table C, that may be useful in meeting the treatment standard.  Use of these specific technologies is not mandatory and does not preclude direct reuse, recovery or the use of other pretreatment technologies, provided deactivation is achieved and underlying hazardous constituents are treated to achieve the UTS.

USEPA hazardous waste number/subcategory Nonwastewaters Wastewaters
D001 Ignitable Liquids based on 35 Ill. Adm. Code 721.121(a)(1)—Low TOC Nonwastewater Subcategory (containing one percent to <10 percent TOC) RORGS
WETOX
INCIN
CHOXD
BIODG
n.a.
D001 Ignitable Liquids based on 35 Ill. Adm. Code 721.121(a)(1)—Ignitable Wastewater Subcategory (containing <one percent TOC) n.a. WETOX
RORGS
INCIN
CHOXD
BIODG
D001 Compressed Gases based on 35 Ill. Adm. Code 721.121(a)(3) RCGAS
FSUBS
INCIN
ADGAS fb.
INCIN
ADGAS fb.
(CHOXD; or
CHRED)
n.a.
D001 Ignitable Reactives based on 35 Ill. Adm. Code 721.121(a)(2) WTRRX
CHOXD
CHRED
STABL
INCIN
n.a.
D001 Ignitable Oxidizers based on 35 Ill. Adm. Code 721.121(a)(4) CHRED
INCIN
CHRED
INCIN
D002 Acid Subcategory based on 35 Ill. Adm. Code 721.122(a)(1) with pH less than or equal to two RCORR
NEUTR
INCIN
NEUTR
INCIN
D002 Alkaline Subcategory based on 35 Ill. Adm. Code 721.122(a)(1) with pH greater than or equal to 12.5 NEUTR
INCIN
NEUTR
INCIN
D002 Other Corrosives based on 35 Ill. Adm. Code 721.122(a)(2) CHOXD
CHRED
INCIN
STABL
CHOXD
CHRED
INCIN
D003 Water Reactives based on 35 Ill. Adm. Code 721.123(a)(2), (a)(3), and (a)(4) INCIN
WTRRX
CHOXD
CHRED
n.a.
D003 Reactive Sulfides based on 35 Ill. Adm. Code 721.123(a)(5) CHOXD
CHRED
INCIN
STABL
CHOXD
CHRED
BIODG
INCIN
D003 Explosives based on 35 Ill. Adm. Code 721.123(a)(6), (a)(7), and (a)(8) INCIN
CHOXD
CHRED
INCIN
CHOXD
CHRED
BIODG
CARBN
D003 Other Reactives based on 35 Ill. Adm. Code 721.123(a)(1) INCIN
CHOXD
CHRED
INCIN
CHOXD
CHRED
BIODG
CARBN
K044 Wastewater treatment sludges from the manufacturing and processing of explosives CHOXD
CHRED
INCIN
CHOXD
CHRED
BIODG
CARBN
INCIN
K045 Spent carbon from the treatment of wastewaters containing explosives CHOXD
CHRED
INCIN
CHOXD
CHRED
BIODG
CARBN
INCIN
K047 Pink/red water from TNT operations CHOXD
CHRED
INCIN
CHOXD
CHRED
BIODG
CARBN
INCIN

 
Note:  “n.a.” stands for “not applicable”.

“fb.” stands for “followed by”.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


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)
August 9, 1993
D001 High TOC Ignitable Liquids
August 8, 1990
D002c All
August 9, 1993
D003e Newly identified surface-disposed elemental phosphorus processing wastes
May 26, 2000
D004 Newly identified D004 and mineral processing wastes
August 24, 1998
D004 Mixed radioactive/newly identified D004 or mineral processing wastes
May 26, 2000
D005 Newly identified D005 and mineral processing wastes
August 24, 1998
D005 Mixed radioactive/newly identified D005 or mineral processing wastes
May 26, 2000
D006 Newly identified D006 and mineral processing wastes
August 24, 1998
D006 Mixed radioactive/newly identified D006 or mineral processing wastes
May 26, 2000
D007 Newly identified D007 and mineral processing wastes
August 24, 1998
D007 Mixed radioactive/newly identified D007or mineral processing wastes
May 26, 2000
D008 Newly identified D008 and mineral processing waste
August 24, 1998
D008 Mixed radioactive/newly identified D008 or mineral processing wastes
May 26, 2000
D009 Newly identified D009 and mineral processing waste
August 24, 1998
D009 Mixed radioactive/newly identified D009or mineral processing wastes
May 26, 2000
D010 Newly identified D010 and mineral processing wastes
August 24, 1998
D010 Mixed radioactive/newly identified D010 or mineral processing wastes
May 26, 2000
D011 Newly identified D011 and mineral processing wastes
August 24, 1998
D011 Mixed radioactive/newly identified D011or mineral processing wastes
May 26, 2000
D012 (that exhibit the toxicity characteristic based on the TCLP)d All
December 14, 1994
D013 (that exhibit the toxicity characteristic based on the TCLP)d All
December 14, 1994
D014 (that exhibit the toxicity characteristic based on the TCLP)d All
December 14, 1994
D015 (that exhibit the toxicity characteristic based on the TCLP)d All
December 14, 1994
D016 (that exhibit the toxicity characteristic based on the TCLP)d All
December 14, 1994
D017 (that exhibit the toxicity characteristic based on the TCLP)d All
December 14, 1994
D018 Mixed with radioactive wastes
September 19, 1996
D018 All others
December 19, 1994
D019 Mixed with radioactive wastes
September 19, 1996
D019 All others
December 19, 1994
D020 Mixed with radioactive wastes
September 19, 1996
D020 All others
December 19, 1994
D021 Mixed with radioactive wastes
September 19, 1996
D021 All others
December 19, 1994
D022 Mixed with radioactive wastes
September 19, 1996
D022 All others
December 19, 1994
D023 Mixed with radioactive wastes
September 19, 1996
D023 All others
December 19, 1994
D024 Mixed with radioactive wastes
September 19, 1996
D024 All others
December 19, 1994
D025 Mixed with radioactive wastes
 
September 19, 1996
D025 All others
December 19, 1994
D026 Mixed with radioactive wastes
September 19, 1996
D026 All others
December 19, 1994
D027 Mixed with radioactive wastes
September 19, 1996
D027 All others
December 19, 1994
D028 Mixed with radioactive wastes
September 19, 1996
D028 All others
December 19, 1994
D029 Mixed with radioactive wastes
September 19, 1996
D029 All others
December 19, 1994
D030 Mixed with radioactive wastes
September 19, 1996
D030 All others
December 19, 1994
D031 Mixed with radioactive wastes
September 19, 1996
D031 All others
December 19, 1994
D032 Mixed with radioactive wastes
September 19, 1996
D032 All others
December 19, 1994
D033 Mixed with radioactive wastes
September 19, 1996
D033 All others
December 19, 1994
D034 Mixed with radioactive wastes
September 19, 1996
D034 All others
December 19, 1994
D035 Mixed with radioactive wastes
September 19, 1996
D035 All others
December 19, 1994
D036 Mixed with radioactive wastes
September 19, 1996
D036 All others
December 19, 1994
D037 Mixed with radioactive wastes
September 19, 1996
D037 All others
December 19, 1994
D038 Mixed with radioactive wastes
September 19, 1996
D038 All others
December 19, 1994
D039 Mixed with radioactive wastes
September 19, 1996
D039 All others
December 19, 1994
D040 Mixed with radioactive wastes
September 19, 1996
D040 All others
December 19, 1994
D041 Mixed with radioactive wastes
September 19, 1996
D041 All others
December 19, 1994
D042 Mixed with radioactive wastes
September 19, 1996
D042 All others
December 19, 1994
D043 Mixed with radioactive wastes
September 19, 1996
D043 All others
December 19, 1994
F001 Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids
November 8, 1988
F001 All others
November 8, 1986
F002 (1,1,2-trichloroethane) Wastewater and Nonwastewater
August 8, 1990
F002 Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids
November 8, 1988
F002 All others
November 8, 1986
F003 Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids
November 8, 1988
F003 All others
November 8, 1986
F004 Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids
November 8, 1988
F004 All others
November 8, 1986
F005 (benzene, 2-ethoxy ethanol, 2-nitropropane) Wastewater and Nonwastewater
August 8, 1990
F005 Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids
November 8, 1988
F005 All others
November 8, 1986
F006 Wastewater
August 8, 1990
F006 Nonwastewater
August 8, 1988
F006 (cyanides) Nonwastewater
July 8, 1989
F007 All
July 8, 1989
F008 All
July 8, 1989
F009 All
July 8, 1989
F010 All
June 8, 1989
F011 (cyanides) Nonwastewater
December 8, 1989
F011 All others
July 8, 1989
F012 (cyanides) Nonwastewater
December 8, 1989
F012 All others
July 8, 1989
F019 All
August 8, 1990
F020 All
November 8, 1988
F021 All
November 8, 1988
F025 All
August 8, 1990
F026 All
November 8, 1988
F027 All
November 8, 1988
F028 All
November 8, 1988
F032 Mixed with radioactive wastes
May 12, 1999
F032 All others
August 12, 1997
F034 Mixed with radioactive wastes
May 12, 1999
F034 All others
August 12, 1997
F035 Mixed with radioactive wastes
May 12, 1999
F035 All others
August 12, 1997
F037 Not generated from surface impoundment cleanouts or closures
June 30, 1993
F037 Generated from surface impoundment cleanouts or closures
June 30, 1994
F037 Mixed with radioactive wastes
June 30, 1994
F038 Not generated from surface impoundment cleanouts or closures
June 30, 1993
F038 Generated from surface impoundment cleanouts or closures
June 30, 1994
F038 Mixed with radioactive wastes
June 30, 1994
F039 Wastewater
August 8, 1990
F039 Nonwastewater
May 8, 1992
K001 (organics)b All
August 8, 1988
K001 All others
August 8, 1988
K002 All
August 8, 1990
K003 All
August 8, 1990
K004 Wastewater
August 8, 1990
K004 Nonwastewater
August 8, 1988
K005 Wastewater
August 8, 1990
K005 Nonwastewater
June 8, 1989
K006 All
August 8, 1990
K007 Wastewater
August 8, 1990
K007 Nonwastewater
June 8, 1989
K008 Wastewater
August 8, 1990
K008 Nonwastewater
August 8, 1988
K009 All
June 8, 1989
K010 All
June 8, 1989
K011 Wastewater
August 8, 1990
K011 Nonwastewater
June 8, 1989
K013 Wastewater
August 8, 1990
K013 Nonwastewater
June 8, 1989
K014 Wastewater
August 8, 1990
K014 Nonwastewater
June 8, 1989
K015 Wastewater
August 8, 1988
K015 Nonwastewater
August 8, 1990
K016 All
August 8, 1988
K017 All
August 8, 1990
K018 All
August 8, 1988
K019 All
August 8, 1988
K020 All
August 8, 1988
K021 Wastewater
August 8, 1990
K021 Nonwastewater
August 8, 1988
K022 Wastewater
August 8, 1990
K022 Nonwastewater
August 8, 1988
K023 All
June 8, 1989
K024 All
August 8, 1988
K025 Wastewater
August 8, 1990
K025 Nonwastewater
August 8, 1988
K026 All
August 8, 1990
K027 All
June 8, 1989
K028 (metals) Nonwastewater
August 8, 1990
K028 All others
June 8, 1989
K029 Wastewater
August 8, 1990
K029 Nonwastewater
June 8, 1989
K030 All
August 8, 1988
K031 Wastewater
August 8, 1990
K031 Nonwastewater
May 8, 1992
K032 All
August 8, 1990
K033 All
August 8, 1990
K034 All
August 8, 1990
K035 All
August 8, 1990
K036 Wastewater
June 8, 1989
K036 Nonwastewater
August 8, 1988
K037b Wastewater
August 8, 1988
K037 Nonwastewater
August 8, 1988
K038 All
June 8, 1989
K039 All
June 8, 1989
K040 All
June 8, 1989
K041 All
August 8, 1990
K042 All
August 8, 1990
K043 All
June 8, 1989
K044 All
August 8, 1988
K045 All
August 8, 1988
K046 (Nonreactive) Nonwastewater
August 8, 1988
K046 All others
August 8, 1990
K047 All
August 8, 1988
K048 Wastewater
August 8, 1990
K048 Nonwastewater
November 8, 1990
K049 Wastewater
August 8, 1990
K049 Nonwastewater
November 8, 1990
K050 Wastewater
August 8, 1990
K050 Nonwastewater
November 8, 1990
K051 Wastewater
August 8, 1990
K051 Nonwastewater
November 8, 1990
K052 Wastewater
August 8, 1990
K052 Nonwastewater
November 8, 1990
K060 Wastewater
August 8, 1990
K060 Nonwastewater
August 8, 1988
K061 Wastewater
August 8, 1990
K061 Nonwastewater
June 30, 1992
K062 All
August 8, 1988
K069 (non-calcium sulfate) Nonwastewater
August 8, 1988
K069 All others
August 8, 1990
K071 All
August 8, 1990
K073 All
August 8, 1990
K083 All
August 8, 1990
K084 Wastewater
August 8, 1990
K084 Nonwastewater
May 8, 1992
K085 All
August 8, 1990
K086 (organics)b All
August 8, 1988
K086 All others
August 8, 1988
K087 All
August 8, 1988
K088 All others
October 8, 1997
K088 All others
January 8, 1997
K093 All
June 8, 1989
K094 All
June 8, 1989
K095 Wastewater
August 8, 1990
K095 Nonwastewater
June 8, 1989
K096 Wastewater
August 8, 1990
K096 Nonwastewater
June 8, 1989
K097 All
August 8, 1990
K098 All
August 8, 1990
K099 All
August 8, 1988
K100 Wastewater
August 8, 1990
K100 Nonwastewater
August 8, 1988
K101 (organics) Wastewater
August 8, 1988
K101 (metals) Wastewater
August 8, 1990
K101 (organics) Nonwastewater
August 8, 1988
K101 (metals) Nonwastewater
May 8, 1992
K102 (organics) Wastewater
August 8, 1988
K102 (metals) Wastewater
August 8, 1990
K102 (organics) Nonwastewater
August 8, 1988
K102 (metals) Nonwastewater
May 8, 1992
K103 All
August 8, 1988
K104 All
August 8, 1988
K105 All
August 8, 1990
K106 Wastewater
August 8, 1990
K106 Nonwastewater
May 8, 1992
K107 Mixed with radioactive wastes
June 30, 1994
K107 All others
November 9, 1992
K108 Mixed with radioactive wastes
June 30, 1994
K108 All others
November 9, 1992
K109 Mixed with radioactive wastes
June 30, 1994
K109 All others
November 9, 1992
K110 Mixed with radioactive wastes
June 30, 1994
K110 All others
November 9, 1992
K111 Mixed with radioactive wastes
June 30, 1994
K111 All others
November 9, 1992
K112 Mixed with radioactive wastes
June 30, 1994
K112 All others
November 9, 1992
K113 All
June 8, 1989
K114 All
June 8, 1989
K115 All
June 8, 1989
K116 All
June 8, 1989
K117 Mixed with radioactive wastes
June 30, 1994
K117 All others
November 9, 1992
K118 Mixed with radioactive wastes
June 30, 1994
K118 All others
November 9, 1992
K123 Mixed with radioactive wastes
June 30, 1994
K123 All others
November 9, 1992
K124 Mixed with radioactive wastes
June 30, 1994
K124 All others
November 9, 1992
K125 Mixed with radioactive wastes
June 30, 1994
K125 All others
November 9, 1992
K126 Mixed with radioactive wastes
June 30, 1994
K126 All others
November 9, 1992
K131 Mixed with radioactive wastes
June 30, 1994
K131 All others
November 9, 1992
K132 Mixed with radioactive wastes
June 30, 1994
K132 All others
November 9, 1992
K136 Mixed with radioactive wastes
June 30, 1994
K136 All others
November 9, 1992
K141 Mixed with radioactive wastes
September 19, 1996
K141 All others
December 19, 1994
K142 Mixed with radioactive wastes
September 19, 1996
K142 All others
December 19, 1994
K143 Mixed with radioactive wastes
September 19, 1996
K143 All others
December 19, 1994
K144 Mixed with radioactive wastes
September 19, 1996
K144 All others
December 19, 1994
K145 Mixed with radioactive wastes
September 19, 1996
K145 All others
December 19, 1994
K147 Mixed with radioactive wastes
September 19, 1996
K147 All others
December 19, 1994
K148 Mixed with radioactive wastes
September 19, 1996
K148 All others
December 19, 1994
K149 Mixed with radioactive wastes
September 19, 1996
K149 All others
December 19, 1994
K150 Mixed with radioactive wastes
September 19, 1996
K150 All others
December 19, 1994
K151 Mixed with radioactive wastes
September 19, 1996
K151 All others
December 19, 1994
K156 Mixed with radioactive wastes
April 8, 1998
K156 All others
July 8, 1996
K157 Mixed with radioactive wastes
April 8, 1998
K157 All others
July 8, 1996
K158 Mixed with radioactive wastes
April 8, 1998
K158 All others
July 8, 1996
K159 Mixed with radioactive wastes
April 8, 1998
K159 All others
July 8, 1996
K160 Mixed with radioactive wastes
April 8, 1998
K160 All others
July 8, 1996
K161 Mixed with radioactive wastes
April 8, 1998
K161 All others
July 8, 1996
K169 All
February 8, 1999
K170 All
February 8, 1999
K171 All
February 8, 1999
K172 All
February 8, 1999
K174 All
May 7, 2001
K175 All
May 7, 2001
K176 All
May 20, 2002
K177 All
May 20, 2002
K178 All
May 20, 2002
K181 All
August 23, 2005
P001 All
August 8, 1990
P002 All
August 8, 1990
P003 All
August 8, 1990
P004 All
August 8, 1990
P005 All
August 8, 1990
P006 All
August 8, 1990
P007 All
August 8, 1990
P008 All
August 8, 1990
P009 All
August 8, 1990
P010 Wastewater
August 8, 1990
P010 Nonwastewater
May 8, 1992
P011 Wastewater
August 8, 1990
P011 Nonwastewater
May 8, 1992
P012 Wastewater
August 8, 1990
P012 Nonwastewater
May 8, 1992
P013 (barium) Nonwastewater
August 8, 1990
P013 All others
June 8, 1989
P014 All
August 8, 1990
P015 All
August 8, 1990
P016 All
August 8, 1990
P017 All
August 8, 1990
P018 All
August 8, 1990
P020 All
August 8, 1990
P021 All
June 8, 1989
P022 All
August 8, 1990
P023 All
August 8, 1990
P024 All
August 8, 1990
P026 All
August 8, 1990
P027 All
August 8, 1990
P028 All
August 8, 1990
P029 All
June 8, 1989
P030 All
June 8, 1989
P031 All
August 8, 1990
P033 All
August 8, 1990
P034 All
August 8, 1990
P036 Wastewater
August 8, 1990
P036 Nonwastewater
May 8, 1992
P037 All
August 8, 1990
P038 Wastewater
August 8, 1990
P038 Nonwastewater
May 8, 1992
P039 All
June 8, 1989
P040 All
June 8, 1989
P041 All
June 8, 1989
P042 All
August 8, 1990
P043 All
June 8, 1989
P044 All
June 8, 1989
P045 All
August 8, 1990
P046 All
August 8, 1990
P047 All
August 8, 1990
P048 All
August 8, 1990
P049 All
August 8, 1990
P050 All
August 8, 1990
P051 All
August 8, 1990
P054 All
August 8, 1990
P056 All
August 8, 1990
P057 All
August 8, 1990
P058 All
August 8, 1990
P059 All
August 8, 1990
P060 All
August 8, 1990
P062 All
June 8, 1989
P063 All
June 8, 1989
P064 All
August 8, 1990
P065 Wastewater
August 8, 1990
P065 Nonwastewater
May 8, 1992
P066 All
August 8, 1990
P067 All
August 8, 1990
P068 All
August 8, 1990
P069 All
August 8, 1990
P070 All
August 8, 1990
P071 All
June 8, 1989
P072 All
August 8, 1990
P073 All
August 8, 1990
P074 All
June 8, 1989
P075 All
August 8, 1990
P076 All
August 8, 1990
P077 All
August 8, 1990
P078 All
August 8, 1990
P081 All
August 8, 1990
P082 All
August 8, 1990
P084 All
August 8, 1990
P085 All
June 8, 1989
P087 All
May 8, 1992
P088 All
August 8, 1990
P089 All
June 8, 1989
P092 Wastewater
August 8, 1990
P092 Nonwastewater
May 8, 1992
P093 All
August 8, 1990
P094 All
June 8, 1989
P095 All
August 8, 1990
P096 All
August 8, 1990
P097 All
June 8, 1989
P098 All
June 8, 1989
P099 (silver) Wastewater
August 8, 1990
P099 All others
June 8, 1989
P101 All
August 8, 1990
P102 All
August 8, 1990
P103 All
August 8, 1990
P104 (silver) Wastewater
August 8, 1990
P104 All others
June 8, 1989
P105 All
August 8, 1990
P106 All
June 8, 1989
P108 All
August 8, 1990
P109 All
June 8, 1989
P110 All
August 8, 1990
P111 All
June 8, 1989
P112 All
August 8, 1990
P113 All
August 8, 1990
P114 All
August 8, 1990
P115 All
August 8, 1990
P116 All
August 8, 1990
P118 All
August 8, 1990
P119 All
August 8, 1990
P120 All
August 8, 1990
P121 All
June 8, 1989
P122 All
August 8, 1990
P123 All
August 8, 1990
P127 Mixed with radioactive wastes
April 8, 1998
P127 All others
July 8, 1996
P128 Mixed with radioactive wastes
April 8, 1998
P128 All others
July 8, 1996
P185 Mixed with radioactive wastes
April 8, 1998
P185 All others
July 8, 1996
P188 Mixed with radioactive wastes
April 8, 1998
P188 All others
July 8, 1996
P189 Mixed with radioactive wastes
April 8, 1998
P189 All others
July 8, 1996
P190 Mixed with radioactive wastes
April 8, 1998
P190 All others
July 8, 1996
P191 Mixed with radioactive wastes
April 8, 1998
P191 All others
July 8, 1996
P192 Mixed with radioactive wastes
April 8, 1998
P192 All others
July 8, 1996
P194 Mixed with radioactive wastes
April 8, 1998
P194 All others
July 8, 1996
P196 Mixed with radioactive wastes
April 8, 1998
P196 All others
July 8, 1996
P197 Mixed with radioactive wastes
April 8, 1998
P197 All others
July 8, 1996
P198 Mixed with radioactive wastes
April 8, 1998
P198 All others
July 8, 1996
P199 Mixed with radioactive wastes
April 8, 1998
P199 All others
July 8, 1996
P201 Mixed with radioactive wastes
April 8, 1998
P201 All others
July 8, 1996
P202 Mixed with radioactive wastes
April 8, 1998
P202 All others
July 8, 1996
P203 Mixed with radioactive wastes
April 8, 1998
P203 All others
July 8, 1996
P204 Mixed with radioactive wastes
April 8, 1998
P204 All others
July 8, 1996
P205 Mixed with radioactive wastes
April 8, 1998
P205 All others
July 8, 1996
U001 All
August 8, 1990
U002 All
August 8, 1990
U003 All
August 8, 1990
U004 All
August 8, 1990
U005 All
August 8, 1990
U006 All
August 8, 1990
U007 All
August 8, 1990
U008 All
August 8, 1990
U009 All
August 8, 1990
U010 All
August 8, 1990
U011 All
August 8, 1990
U012 All
August 8, 1990
U014 All
August 8, 1990
U015 All
August 8, 1990
U016 All
August 8, 1990
U017 All
August 8, 1990
U018 All
August 8, 1990
U019 All
August 8, 1990
U020 All
August 8, 1990
U021 All
August 8, 1990
U022 All
August 8, 1990
U023 All
August 8, 1990
U024 All
August 8, 1990
U025 All
August 8, 1990
U026 All
August 8, 1990
U027 All
August 8, 1990
U028 All
June 8, 1989
U029 All
August 8, 1990
U030 All
August 8, 1990
U031 All
August 8, 1990
U032 All
August 8, 1990
U033 All
August 8, 1990
U034 All
August 8, 1990
U035 All
August 8, 1990
U036 All
August 8, 1990
U037 All
August 8, 1990
U038 All
August 8, 1990
U039 All
August 8, 1990
U041 All
August 8, 1990
U042 All
August 8, 1990
U043 All
August 8, 1990
U044 All
August 8, 1990
U045 All
August 8, 1990
U046 All
August 8, 1990
U047 All
August 8, 1990
U048 All
August 8, 1990
U049 All
August 8, 1990
U050 All
August 8, 1990
U051 All
August 8, 1990
U052 All
August 8, 1990
U053 All
August 8, 1990
U055 All
August 8, 1990
U056 All
August 8, 1990
U057 All
August 8, 1990
U058 All
June 8, 1989
U059 All
August 8, 1990
U060 All
August 8, 1990
U061 All
August 8, 1990
U062 All
August 8, 1990
U063 All
August 8, 1990
U064 All
August 8, 1990
U066 All
August 8, 1990
U067 All
August 8, 1990
U068 All
August 8, 1990
U069 All
June 30, 1992
U070 All
August 8, 1990
U071 All
August 8, 1990
U072 All
August 8, 1990
U073 All
August 8, 1990
U074 All
August 8, 1990
U075 All
August 8, 1990
U076 All
August 8, 1990
U077 All
August 8, 1990
U078 All
August 8, 1990
U079 All
August 8, 1990
U080 All
August 8, 1990
U081 All
August 8, 1990
U082 All
August 8, 1990
U083 All
August 8, 1990
U084 All
August 8, 1990
U085 All
August 8, 1990
U086 All
August 8, 1990
U087 All
June 8, 1989
U088 All
June 8, 1989
U089 All
August 8, 1990
U090 All
August 8, 1990
U091 All
August 8, 1990
U092 All
August 8, 1990
U093 All
August 8, 1990
U094 All
August 8, 1990
U095 All
August 8, 1990
U096 All
August 8, 1990
U097 All
August 8, 1990
U098 All
August 8, 1990
U099 All
August 8, 1990
U101 All
August 8, 1990
U102 All
June 8, 1989
U103 All
August 8, 1990
U105 All
August 8, 1990
U106 All
August 8, 1990
U107 All
June 8, 1989
U108 All
August 8, 1990
U109 All
August 8, 1990
U110 All
August 8, 1990
U111 All
August 8, 1990
U112 All
August 8, 1990
U113 All
August 8, 1990
U114 All
August 8, 1990
U115 All
August 8, 1990
U116 All
August 8, 1990
U117 All
August 8, 1990
U118 All
August 8, 1990
U119 All
August 8, 1990
U120 All
August 8, 1990
U121 All
August 8, 1990
U122 All
August 8, 1990
U123 All
August 8, 1990
U124 All
August 8, 1990
U125 All
August 8, 1990
U126 All
August 8, 1990
U127 All
August 8, 1990
U128 All
August 8, 1990
U129 All
August 8, 1990
U130 All
August 8, 1990
U131 All
August 8, 1990
U132 All
August 8, 1990
U133 All
August 8, 1990
U134 All
August 8, 1990
U135 All
August 8, 1990
U136 Wastewater
August 8, 1990
U136 Nonwastewater
May 8, 1992
U137 All
August 8, 1990
U138 All
August 8, 1990
U140 All
August 8, 1990
U141 All
August 8, 1990
U142 All
August 8, 1990
U143 All
August 8, 1990
U144 All
August 8, 1990
U145 All
August 8, 1990
U146 All
August 8, 1990
U147 All
August 8, 1990
U148 All
August 8, 1990
U149 All
August 8, 1990
U150 All
August 8, 1990
U151 Wastewater
August 8, 1990
U151 Nonwastewater
May 8, 1992
U152 All
August 8, 1990
U153 All
August 8, 1990
U154 All
August 8, 1990
U155 All
August 8, 1990
U156 All
August 8, 1990
U157 All
August 8, 1990
U158 All
August 8, 1990
U159 All
August 8, 1990
U160 All
August 8, 1990
U161 All
August 8, 1990
U162 All
August 8, 1990
U163 All
August 8, 1990
U164 All
August 8, 1990
U165 All
August 8, 1990
U166 All
August 8, 1990
U167 All
August 8, 1990
U168 All
August 8, 1990
U169 All
August 8, 1990
U170 All
August 8, 1990
U171 All
August 8, 1990
U172 All
August 8, 1990
U173 All
August 8, 1990
U174 All
August 8, 1990
U176 All
August 8, 1990
U177 All
August 8, 1990
U178 All
August 8, 1990
U179 All
August 8, 1990
U180 All
August 8, 1990
U181 All
August 8, 1990
U182 All
August 8, 1990
U183 All
August 8, 1990
U184 All
August 8, 1990
U185 All
August 8, 1990
U186 All
August 8, 1990
U187 All
August 8, 1990
U188 All
August 8, 1990
U189 All
August 8, 1990
U190 All
June 8, 1989
U191 All
August 8, 1990
U192 All
August 8, 1990
U193 All
August 8, 1990
U194 All
June 8, 1989
U196 All
August 8, 1990
U197 All
August 8, 1990
U200 All
August 8, 1990
U201 All
August 8, 1990
U203 All
August 8, 1990
U204 All
August 8, 1990
U205 All
August 8, 1990
U206 All
August 8, 1990
U207 All
August 8, 1990
U208 All
August 8, 1990
U209 All
August 8, 1990
U210 All
August 8, 1990
U211 All
August 8, 1990
U213 All
August 8, 1990
U214 All
August 8, 1990
U215 All
August 8, 1990
U216 All
August 8, 1990
U217 All
August 8, 1990
U218 All
August 8, 1990
U219 All
August 8, 1990
U220 All
August 8, 1990
U221 All
June 8, 1989
U222 All
August 8, 1990
U223 All
June 8, 1989
U225 All
August 8, 1990
U226 All
August 8, 1990
U227 All
August 8, 1990
U228 All
August 8, 1990
U234 All
August 8, 1990
U235 All
June 8, 1989
U236 All
August 8, 1990
U237 All
August 8, 1990
U238 All
August 8, 1990
U239 All
August 8, 1990
U240 All
August 8, 1990
U243 All
August 8, 1990
U244 All
August 8, 1990
U246 All
August 8, 1990
U247 All
August 8, 1990
U248 All
August 8, 1990
U249 All
August 8, 1990
U271 Mixed with radioactive wastes
April 8, 1998
U271 All others
July 8, 1996
U277 Mixed with radioactive wastes
April 8, 1998
U277 All others
July 8, 1996
U278 Mixed with radioactive wastes
April 8, 1998
U278 All others
July 8, 1996
U279 Mixed with radioactive wastes
April 8, 1998
U279 All others
July 8, 1996
U280 Mixed with radioactive wastes
April 8, 1998
U280 All others
July 8, 1996
U328 Mixed with radioactive wastes
June 30, 1994
U328 All others
November 9, 1992
U353 Mixed with radioactive wastes
June 30, 1994
U353 All others
November 9, 1992
U359 Mixed with radioactive wastes
June 30, 1994
U359 All others
November 9, 1992
U364 Mixed with radioactive wastes
April 8, 1998
U364 All others
July 8, 1996
U365 Mixed with radioactive wastes
April 8, 1998
U365 All others
July 8, 1996
U366 Mixed with radioactive wastes
April 8, 1998
U366 All others
July 8, 1996
U367 Mixed with radioactive wastes
April 8, 1998
U367 All others
July 8, 1996
U372 Mixed with radioactive wastes
April 8, 1998
U372 All others
July 8, 1996
U373 Mixed with radioactive wastes
April 8, 1998
U373 All others
July 8, 1996
U375 Mixed with radioactive wastes
April 8, 1998
U375 All others
July 8, 1996
U376 Mixed with radioactive wastes
April 8, 1998
U376 All others
July 8, 1996
U377 Mixed with radioactive wastes
April 8, 1998
U377 All others
July 8, 1996
U378 Mixed with radioactive wastes
April 8, 1998
U378 All others
July 8, 1996
U379 Mixed with radioactive wastes
April 8, 1998
U379 All others
July 8, 1996
U381 Mixed with radioactive wastes
April 8, 1998
U381 All others
July 8, 1996
U382 Mixed with radioactive wastes
April 8, 1998
U382 All others
July 8, 1996
U383 Mixed with radioactive wastes
April 8, 1998
U383 All others
July 8, 1996
U384 Mixed with radioactive wastes
April 8, 1998
U384 All others
July 8, 1996
U385 Mixed with radioactive wastes
April 8, 1998
U385 All others
July 8, 1996
U386 Mixed with radioactive wastes
April 8, 1998
U386 All others
July 8, 1996
U387 Mixed with radioactive wastes
April 8, 1998
U387 All others
July 8, 1996
U389 Mixed with radioactive wastes
April 8, 1998
U389 All others
July 8, 1996
U390 Mixed with radioactive wastes
April 8, 1998
U390 All others
July 8, 1996
U391 Mixed with radioactive wastes
April 8, 1998
U391 All others
July 8, 1996
U392 Mixed with radioactive wastes
April 8, 1998
U392 All others
July 8, 1996
U393 Mixed with radioactive wastes
April 8, 1998
U393 All others
July 8, 1996
U394 Mixed with radioactive wastes
April 8, 1998
U394 All others
July 8, 1996
U395 Mixed with radioactive wastes
April 8, 1998
U395 All others
July 8, 1996
U396 Mixed with radioactive wastes
April 8, 1998
U396 All others
July 8, 1996
U400 Mixed with radioactive wastes
April 8, 1998
U400 All others
July 8, 1996
U401 Mixed with radioactive wastes
April 8, 1998
U401 All others
July 8, 1996
U402 Mixed with radioactive wastes
April 8, 1998
U402 All others
July 8, 1996
U403 Mixed with radioactive wastes
April 8, 1998
U403 All others
July 8, 1996
U404 Mixed with radioactive wastes
April 8, 1998
U404 All others
July 8, 1996
U407 Mixed with radioactive wastes
April 8, 1998
U407 All others
July 8, 1996
U409 Mixed with radioactive wastes
April 8, 1998
U409 All others
July 8, 1996
U410 Mixed with radioactive wastes
April 8, 1998
U410 All others
July 8, 1996
U411 Mixed with radioactive wastes
April 8, 1998
U411 All others
July 8, 1996

 
a  This table 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), which the Board adopted in docket R90-11 at 15 Ill. Reg. 9462, effective June 17, 1991.

c  USEPA amended the standard in the Third Third Emergency Rule (at 58 Fed. Reg. 29860 (May 24, 1993), which the Board adopted in docket R93-16 at 18 Ill. Reg. 6799, effective April 26, 1994); the original effective date was August 8, 1990.

d  The standard was revised in the Phase II Final Rule (that USEPA adopted at 59 Fed. Reg. 47982 (September 19, 1994), which the Board adopted in docket R95-6 at 19 Ill. Reg. 9660, effective June 27, 1995); the original effective date was August 8, 1990.

e  The standards for selected reactive wastes was revised in the Phase III Final Rule (that USEPA adopted at 61 Fed. Reg. 15566 (April 8, 1996), which the Board adopted in docket R96-10/R97-3/R97-5 (consolidated) at 22 Ill. Reg. 783, effective December 16, 1997); the original effective date was August 8, 1990.

TABLE 2

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

Restricted hazardous waste in CSD
Effective date
1.  Solvent- (F001-F005) and dioxin- (F020-F023 and F026-F028) containing soil and debris from CERCLA response or RCRA corrective actions.
November 8, 1990
2.  Soil and debris not from CERCLA response or RCRA corrective actions contaminated with less than one percent total solvents (F001-F005) or dioxins (F020-F023 and F026-F028).
November 8, 1988
3.  All soil and debris contaminated with First Third wastes for which treatment standards are based on incineration.
August 8, 1990
4.  All soil and debris contaminated with Second Third wastes for which treatment standards are based on incineration.
June 8, 1991
5.  All soil and debris contaminated with Third Third wastes or, First or Second Third “soft hammer” wastes that had treatment standards promulgated in the Third Third rule, for which treatment standards are based on incineration, vitrification, or mercury retorting, acid leaching followed by chemical precipitation, or thermal recovery of metals, as well as all inorganic solids debris contaminated with D004-D011 wastes, and all soil and debris contaminated with mixed RCRA/radioactive wastes.
May 8, 1992
6.  Soil and debris contaminated with D012-D043, K141-K145, and K147-151 wastes.
December 19, 1994
7.  Debris (only) contaminated with F037, F038, K107-K112, K117, K118, K123-K126, K131, K132, K136, U328, U353, U359.
December 19, 1994
8.  Soil and debris contaminated with K156- K161, P127, P128, P188-P192, P194, P196- P199, P201-P205, U271, U277-U280, U364-U367, U372, U373, U375-U379, U381-U387, U389-U396, U400-U404, U407, and U409-U411 wastes.
July 8, 1996
9.  Soil and debris contaminated with K088 wastes.
October 8, 1997
10.  Soil and debris contaminated with radioactive wastes mixed with K088, K156-K161, P127, P128, P188-P192, P194, P196-P199, P201-P205, U271, U277-U280, U364-U367, U372, U373, U375-U379, U381-U387, U389-U396, U400-U404, U407, and U409-U411 wastes.
April 8, 1998
11.  Soil and debris contaminated with F032, F034, and F035.
May 12, 1997
12.  Soil and debris contaminated with newly identified D004-D011 toxicity characteristic wastes and mineral processing wastes.
August 24, 1998
13.  Soil and debris contaminated with mixed radioactive newly identified D011 characteristic wastes and mineral processing wastes.
May 26, 2000

 
BOARD NOTE:  These tables are provided for the convenience of the reader.

(Source: Amended at 40 Ill. Reg. 12052, effective August 9, 2016)


Section 728.APPENDIX H National Capacity LDR Variances for UIC Wastes

See Notea

USEPA Hazardous Waste Number Waste Category
Effective Date
D001 (except High TOC Ignitable Liquids Subcategory)c All
February 10, 1994
D001 (High TOC Ignitable Characteristic Liquids Subcategory) Nonwastewater
September 19, 1995
D002b All
May 8, 1992
D002c All
February 10, 1994
D003 (cyanides) All
May 8, 1992
D003 (sulfides) All
May 8, 1992
D003 (explosives, reactives) All
May 8, 1992
D007 All
May 8, 1992
D009 Nonwastewater
May 8, 1992
D012 All
September 19, 1995
D013 All
September 19, 1995
D014 All
September 19, 1995
D015 All
September 19, 1995
D016 All
September 19, 1995
D017 All
September 19, 1995
D018 All, including mixed with radioactive wastes
April 8, 1998
D019 All, including mixed with radioactive wastes
April 8, 1998
D020 All, including mixed with radioactive wastes
April 8, 1998
D021 All, including mixed with radioactive wastes
April 8, 1998
D022 All, including mixed with radioactive wastes
April 8, 1998
D023 All, including mixed with radioactive wastes
April 8, 1998
D024 All, including mixed with radioactive wastes
April 8, 1998
D025 All, including mixed with radioactive wastes
April 8, 1998
D026 All, including mixed with radioactive wastes
April 8, 1998
D027 All, including mixed with radioactive wastes
April 8, 1998
D028 All, including mixed with radioactive wastes
April 8, 1998
D029 All, including mixed with radioactive wastes
April 8, 1998
D030 All, including mixed with radioactive wastes
April 8, 1998
D031 All, including mixed with radioactive wastes
April 8, 1998
D032 All, including mixed with radioactive wastes
April 8, 1998
D033 All, including mixed with radioactive wastes
April 8, 1998
D034 All, including mixed with radioactive wastes
April 8, 1998
D035 All, including mixed with radioactive wastes
April 8, 1998
D036 All, including mixed with radioactive wastes
April 8, 1998
D037 All, including mixed with radioactive wastes
April 8, 1998
D038 All, including mixed with radioactive wastes
April 8, 1998
D039 All, including mixed with radioactive wastes
April 8, 1998
D040 All, including mixed with radioactive wastes
April 8, 1998
D041 All, including mixed with radioactive wastes
April 8, 1998
D042 All, including mixed with radioactive wastes
April 8, 1998
D043 All, including mixed with radioactive wastes
April 8, 1998
F001-F005 All spent F001-F005 solvent containing less than 1 percent total F001-F005 solvent constituents
August 8, 1990
F007 All
June 8, 1991
F032 All, including mixed with radioactive wastes
May 12, 1999
F034 All, including mixed with radioactive wastes
May 12,1999
F035 All, including mixed with radioactive wastes
May 12, 1999
F037 All
November 8, 1992
F038 All
November 8, 1992
F039 Wastewater
May 8, 1992
K009 Wastewater
June 8, 1991
K011 Nonwastewater
June 8, 1991
K011 Wastewater
May 8, 1992
K013 Nonwastewater
June 8, 1991
K013 Wastewater
May 8, 1992
K014 All
May 8, 1992
K016 (dilute) All
June 8, 1991
K049 All
August 8, 1990
K050 All
August 8, 1990
K051 All
August 8, 1990
K052 All
August 8, 1990
K062 All
August 8, 1990
K071 All
August 8, 1990
K088 All
January 8, 1997
K104 All
August 8, 1990
K107 All
November 8, 1992
K108 All
November 9, 1992
K109 All
November 9, 1992
K110 All
November 9, 1992
K111 All
November 9, 1992
K112 All
November 9, 1992
K117 All
June 30, 1995
K118 All
June 30, 1995
K123 All
November 9, 1992
K124 All
November 9, 1992
K125 All
November 9, 1992
K126 All
November 9, 1992
K131 All
June 30, 1995
K132 All
June 30, 1995
K136 All
November 9, 1992
K141 All
December 19, 1994
K142 All
December 19, 1994
K143 All
December 19, 1994
K144 All
December 19, 1994
K145 All
December 19, 1994
K147 All
December 19, 1994
K148 All
December 19, 1994
K149 All
December 19, 1994
K150 All
December 19, 1994
K151 All
December 19, 1994
K156 All
July 8, 1996
K157 All
July 8, 1996
K158 All
July 8, 1996
K159 All
July 8, 1996
K160 All
July 8, 1996
K161 All
July 8, 1996
NA Newly identified mineral processing wastes from titanium dioxide production and mixed radioactive/newly identified D004-D011 characteristic wastes and mineral processing wastes
May 26, 2000
P127 All
July 8, 1996
P128 All
July 8, 1996
P185 All
July 8, 1996
P188 All
July 8, 1996
P189 All
July 8, 1996
P190 All
July 8, 1996
P191 All
July 8, 1996
P192 All
July 8, 1996
P194 All
July 8, 1996
P196 All
July 8, 1996
P197 All
July 8, 1996
P198 All
July 8, 1996
P199 All
July 8, 1996
P201 All
July 8, 1996
P202 All
July 8, 1996
P203 All
July 8, 1996
P204 All
July 8, 1996
P205 All
July 8, 1996
U271 All
July 8, 1996
U277 All
July 8, 1996
U278 All
July 8, 1996
U279 All
July 8, 1996
U280 All
July 8, 1996
U328 All
November 9, 1992
U353 All
November 9, 1992
U359 All
November 9, 1992
U364 All
July 8, 1996
U365 All
July 8, 1996
U366 All
July 8, 1996
U367 All
July 8, 1996
U372 All
July 8, 1996
U373 All
July 8, 1996
U375 All
July 8, 1996
U376 All
July 8, 1996
U377 All
July 8, 1996
U378 All
July 8, 1996
U379 All
July 8, 1996
U381 All
July 8, 1996
U382 All
July 8, 1996
U383 All
July 8, 1996
U384 All
July 8, 1996
U385 All
July 8, 1996
U386 All
July 8, 1996
U387 All
July 8, 1996
U389 All
July 8, 1996
U390 All
July 8, 1996
U391 All
July 8, 1996
U392 All
July 8, 1996
U395 All
July 8, 1996
U396 All
July 8, 1996
U400 All
July 8, 1996
U401 All
July 8, 1996
U402 All
July 8, 1996
U403 All
July 8, 1996
U404 All
July 8, 1996
U407 All
July 8, 1996
U409 All
July 8, 1996
U410 All
July 8, 1996
U411 All
July 8, 1996

 
a  Wastes that are deep well disposed on-site receive a six-month variance, with restrictions, effective in November 1990.

b  Deep well injected D002 liquids with a pH less than two must meet the California List treatment standards on August 8, 1990.

c  Managed in systems defined in 35 Ill. Adm. Code 730.105(e) as Class V injection wells that do not engage in CWA-equivalent treatment before injection.

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

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.APPENDIX I EP Toxicity Test Method and Structural Integrity Test

BOARD NOTE: Method 1310B (Extraction Procedure Toxicity Test) is published in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.Appendix J Recordkeeping, Notification, and Certification Requirements (Repealed)

 

(Source:  Repealed at 22 Ill. Reg. 17706, effective September 28, 1998)


Section 728.APPENDIX K Metal-Bearing Wastes Prohibited from Dilution in a Combustion Unit According to Section 728.103(c)

BOARD NOTE: A combustion unit is defined as any thermal technology subject to Subpart O of 35 Ill. Adm. Code 724, Subpart O of 35 Ill. Adm. Code 725, or Subpart H of 35 Ill. Adm. Code 726.

USEPA Hazardous Waste Number Waste Description
D004 Toxicity Characteristic for Arsenic.
D005 Toxicity Characteristic for Barium.
D006 Toxicity Characteristic for Cadmium.
D007 Toxicity Characteristic for Chromium.
D008 Toxicity Characteristic for Lead.
D009 Toxicity Characteristic for Mercury.
D010 Toxicity Characteristic for Selenium.
D011 Toxicity Characteristic for Silver.
F006 Wastewater treatment sludges from electroplating operations except from the following processes: (1) sulfuric acid anodizing of aluminum; (2) tin plating carbon steel; (3) zinc plating basis on carbon steel; (4) aluminum or zinc-plating on carbon steel; (5) cleaning/stripping associated with tin, zinc and aluminum plating on carbon steel; and (6) chemical etching and milling of aluminum.
F007 Spent cyanide plating bath solutions from electroplating operations.
F008 Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process.
F009 Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process.
F010 Quenching bath residues from oil baths from metal treating operations where cyanides are used in the process.
F011 Spent cyanide solutions from salt bath pot cleaning from metal heat-treating operations.
F012 Quenching waste water treatment sludges from metal heat-treating operations where cyanides are used in the process.
F019 Wastewater treatment sludges from the chemical conversion coating of aluminum except from zirconium phosphating in aluminum car washing when such phosphating is an exclusive conversion coating process.
K002 Wastewater treatment sludge from the production of chrome yellow and orange pigments.
K003 Wastewater treatment sludge from the production of molybdate orange pigments.
K004 Wastewater treatment sludge from the production of zinc yellow pigments.
K005 Wastewater treatment sludge from the production of chrome green pigments.
K006 Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous and hydrated).
K007 Wastewater treatment sludge from the production of iron blue pigments.
K008 Oven residue from the production of chrome oxide green pigments.
K061 Emission control dust/sludge from the primary production of steel in electric furnaces.
K069 Emission control dust/sludge from secondary lead smelting.
K071 Brine purification muds from the mercury cell processes in chlorine production, where separately prepurified brine is not used.
K100 Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting.
K106 Sludges from the mercury cell processes for making chlorine.
P010 Arsenic acid H3AsO4.
P011 Arsenic oxide As2O5.
P012 Arsenic trioxide.
P013 Barium cyanide.
P015 Beryllium.
P029 Copper (I) cyanide Cu(CN).
P074 Nickel (II) cyanide Ni(CN)2.
P087 Osmium (VIII) tetroxide OsO4.
P099 Potassium silver cyanide KAg(CN)2.
P104 Silver cyanide AgCN.
P113 Thallic (III) oxide Tl2O3.
P114 Thallium (I) selenite Tl2SeO3.
P115 Thallium (I) sulfate Tl2SO4.
P119 Ammonium (V) vanadate NH3VO3.
P120 Vanadium (V) oxide V2O5.
P121 Zinc cyanide ZnCN.
U032 Calcium chromate CaCrO4.
U145 Lead phosphate.
U151 Mercury.
U204 Selenous acid H2SeO3.
U205 Selenium (IV) disulfide SeS2.
U216 Thallium (I) chloride TlCl.
U217 Thallium (I) nitrate TlNO3.

 
(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.TABLE A Constituent Concentrations in Waste Extract (CCWE)

For the requirements previously found in this Section and Section 728.141, refer to Section 728.140 and Table T, “Treatment Standards for Hazardous Wastes”.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.TABLE B Constituent Concentrations in Wastes (CCW)

For the requirements previously found in this Section and for treatment standards in Section 728.143, “Constituent Concentrations in Wastes (CCW)”, refer to Section 728.140 and Table T, “Treatment Standards for Hazardous Wastes”.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.TABLE C Technology Codes and Description of Technology-Based Standards

Technology

Code  Description of Technology-Based Standard

ADGAS  Venting of compressed gases into an absorbing or reacting media (i.e., solid or liquid)—venting can be accomplished through physical release utilizing valves or piping; physical penetration of the container; or penetration through detonation.

AMLGM  Amalgamation of liquid, elemental mercury contaminated with radioactive materials utilizing inorganic reagents such as copper, zinc, nickel, gold, and sulfur that result in a nonliquid, semi-solid amalgam and thereby reducing potential emissions of elemental mercury vapors to the air.

BIODG  Biodegradation of organics or non-metallic inorganics (i.e., degradable inorganics that contain the elements of phosphorus, nitrogen, and sulfur) in units operated under either aerobic or anaerobic conditions such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., total organic carbon (TOC) can often be used as an indicator parameter for the biodegradation of many organic constituents that cannot be directly analyzed in wastewater residues).

CARBN  Carbon adsorption (granulated or powdered) of non-metallic inorganics, organo-metallics, or organic constituents, operated so that a surrogate compound or indicator parameter has not undergone breakthrough (e.g., total organic carbon (TOC) can often be used as an indicator parameter for the adsorption of many organic constituents that cannot be directly analyzed in wastewater residues).  Breakthrough occurs when the carbon has become saturated with the constituent (or indicator parameter) and substantial change in adsorption rate associated with that constituent occurs.

CHOXD  Chemical or electrolytic oxidation utilizing the following oxidation reagents (or waste reagents) or combinations or reagents:

1)  hypochlorite (e.g., bleach);

2)  chlorine;

3)  chlorine dioxide;

4)  ozone or UV (ultraviolet light) assisted ozone;

5)  peroxides;

6)  persulfates;

7)  perchlorates;

8)  permanganates; or

9)  other oxidizing reagents of equivalent efficiency, performed in units operated so that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., total organic carbon (TOC) can often be used as an indicator parameter for the oxidation of many organic constituents that cannot be directly analyzed in wastewater residues).  Chemical oxidation specifically includes what is commonly referred to as alkaline chlorination.

CHRED  Chemical reduction utilizing the following reducing reagents (or waste reagents) or combinations of reagents:

1)  sulfur dioxide;

2)  sodium, potassium, or alkali salts of sulfites, bisulfites, metabisulfites, and polyethylene glycols (e.g., NaPEG and KPEG);

3)  sodium hydrosulfide;

4)  ferrous salts; or

5)  other reducing reagents of equivalent efficiency, performed in units operated such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., total organic halogens (TOX) can often be used as an indicator parameter for the reduction of many halogenated organic constituents that cannot be directly analyzed in wastewater residues).  Chemical reduction is commonly used for the reduction of hexavalent chromium to the trivalent state.

CMBST  High temperature organic destruction technologies, such as combustion in incinerators, boilers, or industrial furnaces operated in accordance with the applicable requirements of Subpart O of 35 Ill. Adm. Code 724, Subpart O of 35 Ill. Adm. Code 725, or Subpart H of 35 Ill. Adm. Code 726, and in other units operated in accordance with applicable technical operating requirements; and certain non-combustive technologies, such as the Catalytic Extraction Process.

DEACT  Deactivation to remove the hazardous characteristics of a waste due to its ignitability, corrosivity, or reactivity.

FSUBS  Fuel substitution in units operated in accordance with applicable technical operating requirements.

HLVIT  Vitrification of high-level mixed radioactive wastes in units in compliance with all applicable radioactive protection requirements under control of the federal Nuclear Regulatory Commission.

IMERC  Incineration of wastes containing organics and mercury in units operated in accordance with the technical operating requirements of Subpart O of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725.  All wastewater and nonwastewater residues derived from this process must then comply with the corresponding treatment standards per USEPA hazardous waste number with consideration of any applicable subcategories (e.g., high or low mercury subcategories).

INCIN  Incineration in units operated in accordance with the technical operating requirements of Subpart O of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725.

LLEXT  Liquid-liquid extraction (often referred to as solvent extraction) of organics from liquid wastes into an immiscible solvent for which the hazardous constituents have a greater solvent affinity, resulting in an extract high in organics that must undergo either incineration, reuse as a fuel, or other recovery or reuse and a raffinate (extracted liquid waste) proportionately low in organics that must undergo further treatment as specified in the standard.

MACRO  Macroencapsulation with surface coating materials such as polymeric organics (e.g., resins and plastics) or with a jacket of inert inorganic materials to substantially reduce surface exposure to potential leaching media.  Macroencapsulation specifically does not include any material that would be classified as a tank or container according to 35 Ill. Adm. Code 720.110.

NEUTR  Neutralization with the following reagents (or waste reagents) or combinations of reagents:

1)  acids;

2)  bases; or

3)  water (including wastewaters) resulting in a pH greater than two but less than 12.5 as measured in the aqueous residuals.

NLDBR  No land disposal based on recycling.

POLYM  Formation of complex high-molecular weight solids through polymerization of monomers in high-TOC D001 nonwastewaters that are chemical components in the manufacture of plastics.

PRECP  Chemical precipitation of metals and other inorganics as insoluble precipitates of oxides, hydroxides, carbonates, sulfides, sulfates, chlorides, fluorides, or phosphates.  The following reagents (or waste reagents) are typically used alone or in combination:

1)  lime (i.e., containing oxides or hydroxides of calcium or magnesium);

2)  caustic (i.e., sodium or potassium hydroxides);

3)  soda ash (i.e., sodium carbonate);

4)  sodium sulfide;

5)  ferric sulfate or ferric chloride;

6)  alum; or

7)  sodium sulfate.  Additional flocculating, coagulation, or similar reagents or processes that enhance sludge dewatering characteristics are not precluded from use.

RBERY  Thermal recovery of beryllium.

RCGAS  Recovery or reuse of compressed gases including techniques such as reprocessing of the gases for reuse or resale; filtering or adsorption of impurities; remixing for direct reuse or resale; and use of the gas as a fuel source.

RCORR  Recovery of acids or bases utilizing one or more of the following recovery technologies:

1)  distillation (i.e., thermal concentration);

2)  ion exchange;

3)  resin or solid adsorption;

4)  reverse osmosis; or

5)  incineration for the recovery of acid

Note:  this does not preclude the use of other physical phase separation or concentration techniques such as decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies.

RLEAD  Thermal recovery of lead in secondary lead smelters.

RMERC  Retorting or roasting in a thermal processing unit capable of volatilizing mercury and subsequently condensing the volatilized mercury for recovery.  The retorting or roasting unit (or facility) must be subject to one or more of the following:

a)  A federal national emissions standard for hazardous air pollutants (NESHAP) for mercury (subpart E of 40 CFR 61);

b)  A best available control technology (BACT) or a lowest achievable emission rate (LAER) standard for mercury imposed pursuant to a prevention of significant deterioration (PSD) permit (including 35 Ill. Adm. Code 201 through 203); or

c)  A state permit that establishes emission limitations (within meaning of Section 302 of the Clean Air Act) for mercury, including a permit issued pursuant to 35 Ill. Adm. Code 201.  All wastewater and nonwastewater residues derived from this process must then comply with the corresponding treatment standards per USEPA hazardous waste number with consideration of any applicable subcategories (e.g., high or low mercury subcategories).

RMETL  Recovery of metals or inorganics utilizing one or more of the following direct physical or removal technologies:

1)  ion exchange;

2)  resin or solid (i.e., zeolites) adsorption;

3)  reverse osmosis;

4)  chelation or solvent extraction;

5)  freeze crystallization;

6)  ultrafiltration; or

7)  simple precipitation (i.e., crystallization)

Note:  this does not preclude the use of other physical phase separation or concentration techniques such as decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies.

RORGS  Recovery of organics utilizing one or more of the following technologies:

1)  Distillation;

2)  thin film evaporation;

3)  steam stripping;

4)  carbon adsorption;

5)  critical fluid extraction;

6)  liquid-liquid extraction;

7)  precipitation or crystallization (including freeze crystallization); or

8)  chemical phase separation techniques (i.e., addition of acids, bases, demulsifiers, or similar chemicals).

Note:  This does not preclude the use of other physical phase separation techniques such as decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies.

RTHRM  Thermal recovery of metals or inorganics from nonwastewaters in units defined as cement kilns, blast furnaces, smelting, melting and refining furnaces, combustion devices used to recover sulfur values from spent sulfuric acid and “other devices” determined by the Agency pursuant to 35 Ill. Adm. Code 720.110, the definition of “industrial furnace”.

RZINC  Resmelting in high temperature metal recovery units for the purpose of recovery of zinc.

STABL  Stabilization with the following reagents (or waste reagents) or combinations of reagents:

1)  Portland cement; or

2)  lime or pozzolans (e.g., fly ash and cement kiln dust)—this does not preclude the addition of reagents (e.g., iron salts, silicates, and clays) designed to enhance the set or cure time or compressive strength, or to overall reduce the leachability of the metal or inorganic.

SSTRP  Steam stripping of organics from liquid wastes utilizing direct application of steam to the wastes operated such that liquid and vapor flow rates, as well as temperature and pressure ranges, have been optimized, monitored, and maintained.  These operating parameters are dependent upon the design parameters of the unit, such as, the number of separation stages and the internal column design.  Thus resulting in a condensed extract high in organics that must undergo either incineration, reuse as a fuel, or other recovery or reuse and an extracted wastewater that must undergo further treatment as specified in the standard.

WETOX  Wet air oxidation performed in units operated such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., total organic carbon (TOC) can often be used as an indicator parameter for the oxidation of many organic constituents that cannot be directly analyzed in wastewater residues).

WTRRX  Controlled reaction with water for highly reactive inorganic or organic chemicals with precautionary controls for protection of workers from potential violent reactions as well as precautionary controls for potential emissions of toxic or ignitable levels of gases released during the reaction.

Note 1:  When a combination of these technologies (i.e., a treatment train) is specified as a single treatment standard, the order of application is specified in Table T by indicating the five letter technology code that must be applied first, then the designation “fb.” (an abbreviation for “followed by”), then the five letter technology code for the technology that must be applied next, and so on.

Note 2:  When more than one technology (or treatment train) are specified as alternative treatment standards, the five letter technology codes (or the treatment trains) are separated by a semicolon (;) with the last technology preceded by the word “OR”.  This indicates that any one of these BDAT technologies or treatment trains can be used for compliance with the standard.

BOARD NOTE: Derived from Table 1 in 40 CFR 268.42 (2017).

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.TABLE D Technology-Based Standards by USEPA Hazardous Waste Number

BOARD NOTE: For the requirements previously found in this Section, refer to Section 728.140 and Table T.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.TABLE E Standards for Radioactive Mixed Waste

BOARD NOTE: For the requirements previously found in this Section, refer to Section 728.140 and Table T.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.TABLE F Alternative Treatment Standards For Hazardous Debris

a)  Hazardous debris must be treated by either the standards indicated in this Table F or by the waste-specific treatment standards for the waste contaminating the debris. The treatment standards must be met for each type of debris contained in a mixture of debris types, unless the debris is converted into treatment residue as a result of the treatment process. Debris treatment residuals are subject to the waste-specific treatment standards for the waste contaminating the debris.

b)  Definitions. For the purposes of this Table F, the following terms are defined as follows:

“Clean debris surface” means the surface, when viewed without magnification, must be free of all visible contaminated soil and hazardous waste except that residual staining from soil and waste consisting of light shadows, slight streaks, or minor discolorations, and soil and waste in cracks, crevices, and pits may be present provided that such staining and waste and soil in cracks, crevices, and pits must be limited to no more than five percent of each square inch of surface area.

“Contaminant restriction” means that the technology is not BDAT for that contaminant. If debris containing a restricted contaminant is treated by the technology, the contaminant must be subsequently treated by a technology for which it is not restricted in order to be land disposed (and excluded from Subtitle C regulation).

“Dioxin-listed wastes” means wastes having any of USEPA hazardous waste numbers FO20, FO21, FO22, FO23, FO26, or FO27.

c)  Notes. In this Table F, the following text is to be read in conjunction with the tabulated text where the appropriate notations appear:

1 Acids, solvents, and chemical reagents may react with some debris and contaminants to form hazardous compounds. For example, acid washing of cyanide-contaminated debris could result in the formation of hydrogen cyanide. Some acids may also react violently with some debris and contaminants, depending on the concentration of the acid and the type of debris and contaminants. Debris treaters should refer to the safety precautions specified in Material Safety Data Sheets for various acids to avoid applying an incompatible acid to a particular debris/contaminant combination. For example, concentrated sulfuric acid may react violently with certain organic compounds, such as acrylonitrile.

2 If reducing the particle size of debris to meet the treatment standards results in material that no longer meets the 60 mm minimum particle size limit for debris, such material is subject to the waste-specific treatment standards for the waste contaminating the material, unless the debris has been cleaned and separated from contaminated soil and waste prior to size reduction. At a minimum, simple physical or mechanical means must be used to provide such cleaning and separation of nondebris materials to ensure that the debris surface is free of caked soil, waste, or other nondebris material.

3 Thermal desorption is distinguished from thermal destruction in that the primary purpose of thermal desorption is to volatilize contaminants and to remove them from the treatment chamber for subsequent destruction or other treatment.

4 The demonstration of “equivalent technology” pursuant to Section 728.142(b) must document that the technology treats contaminants subject to treatment to a level equivalent to that required by the performance and design and operating standards for other technologies in this table such that residual levels of hazardous contaminants will not pose a hazard to human health and the environment absent management controls.

5 Any soil, waste, and other nondebris material that remains on the debris surface (or remains mixed with the debris) after treatment is considered a treatment residual that must be separated from the debris using, at a minimum, simple physical or mechanical means. Examples of simple physical or mechanical means are vibratory or trommel screening or water washing. The debris surface need not be cleaned to a “clean debris surface” as defined in subsection (b) when separating treated debris from residue; rather, the surface must be free of caked soil, waste, or other nondebris material. Treatment residuals are subject to the waste-specific treatment standards for the waste contaminating the debris.

Technology Description Performance or Design and Operating Standard Contaminant Restrictions
A. Extraction Technologies    
1. Physical Extraction    
a. Abrasive Blasting: Removal of contaminated debris surface layers using water or air pressure to propel a solid media (e.g., steel shot, aluminum oxide grit, plastic beads). Glass, Metal, Plastic, Rubber: Treatment to a clean debris surface.
Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Removal of at least 0.6 cm of the surface layer; treatment to a clean debris surface.
All Debris: None.
b. Scarification, Grinding, and Planing: Process utilizing striking piston heads, saws, or rotating grinding wheels such that contaminated debris surface layers are removed. Same as above Same as above
c. Spalling: Drilling or chipping holes at appropriate locations and depth in the contaminated debris surface and applying a tool that exerts a force on the sides of those holes such that the surface layer is removed. The surface layer removed remains hazardous debris subject to the debris treatment standards. Same as above Same as above
d. Vibratory Finishing: Process utilizing scrubbing media, flushing fluid, and oscillating energy such that hazardous contaminants or contaminated debris surface layers are removed.1 Same as above Same as above
e. High Pressure Steam and Water Sprays: Application of water or steam sprays of sufficient temperature, pressure, residence time, agitation, surfactants, and detergents to remove hazardous contaminants from debris surfaces or to remove contaminated debris surface layers Same as above Same as above.
2. Chemical Extraction    
a. Water Washing and Spraying: Application of water sprays or water baths of sufficient temperature, pressure, residence time, agitation, surfactants, acids, bases, and detergents to remove hazardous contaminants from debris surfaces and surface pores or to remove contaminated debris surface layers. All Debris: Treatment to a clean debris surface; Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (½ inch) in one dimension (i.e., thickness limit,2 except that this thickness limit may be waived under an “Equivalent Technology” approval pursuant to Section 728.142(b);4 debris surfaces must be in contact with water solution for at least 15 minutes Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Contaminant must be soluble to at least five percent by weight in water solution or five percent by weight in emulsion; if debris is contaminated with a dioxin-listed waste,3 an “Equivalent Technology” approval pursuant to Section 728.142(b) must be obtained.4
b. Liquid Phase Solvent Extraction: Removal of hazardous contaminants from debris surfaces and surface pores by applying a nonaqueous liquid or liquid solution that causes the hazardous contaminants to enter the liquid phase and be flushed away from the debris along with the liquid or liquid solution while using appropriate agitation, temperature, and residence time.1 Same as above Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Same as above, except that contaminant must be soluble to at least five percent by weight in the solvent.
c. Vapor Phase Solvent Extraction: Application of an organic vapor using sufficient agitation, residence time, and temperature to cause hazardous contaminants on contaminated debris surfaces and surface pores to enter the vapor phase and be flushed away with the organic vapor.1 Same as above, except that brick, cloth, concrete, paper, pavement, rock and wood surfaces must be in contact with the organic vapor for at least 60 minutes. Same as above.
3. Thermal Extraction    
a. High Temperature Metals Recovery: Application of sufficient heat, residence time, mixing, fluxing agents, or carbon in a smelting, melting, or refining furnace to separate metals from debris. For refining furnaces, treated debris must be separated from treatment residuals using simple physical or mechanical means,5 and, prior to further treatment, such residuals must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris. Debris contaminated with a dioxin-listed waste:2 Obtain an “Equivalent Technology” approval pursuant to Section 728.142(b).4
b. Thermal Desorption: Heating in an enclosed chamber under either oxidizing or nonoxidizing atmospheres at sufficient temperature and residence time to vaporize hazardous contaminants from contaminated surfaces and surface pores and to remove the contaminants from the heating chamber in a gaseous exhaust gas.3 All Debris: Obtain an “Equivalent Technology” approval pursuant to Section 728.142(b);4 treated debris must be separated from treatment residuals using simple physical or mechanical means,5 and, prior to further treatment, such residue must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris.
Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 10 cm (4 inches) in one dimension (i.e., thickness limit),2 except that this thickness limit may be waived under the “Equivalent Technology” approval
All Debris: Metals other than mercury.
B. Destruction Technologies    
1. Biological Destruction (Biodegradation): Removal of hazardous contaminants from debris surfaces and surface pores in an aqueous solution and biodegradation of organic or nonmetallic inorganic compounds (i.e., inorganics that contain phosphorus, nitrogen, or sulfur) in units operated under either aerobic or anaerobic conditions. All Debris: Obtain an “Equivalent Technology” approval pursuant to Section 728.142(b);4 treated debris must be separated from treatment residuals using simple physical or mechanical means,5 and, prior to further treatment, such residue must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris.
Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (½ inch) in one dimension (i.e., thickness limit),2 except that this thickness limit may be waived under the “Equivalent Technology” approval
All Debris: Metal contaminants.
2. Chemical Destruction    
a. Chemical Oxidation: Chemical or electrolytic oxidation utilizing the following oxidation reagents (or waste reagents) or combination of reagents: (1) hypochlorite (e.g., bleach); (2) chlorine; (3) chlorine dioxide; (4) ozone or UV (ultraviolet light) assisted ozone; (5) peroxides; (6) persulfates; (7) perchlorates; (8) permanganates; or (9) other oxidizing reagents of equivalent destruction efficiency.1 Chemical oxidation specifically includes what is referred to as alkaline chlorination. All Debris: Obtain an “Equivalent Technology” approval pursuant to 35 Ill. Adm. Code.142(b);4 treated debris must be separated from treatment residuals using simple physical or mechanical means,5 and, prior to further treatment, such residue must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris.
Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (½ inch) in one dimension (i.e., thickness limit),2 except that this thickness limit may be waived under the “Equivalent Technology” approval
All Debris: Metal contaminants.
b. Chemical Reduction: Chemical reaction utilizing the following reducing reagents (or waste reagents) or combination of reagents: (1) sulfur dioxide; (2) sodium, potassium, or alkali salts of sulfites, bisulfites, and metabisulfites, and polyethylene glycols (e.g., NaPEG and KPEG); (3) sodium hydrosulfide; (4) ferrous salts; or (5) other reducing reagents of equivalent efficiency.1 Same as above Same as above.
3. Thermal Destruction: Treatment in an incinerator operating in accordance with Subpart O of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725; a boiler or industrial furnace operating in accordance with Subpart H of 35 Ill. Adm. Code 726, or other thermal treatment unit operated in accordance with Subpart X of 35 Ill. Adm. Code 724, or Subpart P of 35 Ill. Adm. Code 725, but excluding for purposes of these debris treatment standards Thermal Desorption units. Treated debris must be separated from treatment residuals using simple physical or mechanical means,5 and, prior to further treatment, such residue must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris. Brick, Concrete, Glass, Metal, Pavement, Rock, Metal: Metals other than mercury, except that there are no metal restrictions for vitrification.
Debris contaminated with a dioxin-listed waste.3 Obtain an “Equivalent Technology” approval pursuant to Section 728.142(b),4 except that this requirement does not apply to vitrification.
C. Immobilization Technologies    
1. Macroencapsulation: Application of surface coating materials such as polymeric organics (e.g., resins and plastics) or use of a jacket of inert inorganic materials to substantially reduce surface exposure to potential leaching media. Encapsulating material must completely encapsulate debris and be resistant to degradation by the debris and its contaminants and materials into which it may come into contact after placement (leachate, other waste, microbes). None.
2. Microencapsulation: Stabilization of the debris with the following reagents (or waste reagents) such that the leachability of the hazardous contaminants is reduced: (1) Portland cement; or (2) lime/ pozzolans (e.g., fly ash and cement kiln dust). Reagents (e.g., iron salts, silicates, and clays) may be added to enhance the set/cure time or compressive strength, or to reduce the leachability of the hazardous constituents.2 Leachability of the hazardous contaminants must be reduced. None.
3. Sealing: Application of an appropriate material that adheres tightly to the debris surface to avoid exposure of the surface to potential leaching media. When necessary to effectively seal the surface, sealing entails pretreatment of the debris surface to remove foreign matter and to clean and roughen the surface. Sealing materials include epoxy, silicone, and urethane compounds, but paint may not be used as a sealant Sealing must avoid exposure of the debris surface to potential leaching media and sealant must be resistant to degradation by the debris and its contaminants and materials into which it may come into contact after placement (leachate, other waste, microbes). None.

 
BOARD NOTE: Derived from Table 1 to 40 CFR 268.45 (2017).

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.TABLE G Alternative Treatment Standards Based on HTMR

For the treatment standards previously found in this Section and Section 728.146, refer to Section 728.140 and Table T, “Treatment Standards for Hazardous Wastes”.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.TABLE H Wastes Excluded from CCW Treatment Standards

The following facilities are excluded from the treatment standard under Section 728.143(a) and Table B, and are subject to the following constituent concentrations.  These facilities have received a treatability exception by regulatory action from USEPA pursuant to 40 CFR 268.44, and have demonstrated that the Board needs to adopt the treatability exception as part of the Illinois RCRA program.  The Board may also grant an “adjusted treatment standard” pursuant to Section 728.144.

Facility Name and Address USEPA HazardousWaste Number See Also Regulated Hazardous Constituent Wastewaters
Concentration (mg/ℓ)
Notes Nonwastewaters
Concentration (mg/kg)
Notes
Craftsman Plating and Tinning Corp., Chicago, IL F006 Section 728.140 Cyanides (Total) 1.2 B 1,800 D
      Cyanides (amenable) 0.86 B and C 30 D
      Cadmium 1.6   NA  
      Chromium 0.32   NA  
      Lead 0.40   NA  
      Nickel 0.44   NA  
Northwestern Plating Works, Inc., Chicago, IL F006 Section 728.140 Cyanides (Total) 1.2 B 970 D
      Cyanides (amenable) 0.86 B and C 30 D
      Cadmium 1.6   NA  
      Chromium 0.32   NA  
      Lead 0.40   NA  
      Nickel 0.44   NA  

Notes:

A  An owner or operator may certify compliance with these treatment standards according to the provisions of Section 728.107.

B  Cyanide wastewater standards for F006 are based on analysis of composite samples.

C  These owners and operators must comply with 0.86 mg/ℓ for amenable cyanides in the wastewater exiting the alkaline chlorination system.  These owners and operators must also comply with Section 728.107(a)(4) for appropriate monitoring frequency consistent with the facilities’ waste analysis plan.

D  Cyanide nonwastewaters are analyzed using Method 9010C (Total and Amenable Cyanide: Distillation) or 9012B (Total and Amenable Cyanide (Automated Colorimetric, with Off-Line Distillation)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(b), with a sample size 10 g, distillation time one hour and fifteen minutes.

NA  Not applicable.

BOARD NOTE: Derived from table to 40 CFR 268.44(o) (2017).

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.TABLE I Generator Paperwork Requirements

Subsection of Section 728.107 under Which the Paperwork is Required:
Required Information (a)(2) (a)(3) (a)(4) (a)(9)
1. USEPA hazardous waste numbers and manifest number of first shipment ü ü ü ü
2. Statement:  this waste is not prohibited from land disposal     ü  
3. The waste is subject to the LDRs.  The constituents of concern for USEPA hazardous waste numbers F001 through F005 and F039 waste, and underlying hazardous constituents in characteristic waste, unless the waste will be treated and monitored for all constituents.  If all constituents will be treated and monitored, there is no need to put them all on the LDR notice ü ü    
4. The notice must include the applicable wastewater/ nonwastewater category (see Section 728.102(d) and (f)) and subdivisions made within a USEPA hazardous waste number based on waste-specific criteria (such as D003 reactive cyanide) ü ü    
5. Waste analysis data (when available) ü ü ü  
6. Date the waste is subject to the prohibition     ü  
7. For hazardous debris, when treating with the alternative treatment technologies provided by Section 728.145:  the contaminants subject to treatment, as described in Section 728.145(b); and an indication that these contaminants are being treated to comply with Section 728.145 ü   ü  
8. For contaminated soil subject to LDRs as provided in Section 728.149(a), the constituents subject to treatment as described in Section 728.149(d), and the following statement:  This contaminated soil (does/does not) contain listed hazardous waste and (does/does not) exhibit a characteristic of hazardous waste and (is subject to/complies with) the soil treatment standards as provided by Section 728.149(c) or the universal treatment standards ü ü    
9. A certification is needed (see applicable subsection for exact wording)   ü   ü

 
BOARD NOTE: Derived from Table 1 to 40 CFR 268.7(a)(4) (2017).

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.TABLE T Treatment Standards for Hazardous Wastes

Note:  The treatment standards that formerly appeared in tables in Sections 728.141, 728.142, and 728.143 have been consolidated into this table.

USEPA Hazardous Waste Number
Waste Description and Treatment or Regulatory Subcategory1

Regulated Hazardous Constituent Wastewaters Nonwastewaters
Common Name CAS2 Number Concentration3 in mg/ℓ; or Technology Code4 Concentration5 in mg/kg 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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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

 
D0069
Radioactively contaminated cadmium-containing batteries.
(Note:  This subcategory consists of nonwastewaters only.)

Cadmium 7440-43-9 NA Macroencapsulation in accordance with Section 728.145

 
D0079
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for chromium based on Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a); 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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a); 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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a); 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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a); 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

 
D0099
Radioactively contaminated mercury-containing batteries.
(Note:  This subcategory consists of nonwastewaters only.)

Mercury 7439-97-6 NA Macroencapsulation in accordance with Section 728.145

 
D0109
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for selenium based on Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

Selenium 7782-49-2 0.82 and meet Section 728.148 standards8 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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

Silver 7440-22-4 0.43 0.14 mg/ℓ TCLP and meet Section 728.148 standards8

 
D0119
Radioactively contaminated silver-containing batteries.
(Note:  This subcategory consists of nonwastewaters only.)

Silver 7440-22-4 NA Macroencapsulation in accordance with Section 728.145

 
D0129
Wastes that are TC for endrin based on Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

a-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
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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

Methoxychlor 72-43-5 WETOX or CMBST 0.18 and meet Section 728.148 standards8

 
D0159
Wastes that are TC for toxaphene based on Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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 Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

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) 55684-94-1 0.000063 0.001
PeCDDs (All Pentachlorodibenzo-p-dioxins) 36088-22-9 0.000063 0.001
PeCDFs (All Pentachlorodibenzofurans) 30402-15-4 0.000035 0.001
Pentachlorophenol 87-86-5 0.089 7.4
TCDDs (All Tetrachlorodibenzo-p-dioxins) 41903-57-5 0.000063 0.001
TCDFs (All Tetrachlorodibenzofurans) 55722-27-5 0.000063 0.001
2,4,5-Trichlorophenol 95-95-4 0.18 7.4
2,4,6-Trichlorophenol 88-06-2 0.035 7.4
2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4

 
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) 55684-94-1 0.000063 0.001
PeCDDs (All Pentachlorodibenzo-p-dioxins) 36088-22-9 0.000063 0.001
PeCDFs (All Pentachlorodibenzofurans) 30402-15-4 0.000035 0.001
Pentachlorophenol 87-86-5 0.089 7.4
TCDDs (All Tetrachlorodibenzo-p-dioxins) 41903-57-5 0.000063 0.001
TCDFs (All Tetrachlorodibenzofurans) 55722-27-5 0.000063 0.001
2,4,5-Trichlorophenol 95-95-4 0.18 7.4
2,4,6-Trichlorophenol 88-06-2 0.035 7.4
2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4

 
F028
Residues resulting from the incineration or thermal treatment of soil contaminated with USEPA hazardous waste numbers F020, F021, F023, F026, and F027.

HxCDDs (All Hexachlorodibenzo-p-dioxins) NA 0.000063 0.001
HxCDFs (All Hexachlorodibenzofurans) 55684-94-1 0.000063 0.001
PeCDDs (All Pentachlorodibenzo-p-dioxins) 36088-22-9 0.000063 0.001
PeCDFs (All Pentachlorodibenzofurans) 30402-15-4 0.000035 0.001
Pentachlorophenol 87-86-5 0.089 7.4
TCDDs (All Tetrachlorodibenzo-p-dioxins) 41903-57-5 0.000063 0.001
TCDFs (All Tetrachlorodibenzofurans) 55722-27-5 0.000063 0.001
2,4,5-Trichlorophenol 95-95-4 0.18 7.4
2,4,6-Trichlorophenol 88-06-2 0.035 7.4
2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4

 
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 USEPA hazardous waste number 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.  (Leachate resulting from the disposal of one or more of the following USEPA hazardous wastes and no other hazardous wastes retains its USEPA hazardous waste numbers:  F020, F021, F022, F026, F027, or F028.).

Acenaphthylene 208-96-8 0.059 3.4
Acenaphthene 83-32-9 0.059 3.4
Acetone 67-64-1 0.28 160
Acetonitrile 75-05-8 5.6 NA
Acetophenone 96-86-2 0.010 9.7
2-Acetylaminofluorene 53-96-3 0.059 140
Acrolein 107-02-8 0.29 NA
Acrylonitrile 107-13-1 0.24 84
Aldrin 309-00-2 0.021 0.066
4-Aminobiphenyl 92-67-1 0.13 NA
Aniline 62-53-3 0.81 14
o-Anisidine (2-methoxyaniline) 90-04-0 0.010 0.66
Anthracene 120-12-7 0.059 3.4
Aramite 140-57-8 0.36 NA
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
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
p-Cresidine 120-71-8 0.010 0.66
o-Cresol 95-48-7 0.11 5.6
m-Cresol
(difficult to distinguish from p-cresol)
108-39-4 0.77 5.6
p-Cresol
(difficult to distinguish from m-cresol)
106-44-5 0.77 5.6
Cyclohexanone 108-94-1 0.36 NA
1,2-Dibromo-3-chloropropane 96-12-8 0.11 15
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
2,4-Dimethylaniline (2,4-xylidine) 95-68-1 0.010 0.66
Diethyl phthalate 84-66-2 0.20 28
2-4-Dimethyl phenol 105-67-9 0.036 14
Dimethyl phthalate 131-11-3 0.047 28
Di-n-butyl phthalate 84-74-2 0.057 28
1,4-Dinitrobenzene 100-25-4 0.32 2.3
4,6-Dinitro-o-cresol 534-52-1 0.28 160
2,4-Dinitrophenol 51-28-5 0.12 160
2,4-Dinitrotoluene 121-14-2 0.32 140
2,6-Dinitrotoluene 606-20-2 0.55 28
Di-n-octyl phthalate 117-84-0 0.017 28
Di-n-propylnitrosamine 621-64-7 0.40 14
1,4-Dioxane 123-91-1 12.0 170
Diphenylamine (difficult to distinguish from 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) 55684-94-1 0.000063 0.001
Hexachloroethane 67-72-1 0.055 30
Hexachloropropylene 1888-71-7 0.035 30
Indeno (1,2,3-c,d) pyrene 193-39-5 0.0055 3.4
Iodomethane 74-88-4 0.19 65
Isobutyl alcohol 78-83-1 5.6 170
Isodrin 465-73-6 0.021 0.066
Isosafrole 120-58-1 0.081 2.6
Kepone 143-50-8 0.0011 0.13
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
1,2,3,4,6,7,8,9-Octachlorodibenzofuran (OCDF) 39001-02-0 0.000063 0.005
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) 36088-22-9 0.000063 0.001
PeCDFs (All Pentachlorodibenzofurans) 30402-15-4 0.000035 0.001
Pentachloronitrobenzene 82-68-8 0.055 4.8
Pentachlorophenol 87-86-5 0.089 7.4
Phenacetin 62-44-2 0.081 16
Phenanthrene 85-01-8 0.059 5.6
Phenol 108-95-2 0.039 6.2
1,3-Phenylenediamine 108-45-2 0.010 0.66
Phorate 298-02-2 0.021 4.6
Phthalic anhydride 85-44-9 0.055 NA
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) 41903-57-5 0.000063 0.001
TCDFs (All Tetrachlorodibenzofurans) 55722-27-5 0.000063 0.001
1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0
1,1,2,2-Tetrachloroethane 79-34-6 0.057 6.0
Tetrachloroethylene 127-18-4 0.056 6.0
2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4
Toluene 108-88-3 0.080 10
Toxaphene 8001-35-2 0.0095 2.6
Bromoform (Tribromomethane) 75-25-2 0.63 15
1,2,4-Trichlorobenzene 120-82-1 0.055 19
1,1,1-Trichloroethane 71-55-6 0.054 6.0
1,1,2-Trichloroethane 79-00-5 0.054 6.0
Trichloroethylene 79-01-6 0.054 6.0
Trichloromonofluoromethane 75-69-4 0.020 30
2,4,5-Trichlorophenol 95-95-4 0.18 7.4
2,4,6-Trichlorophenol 88-06-2 0.035 7.4
1,2,3-Trichloropropane 96-18-4 0.85 30
1,1,2-Trichloro-1,2,2-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 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 distillation 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) 55684-94-1 0.000063 0.001
PeCDDs (All Pentachlorodibenzo-p-dioxins) 36088-22-9 0.000063 0.001
PeCDFs (All Pentachlorodibenzofurans) 30402-15-4 0.000035 0.001
TCDDs (All Tetrachlorodibenzo-p-dioxins) 41903-57-5 0.000063 0.001
TCDFs (All Tetrachlorodibenzofurans) 55722-27-5 0.000063 0.001

 
K044
Wastewater treatment sludges from the manufacturing and processing of explosives.

NA NA DEACT DEACT

 
K045
Spent carbon from the treatment of wastewater containing explosives.

NA NA DEACT DEACT

 
K046
Wastewater treatment sludges from the manufacturing, formulation and loading of lead-based initiating compounds.

Lead 7439-92-1 0.69 0.75 mg/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 218-01-9 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 218-01-9 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-cd)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) 55684-94-1 0.000063 0.001
PeCDDs (All Pentachlorodibenzo-p-dioxins) 36088-22-9 0.000063 0.001
PeCDFs (All Pentachlorodibenzofurans) 30402-15-4 0.000035 0.001
TCDDs (All Tetrachlorodibenzo-p-dioxins) 41903-57-5 0.000063 0.001
TCDFs (All Tetrachlorodibenzofurans) 55722-27-5 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 121-14-2 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.

Acetonitrile 75-05-8 5.6 1.8
Acetophenone 98-86-2 0.010 9.7
Aniline 62-53-3 0.81 14
Benomyl10 17804-35-2 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Benzene 71-43-2 0.14 10
Carbaryl10 63-25-2 0.006; or CMBST, CHOXD, BIODG or CARBN 0.14; or CMBST
Carbenzadim10 10605-21-7 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Carbofuran10 1563-66-2 0.006; or CMBST, CHOXD, BIODG or CARBN 0.14; or CMBST
Carbosulfan10 55285-14-8 0.028; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
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
Methomyl10 16752-77-5 0.028; or CMBST, CHOXD, BIODG or CARBN 0.14; or CMBST
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; or CMBST, CHOXD, BIODG or CARBN 1.5; or CMBST

 
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
Methomyl10 16752-77-5 0.028; or CMBST, CHOXD, BIODG or CARBN 0.14; or CMBST
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; or CMBST, CHOXD, BIODG or CARBN 1.5; or CMBST

 
K158
Baghouse dusts and filter/separation solids from the production of carbamates and carbamoyl oximes.

Benomyl10 17804-35-2 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBSTP
Benzene 71-43-2 0.14 10
Carbenzadim10 10605-21-7 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Carbofuran10 1563-66-2 0.006; or CMBST, CHOXD, BIODG or CARBN 0.14; or CMBST
Carbosulfan10 55285-14-8 0.028; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
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
Butylate10 2008-41-5 0.042; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
EPTC (Eptam)10 759-94-4 0.042; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Molinate10 2212-67-1 0.042; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Pebulate10 1114-71-2 0.042; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Vernolate10 1929-77-7 0.042; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
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)10 137-30-4 0.028; or CMBST, CHOXD, BIODG or CARBN 28; or CMBST
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 7439-97-6 NA 0.025 mg/ℓ TCLP
PH12   NA pH £ 6.0

 
K175
All K175 wastewaters.

Mercury 7439-97-6 0.15 NA

 
K176
Baghouse filters from the production of antimony oxide, including filters from the production of intermediates e.g., antimony metal or crude antimony oxide).

Antimony 7440-36-0 1.9 1.15 mg/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

 
K181
Nonwastewaters from the production of dyes or pigments (including nonwastewaters commingled at the point of generation with nonwastewaters from other processes) that, at the point of generation, contain mass loadings of any of the constituents identified in Section 721.132(c) which are equal to or greater than the corresponding Section 721.132(c) levels, as determined on a calendar-year basis.

Aniline 62-53-3 0.81 14
o-Anisidine (2-methoxyaniline) 90-04-0 0.010 0.66
4-Chloroaniline 106-47-8 0.46 16
p-Cresidine 120-71-8 0.010 0.66
2,4-Dimethylaniline (2,4-xylidine) 95-68-1 0.010 0.66
1,2-Phenylenediamine 95-54-5 CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN
1,3-Phenylenediamine 108-45-2 0.010 0.66

 
P001
Warfarin, & salts, when present at concentrations greater than 0.3 percent.

Warfarin 81-81-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST

 
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) 16984-48-8 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.10

Carbofuran 1563-66-2 0.006; or CMBST, CHOXD, BIODG or CARBN 0.14; or CMBST

 
P128
Mexacarbate.10

Mexacarbate 315-18-4 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
P185
Tirpate.10

Tirpate 26419-73-8 0.056; or CMBST, CHOXD, BIODG or CARBN 0.28; or CMBST

 
P188
Physostigimine salicylate.10

Physostigmine salicylate 57-64-7 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
P189
Carbosulfan.10

Carbosulfan 55285-14-8 0.028; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
P190
Metolcarb.10

Metolcarb 1129-41-5 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
P191
Dimetilan.10

Dimetilan 644-64-4 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
P192
Isolan.10

Isolan 119-38-0 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
P194
Oxamyl.10

Oxamyl 23135-22-0 0.056; or CMBST, CHOXD, BIODG or CARBN 0.28; or CMBST

 
P196
Manganese dimethyldithiocarbamates (total).10

Dithiocarbamates (total) NA 0.028; or CMBST, CHOXD, BIODG or CARBN 28; or CMBST

 
P197
Formparanate.10

Formparanate 17702-57-7 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
P198
Formetanate hydrochloride.10

Formetanate hydrochloride 23422-53-9 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
P199
Methiocarb.10

Methiocarb 2032-65-7 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
P201
Promecarb.10

Promecarb 2631-37-0 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
P202
m-Cumenyl methylcarbamate.10

m-Cumenyl methylcarbamate 64-00-6 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
P203
Aldicarb sulfone.10

Aldicarb sulfone 1646-88-4 0.056; or CMBST, CHOXD, BIODG or CARBN 0.28; or CMBST

 
P204
Physostigmine.10

Physostigmine 57-47-6 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
P205
Ziram.10

Dithiocarbamates (total) NA 0.028; or CMBST, CHOXD, BIODG or CARBN 28; or CMBST

 
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
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) 7664-39-3 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-cd)pyrene.

Indeno(1,2,3-cd)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
Elemental Mercury Contaminated with Radioactive Materials.

Mercury 7439-97-6 NA AMLGM

 
U152
Methacrylonitrile.

Methacrylonitrile 126-98-7 0.24 84

 
U153
Methanethiol.

Methanethiol 74-93-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST

 
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

 
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.10

Benomyl 17804-35-2 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
U278
Bendiocarb.10

Bendiocarb 22781-23-3 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
U279
Carbaryl.10

Carbaryl 63-25-2 0.006; or CMBST, CHOXD, BIODG or CARBN 0.14; or CMBST

 
U280
Barban.10

Barban 101-27-9 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
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 phenol.10

Bendiocarb phenol 22961-82-6 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
U367
Carbofuran phenol.10

Carbofuran phenol 1563-38-8 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
U372
Carbendazim.10

Carbendazim 10605-21-7 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
U373
Propham.10

Propham 122-42-9 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
U387
Prosulfocarb.10

Prosulfocarb 52888-80-9 0.042; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
U389
Triallate.10

Triallate 2303-17-5 0.042; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
U394
A2213.10

A2213 30558-43-1 0.042; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 

U395
Diethylene glycol, dicarbamate.10

Diethylene glycol, dicarbamate 5952-26-1 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
U404
Triethylamine.10

Triethylamine 121-44-8 0.081; or CMBST, CHOXD, BIODG or CARBN 1.5; or CMBST

 
U409
Thiophanate-methyl.10

Thiophanate-methyl 23564-05-8 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
U410
Thiodicarb.10

Thiodicarb 59669-26-0 0.019; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
U411
Propoxur.10

Propoxur 114-26-1 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST

 
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 USEPA hazardous waste number 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, “Technology Codes and Descriptions of Technology-Based Standards”.  “fb” inserted between USEPA hazardous waste numbers denotes “followed by”, so that the first-listed treatment is followed by the second-listed treatment.  A semicolon (;) separates alternative treatment schemes.

5  Except for Metals (EP or TCLP) and Cyanides (Total and Amenable), the nonwastewater treatment standards expressed as a concentration were established, in part, based on incineration in units operated in accordance with the technical requirements of Subpart O of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725 or based on combustion in fuel substitution units operating in accordance with applicable technical requirements.  A facility may comply with these treatment standards according to provisions in Section 728.140(d).  All concentration standards for nonwastewaters are based on analysis of grab samples.

6  Where an alternate treatment standard or set of alternate standards has been indicated, a facility may comply with this alternate standard, but only for the Treatment or Regulatory Subcategory or physical form (i.e., wastewater or nonwastewater) specified for that alternate standard.

7  Both Cyanides (Total) and Cyanides (Amenable) for nonwastewaters are to be analyzed using Method 9010C or 9012B, in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a), with a sample size of 10 grams and a distillation time of one hour and 15 minutes.

8  These wastes, when rendered non-hazardous and then subsequently managed in CWA or CWA-equivalent systems, are not subject to treatment standards.  (See Section 728.101(c)(3) and (c)(4).)

9  These wastes, when rendered non-hazardous and then subsequently injected in a Class I SDWA well, are not subject to treatment standards.  (See 35 Ill. Adm. Code 738.101(d).)

10  The treatment standard for this waste may be satisfied by either meeting the constituent concentrations in the table in this Section or by treating the waste by the specified technologies: combustion, as defined by the technology code CMBST at Table C for nonwastewaters; and biodegradation, as defined by the technology code BIODG; carbon adsorption, as defined by the technology code CARBN; chemical oxidation, as defined by the technology code CHOXD; or combustion, as defined as technology code CMBST, at Table C, for wastewaters.

11  For these wastes, the definition of CMBST is limited to any of the following that have obtained a determination of equivalent treatment under Section 728.142(b):  (1) combustion units operating under 35 Ill. Adm. Code 726, (2) combustion units permitted under Subpart O of 35 Ill. Adm. Code 724, or (3) combustion units operating under Subpart O of 35 Ill. Adm. Code 725.

12  Disposal of USEPA hazardous waste number K175 waste that has complied with all applicable Section 728.140 treatment standards must also be macroencapsulated in accordance with Table F, unless the waste is placed in either of the following types of facilities:

a)  A RCRA Subtitle C monofill containing only K175 wastes that meet all applicable 40 CFR 268.40 treatment standards; or

b)  A dedicated RCRA Subtitle C landfill cell in which all other wastes being co-disposed are at pH≤6.0.

BOARD NOTE:  Derived from table to 40 CFR 268.40 (2017).

NA  means not applicable.

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)


Section 728.TABLE U Universal Treatment Standards (UTS)

Regulated Constituent-Common Name CAS1 No. Wastewater Standard Concentration2 (in mg/ℓ) Nonwastewater Standard Concentration3 (in mg/kg 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
Aldrin 309-00-2 0.021 0.066
4-Aminobiphenyl 92-67-1 0.13 NA
Aniline 62-53-3 0.81 14
o-Anisidine (2-methoxyaniline) 90-04-0 0.010 0.66
Anthracene 120-12-7 0.059 3.4
Aramite 140-57-8 0.36 NA
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
g-BHC 58-89-9 0.0017 0.066
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
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 4.8 mg/ℓ TCLP
Carbon tetrachloride 56-23-5 0.057 6.0
Chlordane ( a and 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
p-Cresidine 120-71-8 0.010 0.66
o-Cresol 95-48-7 0.11 5.6
m-Cresol (difficult to distinguish from p-cresol) 108-39-4 0.77 5.6
p-Cresol (difficult to distinguish from m-cresol) 106-44-5 0.77 5.6
Cyclohexanone 108-94-1 0.36 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-Dimethylaniline (2,4-xylidine) 95-68-1 0.010 0.66
2,4-Dimethyl phenol 105-67-9 0.036 14
Dimethyl phthalate 131-11-3 0.047 28
Di-n-butyl phthalate 84-74-2 0.057 28
1,4-Dinitrobenzene 100-25-4 0.32 2.3
4,6-Dinitro-o-cresol 534-52-1 0.28 160
2,4-Dinitrophenol 51-28-5 0.12 160
2,4-Dinitrotoluene 121-14-2 0.32 140
2,6-Dinitrotoluene 606-20-2 0.55 28
Di-n-octyl phthalate 117-84-0 0.017 28
Di-n-propylnitrosamine 621-64-7 0.40 14
1,4-Dioxane 123-91-1 12.0 170
Diphenylamine (difficult to distinguish from diphenylnitrosamine) 122-39-4 0.92 13
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
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
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
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) 55684-94-1 0.000063 0.001
Hexachloroethane 67-72-1 0.055 30
Hexachloropropylene 1888-71-7 0.035 30
Indeno (1,2,3-c,d) pyrene 193-39-5 0.0055 3.4
Iodomethane 74-88-4 0.19 65
Isobutyl alcohol 78-83-1 5.6 170
Isodrin 465-73-6 0.021 0.066
Isosafrole 120-58-1 0.081 2.6
Kepone 143-50-0 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
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
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
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
Pentachlorobenzene 608-93-5 0.055 10
PeCDDs (All Pentachlorodibenzo-p-dioxins) 36088-22-9 0.000063 0.001
PeCDFs (All Pentachlorodibenzofurans) 30402-15-4 0.000035 0.001
Pentachloroethane 76-01-7 0.055 6.0
Pentachloronitrobenzene 82-68-8 0.055 4.8
Pentachlorophenol 87-86-5 0.089 7.4
Phenacetin 62-44-2 0.081 16
Phenanthrene 85-01-8 0.059 5.6
Phenol 108-95-2 0.039 6.2
1,3-Phenylenediamine 108-45-2 0.010 0.66
Phorate 298-02-2 0.021 4.6
Phthalic acid 100-21-0 0.055 28
Phthalic anhydride 85-44-9 0.055 28
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
1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14
TCDDs (All Tetrachlorodibenzo-p-dioxins) 41903-57-5 0.000063 0.001
TCDFs (All Tetrachlorodibenzofurans) 55722-27-5 0.000063 0.001
1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0
1,1,2,2-Tetrachloroethane 79-34-5 0.057 6.0
Tetrachloroethylene 127-18-4 0.056 6.0
2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4
Toluene 108-88-3 0.080 10
Toxaphene 8001-35-2 0.0095 2.6
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
tris-(2,3-Dibromopropyl) phosphate 126-72-7 0.11 0.10
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 USEPA hazardous waste number 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 Subpart O of 35 Ill. Adm. Code 724 or Subpart O of 35 Ill. Adm. Code 725 or on combustion in fuel substitution units operating in accordance with applicable technical requirements.  A facility may comply with these treatment standards according to provisions in Section 728.140(d).  All concentration standards for nonwastewaters are based on analysis of grab samples.

4  Both Cyanides (Total) and Cyanides (Amenable) for nonwastewaters are to be analyzed using Method 9010C or 9012B, in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a), 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 USEPA has removed and marked “reserved”.  This statement maintains structural consistency with the corresponding federal regulations.

7  This constituent is not an underlying hazardous constituent, as defined at Section 728.102(i), because its UTS level is greater than its TC level. Thus, a treated selenium waste would always be characteristically hazardous unless it is treated to below its characteristic level.

8  This standard is temporarily deferred for soil exhibiting a hazardous characteristic due to USEPA hazardous waste numbers D004 through D011 only.

Note:  NA means not applicable.

BOARD NOTE:  Derived from table to 40 CFR 268.48(a) (2017).

(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)

Back to top