TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARDSUBCHAPTER 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, 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728.108 Landfill and Surface Impoundment Disposal Restrictions (Repealed)728.109 Special Rules for Characteristic Wastes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728.110 First Third (Repealed)
728.111 Second Third (Repealed)
728.112 Third Third (Repealed)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 Wastes728.114 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 Wastes728.139 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 Standards728.149 Alternative LDR Treatment Standards for Contaminated Soil
SUBPART E: PROHIBITIONS ON STORAGE
Section728.150 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 Wastes728.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.
SUBPART A: GENERAL
Section 728.101 Purpose, Scope, and Applicability
a) This Part identifies hazardous wastes that are restricted from land disposal and defines those limited circumstances under which an otherwise prohibited waste may continue to be land disposed.
b) Except as specifically provided otherwise in this Part or 35 Ill. Adm. Code 721, the requirements of this Part apply to persons that generate or transport hazardous waste and to owners and operators of hazardous waste treatment, storage, and disposal facilities.
c) Restricted wastes may continue to be land disposed as follows:
1) Where a person has been granted an extension to the effective date of a prohibition pursuant to Subpart C or pursuant to Section 728.105, with respect to those wastes covered by the extension;
2) Where a person has been granted an exemption from a prohibition pursuant to a petition pursuant to 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 which is otherwise prohibited pursuant to 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 which is otherwise prohibited pursuant to 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 pursuant to a permit issued pursuant to 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 pursuant to 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 pursuant to 35 Ill. Adm. Code 722.170;
3) Waste identified or listed as hazardous after November 8, 1984, for which USEPA has not promulgated a land disposal prohibition or treatment standard; 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 pursuant to 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; and
4) Lamps, as described in 35 Ill. Adm. Code 733.105.
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 pursuant to 35 Ill. Adm. Code 709 or Section 22.6 or 39(h) of the Environmental Protection 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 pursuant to 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) (2017).
(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)
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, Treaters, and Disposal Facilities
a) Requirements for Generators
1) A generator of a hazardous waste must determine if the waste has to be treated before it can be land disposed. This is done by determining if the hazardous waste meets the treatment standards in Section 728.140, 728.145, or 728.149. This determination can be made 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, where 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 pursuant to 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 which is exempt from Subtitle C regulation under 35 Ill. Adm. Code 721.102 through 721.106 subsequent to the point of generation (including deactivated characteristic hazardous wastes that are managed in wastewater treatment systems subject to the CWA, as specified at 35 Ill. Adm. Code 721.104(a)(2); that are CWA-equivalent; or that are managed in an underground injection well regulated under 35 Ill. Adm. Code 730), the generator must place a one-time notice stating such generation, subsequent exclusion from the definition of hazardous or solid waste or exemption from RCRA Subtitle C regulation, and the disposition of the waste in the generating facility’s on-site file.
8) A generator must retain a copy of all notices, certifications, waste analysis data, and other documentation produced pursuant to this Section on-site for at least three years from the date that the waste that is the subject of such documentation was last sent to on-site or off-site treatment, storage, or disposal. The three-year record retention period is automatically extended during the course of any unresolved enforcement action regarding the regulated activity or as requested 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 pursuant to 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 pursuant to 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 pursuant to 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 which contain underlying hazardous constituents, as defined in Section 728.102(i); if these wastes are treated on-site to remove the hazardous characteristic; and that are then sent off-site for treatment of underlying hazardous constituents, the certification must state as follows:
I certify under penalty of law that the waste has been treated in accordance with the requirements of 35 Ill. Adm. Code 728.140 and Table T of Section 728.149 of that Part to remove the hazardous characteristic. This decharacterized waste contains underlying hazardous constituents that require further treatment to meet treatment standards. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.
E) For characteristic wastes that contain underlying hazardous constituents, as defined in Section 728.102(i), that are treated on-site to remove the hazardous characteristic and to treat underlying hazardous constituents to levels in Section 728.148 and Table U universal treatment standards, the certification must state as follows:
I certify under penalty of law that the waste has been treated in accordance with the requirements of 35 Ill. Adm. Code 728.140 and Table T of that Part to remove the hazardous characteristic and that underlying hazardous constituents, as defined in 35 Ill. Adm. Code 728.102(i), have been treated on-site to meet the universal treatment standards of 35 Ill. Adm. Code 728.148 and Table U of that Part. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.
5) If the waste or treatment residue will be further managed at a different treatment, storage, or disposal facility, the treatment, storage, or disposal facility that sends the waste or treatment residue off-site must comply with the notice and certification requirements applicable to generators under this Section.
6) Where the wastes are recyclable materials used in a manner constituting disposal subject to the provisions of 35 Ill. Adm. Code 726.120(b), regarding treatment standards and prohibition levels, the owner or operator of a treatment facility (i.e., the recycler) 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 where the owner or operator is disposing of any waste that is a recyclable material used in a manner constituting disposal pursuant to 35 Ill. Adm. Code 726.120(b), the owner or operator of any land disposal facility disposing any waste subject to restrictions under this Part 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) Where the owner or operator is disposing of any waste that is subject to the prohibitions under Section 728.133(f) but not subject to the prohibitions set forth in Section 728.132, the owner or operator must ensure that such waste is the subject of a certification according to the requirements of Section 728.108 prior to disposal in a landfill or surface impoundment unit, and that such disposal is in accordance with the requirements of Section 728.105(h)(2). The same requirement applies to any waste that is subject to the prohibitions under Section 728.133(f) and also is subject to the statutory prohibitions in the codified prohibitions in Section 728.139 or Section 728.132.
4) Where the owner or operator is disposing of any waste that is a recyclable material used in a manner constituting disposal subject to the provisions of 35 Ill. Adm. Code 726.120(b), the owner or operator is not subject to subsections (c)(1) through (c)(3) 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 42 Ill. Reg. 24924, effective November 19, 2018)
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 STANDARDSSection 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:
* 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.
If the LDRs And if the LDRs And if Then the owner or operatorApplied 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. 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 which must store hazardous wastes for longer than 90 days due to the regulations under this Part becomes an owner or operator of a storage facility and must obtain a RCRA permit, as required by 35 Ill. Adm. Code 703. Such a facility may qualify for interim status upon compliance with the regulations governing interim status under 35 Ill. Adm. Code 703.153.)
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.
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 pursuant to 40 CFR 268.5, an approved Section 728.106 petition or a national capacity variance granted by USEPA pursuant to 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, where treatment standards have not been specified, the waste is in compliance with the applicable prohibitions specified in Section 728.132 or 728.139.
f) Liquid hazardous wastes containing PCBs at concentrations greater than or equal to 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 pursuant to 35 Ill. Adm. Code 724.654.
(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)
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.
Note: “n.a.” stands for “not applicable”.
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
BIODGn.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
BIODGD001 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
INCINn.a. D001 Ignitable Oxidizers based on 35 Ill. Adm. Code 721.121(a)(4) CHRED
INCINCHRED
INCIND002 Acid Subcategory based on 35 Ill. Adm. Code 721.122(a)(1) with pH less than or equal to two RCORR
NEUTR
INCINNEUTR
INCIND002 Alkaline Subcategory based on 35 Ill. Adm. Code 721.122(a)(1) with pH greater than or equal to 12.5 NEUTR
INCINNEUTR
INCIND002 Other Corrosives based on 35 Ill. Adm. Code 721.122(a)(2) CHOXD
CHRED
INCIN
STABLCHOXD
CHRED
INCIND003 Water Reactives based on 35 Ill. Adm. Code 721.123(a)(2), (a)(3), and (a)(4) INCIN
WTRRX
CHOXD
CHREDn.a. D003 Reactive Sulfides based on 35 Ill. Adm. Code 721.123(a)(5) CHOXD
CHRED
INCIN
STABLCHOXD
CHRED
BIODG
INCIND003 Explosives based on 35 Ill. Adm. Code 721.123(a)(6), (a)(7), and (a)(8) INCIN
CHOXD
CHREDINCIN
CHOXD
CHRED
BIODG
CARBND003 Other Reactives based on 35 Ill. Adm. Code 721.123(a)(1) INCIN
CHOXD
CHREDINCIN
CHOXD
CHRED
BIODG
CARBNK044 Wastewater treatment sludges from the manufacturing and processing of explosives CHOXD
CHRED
INCINCHOXD
CHRED
BIODG
CARBN
INCINK045 Spent carbon from the treatment of wastewaters containing explosives CHOXD
CHRED
INCINCHOXD
CHRED
BIODG
CARBN
INCINK047 Pink/red water from TNT operations CHOXD
CHRED
INCINCHOXD
CHRED
BIODG
CARBN
INCIN“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
a This table also does not include contaminated soil and debris wastes.
Waste code Waste category Effective dateD001c All (except High TOC Ignitable Liquids) August 9, 1993D001 High TOC Ignitable Liquids August 8, 1990D002c All August 9, 1993D003e Newly identified surface-disposed elemental phosphorus processing wastes May 26, 2000D004 Newly identified D004 and mineral processing wastes August 24, 1998D004 Mixed radioactive/newly identified D004 or mineral processing wastes May 26, 2000D005 Newly identified D005 and mineral processing wastes August 24, 1998D005 Mixed radioactive/newly identified D005 or mineral processing wastes May 26, 2000D006 Newly identified D006 and mineral processing wastes August 24, 1998D006 Mixed radioactive/newly identified D006 or mineral processing wastes May 26, 2000D007 Newly identified D007 and mineral processing wastes August 24, 1998D007 Mixed radioactive/newly identified D007or mineral processing wastes May 26, 2000D008 Newly identified D008 and mineral processing waste August 24, 1998D008 Mixed radioactive/newly identified D008 or mineral processing wastes May 26, 2000D009 Newly identified D009 and mineral processing waste August 24, 1998D009 Mixed radioactive/newly identified D009or mineral processing wastes May 26, 2000D010 Newly identified D010 and mineral processing wastes August 24, 1998D010 Mixed radioactive/newly identified D010 or mineral processing wastes May 26, 2000D011 Newly identified D011 and mineral processing wastes August 24, 1998D011 Mixed radioactive/newly identified D011or mineral processing wastes May 26, 2000D012 (that exhibit the toxicity characteristic based on the TCLP)d All December 14, 1994D013 (that exhibit the toxicity characteristic based on the TCLP)d All December 14, 1994D014 (that exhibit the toxicity characteristic based on the TCLP)d All December 14, 1994D015 (that exhibit the toxicity characteristic based on the TCLP)d All December 14, 1994D016 (that exhibit the toxicity characteristic based on the TCLP)d All December 14, 1994D017 (that exhibit the toxicity characteristic based on the TCLP)d All December 14, 1994D018 Mixed with radioactive wastes September 19, 1996D018 All others December 19, 1994D019 Mixed with radioactive wastes September 19, 1996D019 All others December 19, 1994D020 Mixed with radioactive wastes September 19, 1996D020 All others December 19, 1994D021 Mixed with radioactive wastes September 19, 1996D021 All others December 19, 1994D022 Mixed with radioactive wastes September 19, 1996D022 All others December 19, 1994D023 Mixed with radioactive wastes September 19, 1996D023 All others December 19, 1994D024 Mixed with radioactive wastes September 19, 1996D024 All others December 19, 1994D025 Mixed with radioactive wastes September 19, 1996D025 All others December 19, 1994D026 Mixed with radioactive wastes September 19, 1996D026 All others December 19, 1994D027 Mixed with radioactive wastes September 19, 1996D027 All others December 19, 1994D028 Mixed with radioactive wastes September 19, 1996D028 All others December 19, 1994D029 Mixed with radioactive wastes September 19, 1996D029 All others December 19, 1994D030 Mixed with radioactive wastes September 19, 1996D030 All others December 19, 1994D031 Mixed with radioactive wastes September 19, 1996D031 All others December 19, 1994D032 Mixed with radioactive wastes September 19, 1996D032 All others December 19, 1994D033 Mixed with radioactive wastes September 19, 1996D033 All others December 19, 1994D034 Mixed with radioactive wastes September 19, 1996D034 All others December 19, 1994D035 Mixed with radioactive wastes September 19, 1996D035 All others December 19, 1994D036 Mixed with radioactive wastes September 19, 1996D036 All others December 19, 1994D037 Mixed with radioactive wastes September 19, 1996D037 All others December 19, 1994D038 Mixed with radioactive wastes September 19, 1996D038 All others December 19, 1994D039 Mixed with radioactive wastes September 19, 1996D039 All others December 19, 1994D040 Mixed with radioactive wastes September 19, 1996D040 All others December 19, 1994D041 Mixed with radioactive wastes September 19, 1996D041 All others December 19, 1994D042 Mixed with radioactive wastes September 19, 1996D042 All others December 19, 1994D043 Mixed with radioactive wastes September 19, 1996D043 All others December 19, 1994F001 Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids November 8, 1988F001 All others November 8, 1986F002 (1,1,2-trichloroethane) Wastewater and Nonwastewater August 8, 1990F002 Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids November 8, 1988F002 All others November 8, 1986F003 Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids November 8, 1988F003 All others November 8, 1986F004 Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids November 8, 1988F004 All others November 8, 1986F005 (benzene, 2-ethoxy ethanol, 2-nitropropane) Wastewater and Nonwastewater August 8, 1990F005 Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids November 8, 1988F005 All others November 8, 1986F006 Wastewater August 8, 1990F006 Nonwastewater August 8, 1988F006 (cyanides) Nonwastewater July 8, 1989F007 All July 8, 1989F008 All July 8, 1989F009 All July 8, 1989F010 All June 8, 1989F011 (cyanides) Nonwastewater December 8, 1989F011 All others July 8, 1989F012 (cyanides) Nonwastewater December 8, 1989F012 All others July 8, 1989F019 All August 8, 1990F020 All November 8, 1988F021 All November 8, 1988F025 All August 8, 1990F026 All November 8, 1988F027 All November 8, 1988F028 All November 8, 1988F032 Mixed with radioactive wastes May 12, 1999F032 All others August 12, 1997F034 Mixed with radioactive wastes May 12, 1999F034 All others August 12, 1997F035 Mixed with radioactive wastes May 12, 1999F035 All others August 12, 1997F037 Not generated from surface impoundment cleanouts or closures June 30, 1993F037 Generated from surface impoundment cleanouts or closures June 30, 1994F037 Mixed with radioactive wastes June 30, 1994F038 Not generated from surface impoundment cleanouts or closures June 30, 1993F038 Generated from surface impoundment cleanouts or closures June 30, 1994F038 Mixed with radioactive wastes June 30, 1994F039 Wastewater August 8, 1990F039 Nonwastewater May 8, 1992K001 (organics)b All August 8, 1988K001 All others August 8, 1988K002 All August 8, 1990K003 All August 8, 1990K004 Wastewater August 8, 1990K004 Nonwastewater August 8, 1988K005 Wastewater August 8, 1990K005 Nonwastewater June 8, 1989K006 All August 8, 1990K007 Wastewater August 8, 1990K007 Nonwastewater June 8, 1989K008 Wastewater August 8, 1990K008 Nonwastewater August 8, 1988K009 All June 8, 1989K010 All June 8, 1989K011 Wastewater August 8, 1990K011 Nonwastewater June 8, 1989K013 Wastewater August 8, 1990K013 Nonwastewater June 8, 1989K014 Wastewater August 8, 1990K014 Nonwastewater June 8, 1989K015 Wastewater August 8, 1988K015 Nonwastewater August 8, 1990K016 All August 8, 1988K017 All August 8, 1990K018 All August 8, 1988K019 All August 8, 1988K020 All August 8, 1988K021 Wastewater August 8, 1990K021 Nonwastewater August 8, 1988K022 Wastewater August 8, 1990K022 Nonwastewater August 8, 1988K023 All June 8, 1989K024 All August 8, 1988K025 Wastewater August 8, 1990K025 Nonwastewater August 8, 1988K026 All August 8, 1990K027 All June 8, 1989K028 (metals) Nonwastewater August 8, 1990K028 All others June 8, 1989K029 Wastewater August 8, 1990K029 Nonwastewater June 8, 1989K030 All August 8, 1988K031 Wastewater August 8, 1990K031 Nonwastewater May 8, 1992K032 All August 8, 1990K033 All August 8, 1990K034 All August 8, 1990K035 All August 8, 1990K036 Wastewater June 8, 1989K036 Nonwastewater August 8, 1988K037b Wastewater August 8, 1988K037 Nonwastewater August 8, 1988K038 All June 8, 1989K039 All June 8, 1989K040 All June 8, 1989K041 All August 8, 1990K042 All August 8, 1990K043 All June 8, 1989K044 All August 8, 1988K045 All August 8, 1988K046 (Nonreactive) Nonwastewater August 8, 1988K046 All others August 8, 1990K047 All August 8, 1988K048 Wastewater August 8, 1990K048 Nonwastewater November 8, 1990K049 Wastewater August 8, 1990K049 Nonwastewater November 8, 1990K050 Wastewater August 8, 1990K050 Nonwastewater November 8, 1990K051 Wastewater August 8, 1990K051 Nonwastewater November 8, 1990K052 Wastewater August 8, 1990K052 Nonwastewater November 8, 1990K060 Wastewater August 8, 1990K060 Nonwastewater August 8, 1988K061 Wastewater August 8, 1990K061 Nonwastewater June 30, 1992K062 All August 8, 1988K069 (non-calcium sulfate) Nonwastewater August 8, 1988K069 All others August 8, 1990K071 All August 8, 1990K073 All August 8, 1990K083 All August 8, 1990K084 Wastewater August 8, 1990K084 Nonwastewater May 8, 1992K085 All August 8, 1990K086 (organics)b All August 8, 1988K086 All others August 8, 1988K087 All August 8, 1988K088 All others October 8, 1997K088 All others January 8, 1997K093 All June 8, 1989K094 All June 8, 1989K095 Wastewater August 8, 1990K095 Nonwastewater June 8, 1989K096 Wastewater August 8, 1990K096 Nonwastewater June 8, 1989K097 All August 8, 1990K098 All August 8, 1990K099 All August 8, 1988K100 Wastewater August 8, 1990K100 Nonwastewater August 8, 1988K101 (organics) Wastewater August 8, 1988K101 (metals) Wastewater August 8, 1990K101 (organics) Nonwastewater August 8, 1988K101 (metals) Nonwastewater May 8, 1992K102 (organics) Wastewater August 8, 1988K102 (metals) Wastewater August 8, 1990K102 (organics) Nonwastewater August 8, 1988K102 (metals) Nonwastewater May 8, 1992K103 All August 8, 1988K104 All August 8, 1988K105 All August 8, 1990K106 Wastewater August 8, 1990K106 Nonwastewater May 8, 1992K107 Mixed with radioactive wastes June 30, 1994K107 All others November 9, 1992K108 Mixed with radioactive wastes June 30, 1994K108 All others November 9, 1992K109 Mixed with radioactive wastes June 30, 1994K109 All others November 9, 1992K110 Mixed with radioactive wastes June 30, 1994K110 All others November 9, 1992K111 Mixed with radioactive wastes June 30, 1994K111 All others November 9, 1992K112 Mixed with radioactive wastes June 30, 1994K112 All others November 9, 1992K113 All June 8, 1989K114 All June 8, 1989K115 All June 8, 1989K116 All June 8, 1989K117 Mixed with radioactive wastes June 30, 1994K117 All others November 9, 1992K118 Mixed with radioactive wastes June 30, 1994K118 All others November 9, 1992K123 Mixed with radioactive wastes June 30, 1994K123 All others November 9, 1992K124 Mixed with radioactive wastes June 30, 1994K124 All others November 9, 1992K125 Mixed with radioactive wastes June 30, 1994K125 All others November 9, 1992K126 Mixed with radioactive wastes June 30, 1994K126 All others November 9, 1992K131 Mixed with radioactive wastes June 30, 1994K131 All others November 9, 1992K132 Mixed with radioactive wastes June 30, 1994K132 All others November 9, 1992K136 Mixed with radioactive wastes June 30, 1994K136 All others November 9, 1992K141 Mixed with radioactive wastes September 19, 1996K141 All others December 19, 1994K142 Mixed with radioactive wastes September 19, 1996K142 All others December 19, 1994K143 Mixed with radioactive wastes September 19, 1996K143 All others December 19, 1994K144 Mixed with radioactive wastes September 19, 1996K144 All others December 19, 1994K145 Mixed with radioactive wastes September 19, 1996K145 All others December 19, 1994K147 Mixed with radioactive wastes September 19, 1996K147 All others December 19, 1994K148 Mixed with radioactive wastes September 19, 1996K148 All others December 19, 1994
K149 Mixed with radioactive wastes September 19, 1996K149 All others December 19, 1994K150 Mixed with radioactive wastes September 19, 1996K150 All others December 19, 1994K151 Mixed with radioactive wastes September 19, 1996K151 All others December 19, 1994K156 Mixed with radioactive wastes April 8, 1998K156 All others July 8, 1996K157 Mixed with radioactive wastes April 8, 1998K157 All others July 8, 1996K158 Mixed with radioactive wastes April 8, 1998K158 All others July 8, 1996K159 Mixed with radioactive wastes April 8, 1998K159 All others July 8, 1996K160 Mixed with radioactive wastes April 8, 1998K160 All others July 8, 1996K161 Mixed with radioactive wastes April 8, 1998K161 All others July 8, 1996K169 All February 8, 1999K170 All February 8, 1999K171 All February 8, 1999K172 All February 8, 1999K174 All May 7, 2001K175 All May 7, 2001K176 All May 20, 2002K177 All May 20, 2002K178 All May 20, 2002K181 All August 23, 2005P001 All August 8, 1990P002 All August 8, 1990P003 All August 8, 1990P004 All August 8, 1990P005 All August 8, 1990P006 All August 8, 1990P007 All August 8, 1990P008 All August 8, 1990P009 All August 8, 1990P010 Wastewater August 8, 1990P010 Nonwastewater May 8, 1992P011 Wastewater August 8, 1990P011 Nonwastewater May 8, 1992P012 Wastewater August 8, 1990P012 Nonwastewater May 8, 1992P013 (barium) Nonwastewater August 8, 1990P013 All others June 8, 1989P014 All August 8, 1990P015 All August 8, 1990P016 All August 8, 1990P017 All August 8, 1990P018 All August 8, 1990P020 All August 8, 1990P021 All June 8, 1989P022 All August 8, 1990P023 All August 8, 1990P024 All August 8, 1990P026 All August 8, 1990P027 All August 8, 1990P028 All August 8, 1990P029 All June 8, 1989P030 All June 8, 1989P031 All August 8, 1990P033 All August 8, 1990P034 All August 8, 1990P036 Wastewater August 8, 1990P036 Nonwastewater May 8, 1992P037 All August 8, 1990P038 Wastewater August 8, 1990P038 Nonwastewater May 8, 1992P039 All June 8, 1989P040 All June 8, 1989P041 All June 8, 1989P042 All August 8, 1990P043 All June 8, 1989P044 All June 8, 1989P045 All August 8, 1990P046 All August 8, 1990P047 All August 8, 1990P048 All August 8, 1990P049 All August 8, 1990P050 All August 8, 1990P051 All August 8, 1990P054 All August 8, 1990P056 All August 8, 1990P057 All August 8, 1990P058 All August 8, 1990P059 All August 8, 1990P060 All August 8, 1990P062 All June 8, 1989P063 All June 8, 1989P064 All August 8, 1990P065 Wastewater August 8, 1990P065 Nonwastewater May 8, 1992P066 All August 8, 1990P067 All August 8, 1990P068 All August 8, 1990P069 All August 8, 1990P070 All August 8, 1990P071 All June 8, 1989P072 All August 8, 1990P073 All August 8, 1990P074 All June 8, 1989P075 All August 8, 1990P076 All August 8, 1990P077 All August 8, 1990P078 All August 8, 1990P081 All August 8, 1990P082 All August 8, 1990P084 All August 8, 1990P085 All June 8, 1989P087 All May 8, 1992P088 All August 8, 1990P089 All June 8, 1989P092 Wastewater August 8, 1990P092 Nonwastewater May 8, 1992P093 All August 8, 1990P094 All June 8, 1989P095 All August 8, 1990P096 All August 8, 1990P097 All June 8, 1989P098 All June 8, 1989P099 (silver) Wastewater August 8, 1990P099 All others June 8, 1989P101 All August 8, 1990P102 All August 8, 1990P103 All August 8, 1990P104 (silver) Wastewater August 8, 1990P104 All others June 8, 1989P105 All August 8, 1990P106 All June 8, 1989P108 All August 8, 1990P109 All June 8, 1989P110 All August 8, 1990P111 All June 8, 1989P112 All August 8, 1990P113 All August 8, 1990P114 All August 8, 1990P115 All August 8, 1990P116 All August 8, 1990P118 All August 8, 1990P119 All August 8, 1990P120 All August 8, 1990P121 All June 8, 1989P122 All August 8, 1990P123 All August 8, 1990P127 Mixed with radioactive wastes April 8, 1998P127 All others July 8, 1996P128 Mixed with radioactive wastes April 8, 1998P128 All others July 8, 1996P185 Mixed with radioactive wastes April 8, 1998P185 All others July 8, 1996P188 Mixed with radioactive wastes April 8, 1998P188 All others July 8, 1996P189 Mixed with radioactive wastes April 8, 1998P189 All others July 8, 1996P190 Mixed with radioactive wastes April 8, 1998P190 All others July 8, 1996P191 Mixed with radioactive wastes April 8, 1998P191 All others July 8, 1996P192 Mixed with radioactive wastes April 8, 1998P192 All others July 8, 1996P194 Mixed with radioactive wastes April 8, 1998P194 All others July 8, 1996P196 Mixed with radioactive wastes April 8, 1998P196 All others July 8, 1996P197 Mixed with radioactive wastes April 8, 1998P197 All others July 8, 1996P198 Mixed with radioactive wastes April 8, 1998P198 All others July 8, 1996P199 Mixed with radioactive wastes April 8, 1998P199 All others July 8, 1996P201 Mixed with radioactive wastes April 8, 1998P201 All others July 8, 1996P202 Mixed with radioactive wastes April 8, 1998P202 All others July 8, 1996P203 Mixed with radioactive wastes April 8, 1998P203 All others July 8, 1996P204 Mixed with radioactive wastes April 8, 1998P204 All others July 8, 1996P205 Mixed with radioactive wastes April 8, 1998P205 All others July 8, 1996U001 All August 8, 1990U002 All August 8, 1990U003 All August 8, 1990U004 All August 8, 1990U005 All August 8, 1990U006 All August 8, 1990U007 All August 8, 1990U008 All August 8, 1990U009 All August 8, 1990U010 All August 8, 1990U011 All August 8, 1990U012 All August 8, 1990U014 All August 8, 1990U015 All August 8, 1990U016 All August 8, 1990U017 All August 8, 1990U018 All August 8, 1990U019 All August 8, 1990U020 All August 8, 1990U021 All August 8, 1990U022 All August 8, 1990U023 All August 8, 1990U024 All August 8, 1990U025 All August 8, 1990U026 All August 8, 1990U027 All August 8, 1990U028 All June 8, 1989U029 All August 8, 1990U030 All August 8, 1990U031 All August 8, 1990U032 All August 8, 1990U033 All August 8, 1990U034 All August 8, 1990U035 All August 8, 1990U036 All August 8, 1990U037 All August 8, 1990U038 All August 8, 1990U039 All August 8, 1990U041 All August 8, 1990U042 All August 8, 1990U043 All August 8, 1990U044 All August 8, 1990U045 All August 8, 1990U046 All August 8, 1990U047 All August 8, 1990U048 All August 8, 1990U049 All August 8, 1990U050 All August 8, 1990U051 All August 8, 1990U052 All August 8, 1990U053 All August 8, 1990U055 All August 8, 1990U056 All August 8, 1990U057 All August 8, 1990U058 All June 8, 1989U059 All August 8, 1990U060 All August 8, 1990U061 All August 8, 1990U062 All August 8, 1990U063 All August 8, 1990U064 All August 8, 1990U066 All August 8, 1990U067 All August 8, 1990U068 All August 8, 1990U069 All June 30, 1992U070 All August 8, 1990U071 All August 8, 1990U072 All August 8, 1990U073 All August 8, 1990U074 All August 8, 1990U075 All August 8, 1990U076 All August 8, 1990U077 All August 8, 1990U078 All August 8, 1990U079 All August 8, 1990U080 All August 8, 1990U081 All August 8, 1990U082 All August 8, 1990U083 All August 8, 1990U084 All August 8, 1990U085 All August 8, 1990U086 All August 8, 1990U087 All June 8, 1989U088 All June 8, 1989U089 All August 8, 1990U090 All August 8, 1990U091 All August 8, 1990U092 All August 8, 1990U093 All August 8, 1990U094 All August 8, 1990U095 All August 8, 1990U096 All August 8, 1990U097 All August 8, 1990U098 All August 8, 1990U099 All August 8, 1990U101 All August 8, 1990U102 All June 8, 1989U103 All August 8, 1990U105 All August 8, 1990U106 All August 8, 1990U107 All June 8, 1989U108 All August 8, 1990U109 All August 8, 1990U110 All August 8, 1990U111 All August 8, 1990U112 All August 8, 1990U113 All August 8, 1990U114 All August 8, 1990U115 All August 8, 1990U116 All August 8, 1990U117 All August 8, 1990U118 All August 8, 1990U119 All August 8, 1990U120 All August 8, 1990U121 All August 8, 1990U122 All August 8, 1990U123 All August 8, 1990U124 All August 8, 1990U125 All August 8, 1990U126 All August 8, 1990U127 All August 8, 1990U128 All August 8, 1990U129 All August 8, 1990U130 All August 8, 1990U131 All August 8, 1990U132 All August 8, 1990U133 All August 8, 1990U134 All August 8, 1990U135 All August 8, 1990U136 Wastewater August 8, 1990U136 Nonwastewater May 8, 1992U137 All August 8, 1990U138 All August 8, 1990U140 All August 8, 1990U141 All August 8, 1990U142 All August 8, 1990U143 All August 8, 1990U144 All August 8, 1990U145 All August 8, 1990U146 All August 8, 1990U147 All August 8, 1990U148 All August 8, 1990U149 All August 8, 1990U150 All August 8, 1990U151 Wastewater August 8, 1990U151 Nonwastewater May 8, 1992U152 All August 8, 1990U153 All August 8, 1990U154 All August 8, 1990U155 All August 8, 1990U156 All August 8, 1990U157 All August 8, 1990U158 All August 8, 1990U159 All August 8, 1990U160 All August 8, 1990U161 All August 8, 1990U162 All August 8, 1990U163 All August 8, 1990U164 All August 8, 1990U165 All August 8, 1990U166 All August 8, 1990U167 All August 8, 1990U168 All August 8, 1990U169 All August 8, 1990U170 All August 8, 1990U171 All August 8, 1990U172 All August 8, 1990U173 All August 8, 1990U174 All August 8, 1990U176 All August 8, 1990U177 All August 8, 1990U178 All August 8, 1990U179 All August 8, 1990U180 All August 8, 1990U181 All August 8, 1990U182 All August 8, 1990U183 All August 8, 1990U184 All August 8, 1990U185 All August 8, 1990U186 All August 8, 1990U187 All August 8, 1990U188 All August 8, 1990U189 All August 8, 1990U190 All June 8, 1989U191 All August 8, 1990U192 All August 8, 1990U193 All August 8, 1990U194 All June 8, 1989U196 All August 8, 1990U197 All August 8, 1990U200 All August 8, 1990U201 All August 8, 1990U203 All August 8, 1990U204 All August 8, 1990U205 All August 8, 1990U206 All August 8, 1990U207 All August 8, 1990U208 All August 8, 1990U209 All August 8, 1990U210 All August 8, 1990U211 All August 8, 1990U213 All August 8, 1990U214 All August 8, 1990U215 All August 8, 1990U216 All August 8, 1990U217 All August 8, 1990U218 All August 8, 1990U219 All August 8, 1990U220 All August 8, 1990U221 All June 8, 1989U222 All August 8, 1990U223 All June 8, 1989U225 All August 8, 1990U226 All August 8, 1990U227 All August 8, 1990U228 All August 8, 1990U234 All August 8, 1990U235 All June 8, 1989U236 All August 8, 1990U237 All August 8, 1990U238 All August 8, 1990U239 All August 8, 1990U240 All August 8, 1990U243 All August 8, 1990U244 All August 8, 1990U246 All August 8, 1990U247 All August 8, 1990U248 All August 8, 1990U249 All August 8, 1990U271 Mixed with radioactive wastes April 8, 1998U271 All others July 8, 1996U277 Mixed with radioactive wastes April 8, 1998U277 All others July 8, 1996U278 Mixed with radioactive wastes April 8, 1998U278 All others July 8, 1996U279 Mixed with radioactive wastes April 8, 1998U279 All others July 8, 1996U280 Mixed with radioactive wastes April 8, 1998U280 All others July 8, 1996U328 Mixed with radioactive wastes June 30, 1994U328 All others November 9, 1992U353 Mixed with radioactive wastes June 30, 1994U353 All others November 9, 1992U359 Mixed with radioactive wastes June 30, 1994U359 All others November 9, 1992U364 Mixed with radioactive wastes April 8, 1998U364 All others July 8, 1996U365 Mixed with radioactive wastes April 8, 1998U365 All others July 8, 1996U366 Mixed with radioactive wastes April 8, 1998U366 All others July 8, 1996U367 Mixed with radioactive wastes April 8, 1998U367 All others July 8, 1996U372 Mixed with radioactive wastes April 8, 1998U372 All others July 8, 1996U373 Mixed with radioactive wastes April 8, 1998U373 All others July 8, 1996U375 Mixed with radioactive wastes April 8, 1998U375 All others July 8, 1996U376 Mixed with radioactive wastes April 8, 1998U376 All others July 8, 1996U377 Mixed with radioactive wastes April 8, 1998U377 All others July 8, 1996U378 Mixed with radioactive wastes April 8, 1998U378 All others July 8, 1996U379 Mixed with radioactive wastes April 8, 1998U379 All others July 8, 1996U381 Mixed with radioactive wastes April 8, 1998U381 All others July 8, 1996U382 Mixed with radioactive wastes April 8, 1998U382 All others July 8, 1996U383 Mixed with radioactive wastes April 8, 1998U383 All others July 8, 1996U384 Mixed with radioactive wastes April 8, 1998U384 All others July 8, 1996U385 Mixed with radioactive wastes April 8, 1998U385 All others July 8, 1996U386 Mixed with radioactive wastes April 8, 1998U386 All others July 8, 1996U387 Mixed with radioactive wastes April 8, 1998U387 All others July 8, 1996U389 Mixed with radioactive wastes April 8, 1998U389 All others July 8, 1996U390 Mixed with radioactive wastes April 8, 1998U390 All others July 8, 1996U391 Mixed with radioactive wastes April 8, 1998U391 All others July 8, 1996U392 Mixed with radioactive wastes April 8, 1998U392 All others July 8, 1996U393 Mixed with radioactive wastes April 8, 1998U393 All others July 8, 1996U394 Mixed with radioactive wastes April 8, 1998U394 All others July 8, 1996U395 Mixed with radioactive wastes April 8, 1998U395 All others July 8, 1996U396 Mixed with radioactive wastes April 8, 1998U396 All others July 8, 1996U400 Mixed with radioactive wastes April 8, 1998U400 All others July 8, 1996U401 Mixed with radioactive wastes April 8, 1998U401 All others July 8, 1996U402 Mixed with radioactive wastes April 8, 1998U402 All others July 8, 1996U403 Mixed with radioactive wastes April 8, 1998U403 All others July 8, 1996U404 Mixed with radioactive wastes April 8, 1998U404 All others July 8, 1996U407 Mixed with radioactive wastes April 8, 1998U407 All others July 8, 1996U409 Mixed with radioactive wastes April 8, 1998U409 All others July 8, 1996U410 Mixed with radioactive wastes April 8, 1998U410 All others July 8, 1996U411 Mixed with radioactive wastes April 8, 1998U411 All others July 8, 1996b 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)
BOARD NOTE: These tables are provided for the convenience of the reader.
Restricted hazardous waste in CSD Effective date1. Solvent- (F001-F005) and dioxin- (F020-F023 and F026-F028) containing soil and debris from CERCLA response or RCRA corrective actions. November 8, 19902. 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, 19883. All soil and debris contaminated with First Third wastes for which treatment standards are based on incineration. August 8, 19904. All soil and debris contaminated with Second Third wastes for which treatment standards are based on incineration. June 8, 19915. 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, 19926. 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(Source: Amended at 40 Ill. Reg. 12052, effective August 9, 2016)
Section 728.APPENDIX H National Capacity LDR Variances for UIC Wastes
See Notea
a Wastes that are deep well disposed on-site receive a six-month variance, with restrictions, effective in November 1990.
USEPA Hazardous Waste Number Waste Category Effective DateD001 (except High TOC Ignitable Liquids Subcategory)c All February 10, 1994D001 (High TOC Ignitable Characteristic Liquids Subcategory) Nonwastewater September 19, 1995D002b All May 8, 1992D002c All February 10, 1994D003 (cyanides) All May 8, 1992D003 (sulfides) All May 8, 1992D003 (explosives, reactives) All May 8, 1992D007 All May 8, 1992D009 Nonwastewater May 8, 1992D012 All September 19, 1995D013 All September 19, 1995D014 All September 19, 1995D015 All September 19, 1995D016 All September 19, 1995D017 All September 19, 1995D018 All, including mixed with radioactive wastes April 8, 1998D019 All, including mixed with radioactive wastes April 8, 1998D020 All, including mixed with radioactive wastes April 8, 1998D021 All, including mixed with radioactive wastes April 8, 1998D022 All, including mixed with radioactive wastes April 8, 1998D023 All, including mixed with radioactive wastes April 8, 1998D024 All, including mixed with radioactive wastes April 8, 1998D025 All, including mixed with radioactive wastes April 8, 1998D026 All, including mixed with radioactive wastes April 8, 1998D027 All, including mixed with radioactive wastes April 8, 1998D028 All, including mixed with radioactive wastes April 8, 1998D029 All, including mixed with radioactive wastes April 8, 1998D030 All, including mixed with radioactive wastes April 8, 1998D031 All, including mixed with radioactive wastes April 8, 1998D032 All, including mixed with radioactive wastes April 8, 1998D033 All, including mixed with radioactive wastes April 8, 1998D034 All, including mixed with radioactive wastes April 8, 1998D035 All, including mixed with radioactive wastes April 8, 1998D036 All, including mixed with radioactive wastes April 8, 1998D037 All, including mixed with radioactive wastes April 8, 1998D038 All, including mixed with radioactive wastes April 8, 1998D039 All, including mixed with radioactive wastes April 8, 1998D040 All, including mixed with radioactive wastes April 8, 1998D041 All, including mixed with radioactive wastes April 8, 1998D042 All, including mixed with radioactive wastes April 8, 1998D043 All, including mixed with radioactive wastes April 8, 1998F001-F005 All spent F001-F005 solvent containing less than 1 percent total F001-F005 solvent constituents August 8, 1990F007 All June 8, 1991F032 All, including mixed with radioactive wastes May 12, 1999F034 All, including mixed with radioactive wastes May 12,1999F035 All, including mixed with radioactive wastes May 12, 1999F037 All November 8, 1992F038 All November 8, 1992F039 Wastewater May 8, 1992K009 Wastewater June 8, 1991K011 Nonwastewater June 8, 1991K011 Wastewater May 8, 1992K013 Nonwastewater June 8, 1991K013 Wastewater May 8, 1992K014 All May 8, 1992K016 (dilute) All June 8, 1991K049 All August 8, 1990K050 All August 8, 1990K051 All August 8, 1990K052 All August 8, 1990K062 All August 8, 1990K071 All August 8, 1990K088 All January 8, 1997K104 All August 8, 1990K107 All November 8, 1992K108 All November 9, 1992K109 All November 9, 1992K110 All November 9, 1992K111 All November 9, 1992K112 All November 9, 1992K117 All June 30, 1995K118 All June 30, 1995K123 All November 9, 1992K124 All November 9, 1992K125 All November 9, 1992K126 All November 9, 1992K131 All June 30, 1995K132 All June 30, 1995K136 All November 9, 1992K141 All December 19, 1994K142 All December 19, 1994K143 All December 19, 1994K144 All December 19, 1994K145 All December 19, 1994K147 All December 19, 1994K148 All December 19, 1994K149 All December 19, 1994K150 All December 19, 1994K151 All December 19, 1994K156 All July 8, 1996K157 All July 8, 1996K158 All July 8, 1996K159 All July 8, 1996K160 All July 8, 1996K161 All July 8, 1996NA Newly identified mineral processing wastes from titanium dioxide production and mixed radioactive/newly identified D004-D011 characteristic wastes and mineral processing wastes May 26, 2000P127 All July 8, 1996P128 All July 8, 1996P185 All July 8, 1996P188 All July 8, 1996P189 All July 8, 1996P190 All July 8, 1996P191 All July 8, 1996P192 All July 8, 1996P194 All July 8, 1996P196 All July 8, 1996P197 All July 8, 1996P198 All July 8, 1996P199 All July 8, 1996P201 All July 8, 1996P202 All July 8, 1996P203 All July 8, 1996P204 All July 8, 1996P205 All July 8, 1996U271 All July 8, 1996U277 All July 8, 1996U278 All July 8, 1996U279 All July 8, 1996U280 All July 8, 1996U328 All November 9, 1992U353 All November 9, 1992U359 All November 9, 1992U364 All July 8, 1996U365 All July 8, 1996U366 All July 8, 1996U367 All July 8, 1996U372 All July 8, 1996U373 All July 8, 1996U375 All July 8, 1996U376 All July 8, 1996U377 All July 8, 1996U378 All July 8, 1996U379 All July 8, 1996U381 All July 8, 1996U382 All July 8, 1996U383 All July 8, 1996U384 All July 8, 1996U385 All July 8, 1996U386 All July 8, 1996U387 All July 8, 1996U389 All July 8, 1996U390 All July 8, 1996U391 All July 8, 1996U392 All July 8, 1996U395 All July 8, 1996U396 All July 8, 1996U400 All July 8, 1996U401 All July 8, 1996U402 All July 8, 1996U403 All July 8, 1996U404 All July 8, 1996U407 All July 8, 1996U409 All July 8, 1996U410 All July 8, 1996U411 All July 8, 1996b 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.
(Source: Amended at 42 Ill. Reg. 24924, effective November 19, 2018)
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. 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.
BOARD NOTE: Derived from Table 1 to 40 CFR 268.45 (2017).
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” approvalAll 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” approvalAll 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” approvalAll 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. (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
BOARD NOTE: Derived from Table 1 to 40 CFR 268.7(a)(4) (2017).
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 ü4. 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 (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 Subcategory1D0019
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
Ignitable Characteristic Wastes, except for the 35 Ill. Adm. Code 721.121(a)(1) High TOC Subcategory.D0019
NA NA DEACT and meet Section 728.148 standards8; or RORGS; or CMBST DEACT and meet Section 728.148 standards8; or RORGS; or CMBST
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.)D0029
NA NA NA RORGS; CMBST; or POLYM
Corrosive Characteristic Wastes.D002, D004, D005, D006, D007, D008, D009, D010, D011
NA NA DEACT and meet Section 728.148 standards8 DEACT and meet Section 728.148 standards8
Radioactive high level wastes generated during the reprocessing of fuel rods.
(Note: This subcategory consists of nonwastewaters only.)D0039
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
Reactive Sulfides Subcategory based on 35 Ill. Adm. Code 721.123(a)(5).D0039
NA NA DEACT DEACT
Explosive subcategory based on 35 Ill. Adm. Code 721.123(a)(6), (a)(7), and (a)(8).D0039
NA NA DEACT and meet Section 728.148 standards8 DEACT and meet Section 728.148 standards8
Unexploded ordnance and other explosive devices that have been the subject of an emergency response.D0039
NA NA DEACT DEACT
Other Reactives Subcategory based on 35 Ill. Adm. Code 721.123(a)(1).D0039
NA NA DEACT and meet Section 728.148 standards8 DEACT and meet Section 728.148 standards8
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.)D0039
NA NA NA DEACT and meet Section 728.148 standards8
Reactive Cyanides Subcategory based on 35 Ill. Adm. Code 721.123(a)(5).D0049
Cyanides (Total)7 57-12-5 — 590 Cyanides (Amenable)7 57-12-5 0.86 30
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).D0059
Arsenic 7440-38-2 1.4 and meet Section 728.148 standards8 5.0 mg/ℓ TCLP and meet Section 728.148 standards8
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).D0069
Barium 7440-39-3 1.2 and meet Section 728.148 standards8 21 mg/ℓ TCLP and meet Section 728.148 standards8
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).D0069
Cadmium 7440-43-9 0.69 and meet Section 728.148 standards8 0.11 mg/ℓ TCLP and meet Section 728.148 standards8
Cadmium-Containing Batteries Subcategory.
(Note: This subcategory consists of nonwastewaters only.)D0069
Cadmium 7440-43-9 NA RTHRM
Radioactively contaminated cadmium-containing batteries.
(Note: This subcategory consists of nonwastewaters only.)D0079
Cadmium 7440-43-9 NA Macroencapsulation in accordance with Section 728.145
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).D0089
Chromium (Total) 7440-47-3 2.77 and meet Section 728.148 standards8 0.60 mg/ℓ TCLP and meet Section 728.148 standards8
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).D0089
Lead 7439-92-1 0.69 and meet Section 728.148 standards8 0.75 mg/ℓ TCLP and meet Section 728.148 standards8
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.)D0089
Lead 7439-92-1 NA RLEAD
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.)D0099
Lead 7439-92-1 NA MACRO
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)D0099
Mercury 7439-97-6 NA IMERC; or RMERC
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)D0099
Mercury 7439-97-6 NA RMERC
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)D0099
Mercury 7439-97-6 NA 0.20 mg/ℓ TCLP and meet Section 728.148 standards8
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)D0099
Mercury 7439-97-6 NA 0.025 mg/ℓ TCLP and meet Section 728.148 standards8
All D009 wastewaters.D0099
Mercury 7439-97-6 0.15 and meet Section 728.148 standards8 NA
Elemental mercury contaminated with radioactive materials.
(Note: This subcategory consists of nonwastewaters only.)D0099
Mercury 7439-97-6 NA AMLGM
Hydraulic oil contaminated with Mercury Radioactive Materials Subcategory.
(Note: This subcategory consists of nonwastewaters only.)D0099
Mercury 7439-97-6 NA IMERC
Radioactively contaminated mercury-containing batteries.
(Note: This subcategory consists of nonwastewaters only.)D0109
Mercury 7439-97-6 NA Macroencapsulation in accordance with Section 728.145
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).D0119
Selenium 7782-49-2 0.82 and meet Section 728.148 standards8 5.7 mg/ℓ TCLP and meet Section 728.148 standards8
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).D0119
Silver 7440-22-4 0.43 0.14 mg/ℓ TCLP and meet Section 728.148 standards8
Radioactively contaminated silver-containing batteries.
(Note: This subcategory consists of nonwastewaters only.)D0129
Silver 7440-22-4 NA Macroencapsulation in accordance with Section 728.145
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).D0139
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
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).D0149
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
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).D0159
Methoxychlor 72-43-5 WETOX or CMBST 0.18 and meet Section 728.148 standards8
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).D0169
Toxaphene 8001-35-2 BIODG or CMBST 2.6 and meet Section 728.148 standards8
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).D0179
2,4-D (2,4-dichlorophenoxyacetic acid) 94-75-7 CHOXD; BIODG; or CMBST 10 and meet Section 728.148 standards8
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).D0189
2,4,5-TP (Silvex) 93-72-1 CHOXD or CMBST 7.9 and meet Section 728.148 standards8
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).D0199
Benzene 71-43-2 0.14 and meet Section 728.148 standards8 10 and meet Section 728.148 standards8
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).D0209
Carbon tetrachloride 56-23-5 0.057 and meet Section 728.148 standards8 6.0 and meet Section 728.148 standards8
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).D0219
Chlordane (a and c isomers) 57-74-9 0.0033 and meet Section 728.148 standards8 0.26 and meet Section 728.148 standards8
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).D0229
Chlorobenzene 108-90-7 0.057 and meet Section 728.148 standards8 6.0 and meet Section 728.148 standards8
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).D0239
Chloroform 67-66-3 0.046 and meet Section 728.148 standards8 6.0 and meet Section 728.148 standards8
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).D0249
o-Cresol 95-48-7 0.11 and meet Section 728.148 standards8 5.6 and meet Section 728.148 standards8
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).D0259
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
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).D0269
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
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).D0279
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
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).D0289
p-Dichlorobenzene (1,4-Dichlorobenzene) 106-46-7 0.090 and meet Section 728.148 standards8 6.0 and meet Section 728.148 standards8
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).D0299
1,2-Dichloroethane 107-06-2 0.21 and meet Section 728.148 standards8 6.0 and meet Section 728.148 standards8
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).D0309
1,1-Dichloroethylene 75-35-4 0.025 and meet Section 728.148 standards8 6.0 and meet Section 728.148 standards8
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).D0319
2,4-Dinitrotoluene 121-14-2 0.32 and meet Section 728.148 standards8 140 and meet Section 728.148 standards8
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).D0329
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
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).D0339
Hexachlorobenzene 118-74-1 0.055 and meet Section 728.148 standards8 10 and meet Section 728.148 standards8
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).D0349
Hexachlorobutadiene 87-68-3 0.055 and meet Section 728.148 standards8 5.6 and meet Section 728.148 standards8
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).D0359
Hexachloroethane 67-72-1 0.055 and meet Section 728.148 standards8 30 and meet Section 728.148 standards8
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).D0369
Methyl ethyl ketone 78-93-3 0.28 and meet Section 728.148 standards8 36 and meet Section 728.148 standards8
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).D0379
Nitrobenzene 98-95-3 0.068 and meet Section 728.148 standards8 14 and meet Section 728.148 standards8
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).D0389
Pentachlorophenol 87-86-5 0.089 and meet Section 728.148 standards8 7.4 and meet Section 728.148 standards8
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).D0399
Pyridine 110-86-1 0.014 and meet Section 728.148 standards8 16 and meet Section 728.148 standards8
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).D0409
Tetrachloroethylene 127-18-4 0.056 and meet Section 728.148 standards8 6.0 and meet Section 728.148 standards8
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).D0419
Trichloroethylene 79-01-6 0.054 and meet Section 728.148 standards8 6.0 and meet Section 728.148 standards8
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).D0429
2,4,5-Trichlorophenol 95-95-4 0.18 and meet Section 728.148 standards8 7.4 and meet Section 728.148 standards8
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).D0439
2,4,6-Trichlorophenol 88-06-2 0.035 and meet Section 728.148 standards8 7.4 and meet Section 728.148 standards8
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).F001, F002, F003, F004 & F005
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, 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.F001, F002, F003, F004 & F005
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
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)).F001, F002, F003, F004 & F005
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
F005 solvent waste containing 2-Nitropropane as the only listed F001 through F005 solvent.F001, F002, F003, F004 & F005
2-Nitropropane 79-46-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
F005 solvent waste containing 2-Ethoxyethanol as the only listed F001 through F005 solvent.F006
2-Ethoxyethanol 110-80-5 BIODG; or CMBST CMBST
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.F007
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
Spent cyanide plating bath solutions from electroplating operations.F008
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
Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process.F009
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
Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process.F010
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
Quenching bath residues from oil baths from metal heat-treating operations where cyanides are used in the process.F011
Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 NA
Spent cyanide solutions from salt bath pot cleaning from metal heat-treating operations.F012
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
Quenching wastewater treatment sludges from metal heat-treating operations where cyanides are used in the process.F019
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
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.F020, F021, F022, F023, F026
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
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).F024
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
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.)F025
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
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.F025
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
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.F027
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
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.)F028
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
Residues resulting from the incineration or thermal treatment of soil contaminated with USEPA hazardous waste numbers F020, F021, F023, F026, and F027.F032
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
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.F034
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
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.F035
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
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.F037
Arsenic 7440-38-2 1.4 5.0 mg/ℓ TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/ℓ TCLP
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.F038
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
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.F039
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
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.).K001
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
Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote or pentachlorophenol.K002
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
Wastewater treatment sludge from the production of chrome yellow and orange pigments.K003
Chromium (Total) 7440-47-3 2.77 0.60 mg/ℓ TCLP Lead 7439-92-1 0.69 0.75 mg/ℓ TCLP
Wastewater treatment sludge from the production of molybdate orange pigments.K004
Chromium (Total) 7440-47-3 2.77 0.60 mg/ℓ TCLP Lead 7439-92-1 0.69 0.75 mg/ℓ TCLP
Wastewater treatment sludge from the production of zinc yellow pigments.K005
Chromium (Total) 7440-47-3 2.77 0.60 mg/ℓ TCLP Lead 7439-92-1 0.69 0.75 mg/ℓ TCLP
Wastewater treatment sludge from the production of chrome green pigments.K006
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
Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous).K006
Chromium (Total) 7440-47-3 2.77 0.60 mg/ℓ TCLP Lead 7439-92-1 0.69 0.75 mg/ℓ TCLP
Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated).K007
Chromium (Total) 7440-47-3 2.77 0.60 mg/ℓ TCLP Lead 7439-92-1 0.69 NA
Wastewater treatment sludge from the production of iron blue pigments.K008
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
Oven residue from the production of chrome oxide green pigments.K009
Chromium (Total) 7440-47-3 2.77 0.60 mg/ℓ TCLP Lead 7439-92-1 0.69 0.75 mg/ℓ TCLP
Distillation bottoms from the production of acetaldehyde from ethylene.K010
Chloroform 67-66-3 0.046 6.0
Distillation side cuts from the production of acetaldehyde from ethylene.K011
Chloroform 67-66-3 0.046 6.0
Bottom stream from the wastewater stripper in the production of acrylonitrile.K013
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
Bottom stream from the acetonitrile column in the production of acrylonitrile.K014
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
Bottoms from the acetonitrile purification column in the production of acrylonitrile.K015
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
Still bottoms from the distillation of benzyl chloride.K016
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
Heavy ends or distillation residues from the production of carbon tetrachloride.K017
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
Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.K018
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
Heavy ends from the fractionation column in ethyl chloride production.K019
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
Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production.K020
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
Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.K021
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
Aqueous spent antimony catalyst waste from fluoromethanes production.K022
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
Distillation bottom tars from the production of phenol or acetone from cumene.K023
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
Distillation light ends from the production of phthalic anhydride from naphthalene.K024
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
Distillation bottoms from the production of phthalic anhydride from naphthalene.K025
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
Distillation bottoms from the production of nitrobenzene by the nitration of benzene.K026
NA NA LLEXT fb SSTRP fb CARBN; or CMBST CMBST
Stripping still tails from the production of methyl ethyl pyridines.K027
NA NA CMBST CMBST
Centrifuge and distillation residues from toluene diisocyanate production.K028
NA NA CARBN; or CMBST CMBST
Spent catalyst from the hydrochlorinator reactor in the production of 1,1,1-trichloroethane.K029
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
Waste from the product steam stripper in the production of 1,1,1-trichloroethane.K030
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
Column bodies or heavy ends from the combined production of trichloroethylene and perchloroethylene.K031
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
By-product salts generated in the production of MSMA and cacodylic acid.K032
Arsenic 7440-38-2 1.4 5.0 mg/ℓ TCLP
Wastewater treatment sludge from the production of chlordane.K033
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
Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane.K034
Hexachlorocyclopentadiene 77-47-4 0.057 2.4
Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.K035
Hexachlorocyclopentadiene 77-47-4 0.057 2.4
Wastewater treatment sludges generated in the production of creosote.K036
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
Still bottoms from toluene reclamation distillation in the production of disulfoton.K037
Disulfoton 298-04-4 0.017 6.2
Wastewater treatment sludges from the production of disulfoton.K038
Disulfoton 298-04-4 0.017 6.2 Toluene 108-88-3 0.080 10
Wastewater from the washing and stripping of phorate production.K039
Phorate 298-02-2 0.021 4.6
Filter cake from the filtration of diethylphosphorodithioic acid in the production of phorate.K040
NA NA CARBN; or CMBST CMBST
Wastewater treatment sludge from the production of phorate.K041
Phorate 298-02-2 0.021 4.6
Wastewater treatment sludge from the production of toxaphene.K042
Toxaphene 8001-35-2 0.0095 2.6
Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5-T.K043
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
2,6-Dichlorophenol waste from the production of 2,4-D.K044
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
Wastewater treatment sludges from the manufacturing and processing of explosives.K045
NA NA DEACT DEACT
Spent carbon from the treatment of wastewater containing explosives.K046
NA NA DEACT DEACT
Wastewater treatment sludges from the manufacturing, formulation and loading of lead-based initiating compounds.K047
Lead 7439-92-1 0.69 0.75 mg/ℓ TCLP
Pink or red water from TNT operations.K048
NA NA DEACT DEACT
Dissolved air flotation (DAF) float from the petroleum refining industry.K049
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
Slop oil emulsion solids from the petroleum refining industry.K050
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
Heat exchanger bundle cleaning sludge from the petroleum refining industry.K051
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
API separator sludge from the petroleum refining industry.K052
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
Tank bottoms (leaded) from the petroleum refining industry.K060
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
Ammonia still lime sludge from coking operations.K061
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
Emission control dust or sludge from the primary production of steel in electric furnaces.K062
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
Spent pickle liquor generated by steel finishing operations of facilities within the iron and steel industry (SIC Codes 331 and 332).K069
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
Emission control dust or sludge from secondary lead smelting - Calcium sulfate (Low Lead) Subcategory.K069
Cadmium 7440-43-9 0.69 0.11 mg/ℓ TCLP Lead 7439-92-1 0.69 0.75 mg/ℓ TCLP
Emission control dust or sludge from secondary lead smelting - Non-Calcium sulfate (High Lead) Subcategory.K071
NA NA NA RLEAD
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.K071
Mercury 7439-97-6 NA 0.20 mg/ℓ TCLP
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.K071
Mercury 7439-97-6 NA 0.025 mg/ℓ TCLP
All K071 wastewaters.K073
Mercury 7439-97-6 0.15 NA
Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production.K083
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
Distillation bottoms from aniline production.K084
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
Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.K085
Arsenic 7440-38-2 1.4 5.0 mg/ℓ TCLP
Distillation or fractionation column bottoms from the production of chlorobenzenes.K086
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
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.K087
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
Decanter tank tar sludge from coking operations.K088
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
Spent potliners from primary aluminum reduction.K093
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
Distillation light ends from the production of phthalic anhydride from ortho-xylene.K094
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
Distillation bottoms from the production of phthalic anhydride from ortho-xylene.K095
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
Distillation bottoms from the production of 1,1,1-trichloroethane.K096
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
Heavy ends from the heavy ends column from the production of 1,1,1-trichloroethane.K097
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
Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.K098
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
Untreated process wastewater from the production of toxaphene.K099
Toxaphene 8001-35-2 0.0095 2.6
Untreated wastewater from the production of 2,4-D.K100
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
Waste leaching solution from acid leaching of emission control dust or sludge from secondary lead smelting.K101
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
Distillation tar residues from the distillation of aniline-based compounds in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.K102
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
Residue from the use of activated carbon for decolorization in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.K103
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
Process residues from aniline extraction from the production of aniline.K104
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
Combined wastewater streams generated from nitrobenzene or aniline production.K105
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
Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes.K106
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 (wastewater treatment sludge from the mercury cell process in chlorine production) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.K106
Mercury 7439-97-6 NA RMERC
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.K106
Mercury 7439-97-6 NA 0.20 mg/ℓ TCLP
Other K106 nonwastewaters that contain less than 260 mg/kg total mercury and are not residues from RMERC.K106
Mercury 7439-97-6 NA 0.025 mg/ℓ TCLP
All K106 wastewaters.K107
Mercury 7439-97-6 0.15 NA
Column bottoms from product separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.K108
NA NA CMBST; or CHOXD fb CARBN; or BIODG fb CARBN CMBST
Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.K109
NA NA CMBST; or CHOXD fb CARBN; or BIODG fb CARBN CMBST
Spent filter cartridges from product purification from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.K110
NA NA CMBST; or CHOXD fb CARBN; or BIODG fb CARBN CMBST
Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.K111
NA NA CMBST; or CHOXD fb CARBN; or BIODG fb CARBN CMBST
Product washwaters from the production of dinitrotoluene via nitration of toluene.K112
2,4-Dinitrotoluene 121-14-2 0.32 140 2,6-Dinitrotoluene 606-20-2 0.55 28
Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene.K113
NA NA CMBST; or CHOXD fb CARBN; or BIODG fb CARBN CMBST
Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.K114
NA NA CARBN; or CMBST CMBST
Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.K115
NA NA CARBN; or CMBST CMBST
Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.K116
Nickel 7440-02-0 3.98 11 mg/ℓ TCLP NA NA CARBN; or CMBST CMBST
Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine.K117
NA NA CARBN; or CMBST CMBST
Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene.K118
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
Spent absorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.K123
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
Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salts.K124
NA NA CMBST; or CHOXD fb (BIODG or CARBN) CMBST
Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.K125
NA NA CMBST; or CHOXD fb (BIODG or CARBN) CMBST
Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts.K126
NA NA CMBST; or CHOXD fb (BIODG or CARBN) CMBST
Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts.K131
NA NA CMBST; or CHOXD fb (BIODG or CARBN) CMBST
Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide.K132
Methyl bromide (Bromomethane) 74-83-9 0.11 15
Spent absorbent and wastewater separator solids from the production of methyl bromide.K136
Methyl bromide (Bromomethane) 74-83-9 0.11 15
Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.K141
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
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).K142
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
Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal.K143
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
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.K144
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
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.K145
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
Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal.K147
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
Tar storage tank residues from coal tar refining.K148
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
Residues from coal tar distillation, including, but not limited to, still bottoms.K149
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
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.)K150
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
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.K151
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
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.K156
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
Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes.K157
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
Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes.K158
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
Baghouse dusts and filter/separation solids from the production of carbamates and carbamoyl oximes.K159
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
Organics from the treatment of thiocarbamate wastes.10K161
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
Purification solids (including filtration, evaporation, and centrifugation solids), baghouse dust, and floor sweepings from the production of dithiocarbamate acids and their salts.K169
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
Crude oil tank sediment from petroleum refining operations.K170
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
Clarified slurry oil sediment from petroleum refining operations.K171
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
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.)K172
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
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.)K174
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
Wastewater treatment sludge from the production of ethylene dicholoride or vinyl choloride monomer.K175
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
Wastewater treatment sludge from the production of vinyl choloride monomer using mercuric chloride catalyst in an acetylene-based process.K175
Mercury12 7439-97-6 NA 0.025 mg/ℓ TCLP PH12 NA pH £ 6.0
All K175 wastewaters.K176
Mercury 7439-97-6 0.15 NA
Baghouse filters from the production of antimony oxide, including filters from the production of intermediates e.g., antimony metal or crude antimony oxide).K177
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
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).K178
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
Residues from manufacturing and manufacturing-site storage of ferric chloride from acids formed during the production of titanium dioxide using the chloride-ilmenite process.K181
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
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.P001
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
Warfarin, & salts, when present at concentrations greater than 0.3 percent.P002
Warfarin 81-81-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
1-Acetyl-2-thiourea.P003
1-Acetyl-2-thiourea 591-08-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Acrolein.P004
Acrolein 107-02-8 0.29 CMBST
Aldrin.P005
Aldrin 309-00-2 0.021 0.066
Allyl alcohol.P006
Allyl alcohol 107-18-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Aluminum phosphide.P007
Aluminum phosphide 20859-73-8 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST
5-Aminomethyl-3-isoxazolol.P008
5-Aminomethyl-3-isoxazolol 2763-96-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
4-Aminopyridine.P009
4-Aminopyridine 504-24-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Ammonium picrate.P010
Ammonium picrate 131-74-8 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST
Arsenic acid.P011
Arsenic 7440-38-2 1.4 5.0 mg/ℓ TCLP
Arsenic pentoxide.P012
Arsenic 7440-38-2 1.4 5.0 mg/ℓ TCLP
Arsenic trioxide.P013
Arsenic 7440-38-2 1.4 5.0 mg/ℓ TCLP
Barium cyanide.P014
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
Thiophenol (Benzene thiol).P015
Thiophenol (Benzene thiol) 108-98-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Beryllium dust.P016
Beryllium 7440-41-7 RMETL;or RTHRM RMETL; or RTHRM
Dichloromethyl ether (Bis(chloromethyl) ether).P017
Dichloromethyl ether 542-88-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Bromoacetone.P018
Bromoacetone 598-31-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Brucine.P020
Brucine 357-57-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
2-sec-Butyl-4,6-dinitrophenol (Dinoseb).P021
2-sec-Butyl-4,6-dinitrophenol (Dinoseb) 88-85-7 0.066 2.5
Calcium cyanide.P022
Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30
Carbon disulfide.P023
Carbon disulfide 75-15-0 3.8 CMBST Carbon disulfide; alternate6 standard for nonwastewaters only 75-15-0 NA 4.8 mg/ℓ TCLP
Chloroacetaldehyde.P024
Chloroacetaldehyde 107-20-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
p-Chloroaniline.P026
p-Chloroaniline 106-47-8 0.46 16
1-(o-Chlorophenyl)thiourea.P027
1-(o-Chlorophenyl)thiourea 5344-82-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
3-Chloropropionitrile.P028
3-Chloropropionitrile 542-76-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Benzyl chloride.P029
Benzyl chloride 100-44-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Copper cyanide.P030
Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30
Cyanides (soluble salts and complexes).P031
Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30
Cyanogen.P033
Cyanogen 460-19-5 CHOXD; WETOX; or CMBST CHOXD; WETOX; or CMBST
Cyanogen chloride.P034
Cyanogen chloride 506-77-4 CHOXD; WETOX; or CMBST CHOXD; WETOX; or CMBST
2-Cyclohexyl-4,6-dinitrophenol.P036
2-Cyclohexyl-4,6-dinitrophenol 131-89-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Dichlorophenylarsine.P037
Arsenic 7440-38-2 1.4 5.0 mg/ℓ TCLP
Dieldrin.P038
Dieldrin 60-57-1 0.017 0.13
Diethylarsine.P039
Arsenic 7440-38-2 1.4 5.0 mg/ℓ TCLP
Disulfoton.P040
Disulfoton 298-04-4 0.017 6.2
O,O-Diethyl-O-pyrazinyl-phosphorothioate.P041
O,O-Diethyl-O-pyrazinylphosphorothioate 297-97-2 CARBN; or CMBST CMBST
Diethyl-p-nitrophenyl phosphate.P042
Diethyl-p-nitrophenyl phosphate 311-45-5 CARBN; or CMBST CMBST
Epinephrine.P043
Epinephrine 51-43-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Diisopropylfluorophosphate (DFP).P044
Diisopropylfluorophosphate (DFP) 55-91-4 CARBN; or CMBST CMBST
Dimethoate.P045
Dimethoate 60-51-5 CARBN; or CMBST CMBST
Thiofanox.P046
Thiofanox 39196-18-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
a,a-Dimethylphenethylamine.P047
a,a-Dimethylphenethylamine 122-09-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
4,6-Dinitro-o-cresol.P047
4,6-Dinitro-o-cresol 543-52-1 0.28 160
4,6-Dinitro-o-cresol salts.P048
NA NA (WETOX or CHOXD) fb CARBN; or CMBST CMBST
2,4-Dinitrophenol.P049
2,4-Dinitrophenol 51-28-5 0.12 160
Dithiobiuret.P050
Dithiobiuret 541-53-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Endosulfan.P051
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.P054
Endrin 72-20-8 0.0028 0.13 Endrin aldehyde 7421-93-4 0.025 0.13
Aziridine.P056
Aziridine 151-56-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Fluorine.P057
Fluoride (measured in wastewaters only) 16984-48-8 35 ADGAS fb NEUTR
Fluoroacetamide.P058
Fluoroacetamide 640-19-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Fluoroacetic acid, sodium salt.P059
Fluoroacetic acid, sodium salt 62-74-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Heptachlor.P060
Heptachlor 76-44-8 0.0012 0.066 Heptachlor epoxide 1024-57-3 0.016 0.066
Isodrin.P062
Isodrin 465-73-6 0.021 0.066
Hexaethyl tetraphosphate.P063
Hexaethyl tetraphosphate 757-58-4 CARBN; or CMBST CMBST
Hydrogen cyanide.P064
Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30
Isocyanic acid, ethyl ester.P065
Isocyanic acid, ethyl ester 624-83-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
P065 (mercury fulminate) nonwastewaters, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC.P065
Mercury 7439-97-6 NA IMERC
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.P065
Mercury 7339-97-6 NA RMERC
P065 (mercury fulminate) nonwastewaters that are residues from RMERC and contain less than 260 mg/kg total mercury.P065
Mercury 7439-97-6 NA 0.20 mg/ℓ TCLP
P065 (mercury fulminate) nonwastewaters that are incinerator residues and contain less than 260 mg/kg total mercury.P065
Mercury 7439-97-6 NA 0.025 mg/ℓ TCLP
All P065 (mercury fulminate) wastewaters.P066
Mercury 7439-97-6 0.15 NA
Methomyl.P067
Methomyl 16752-77-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
2-Methyl-aziridine.P068
2-Methyl-aziridine 75-55-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Methyl hydrazine.P069
Methyl hydrazine 60-34-4 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED, or CMBST
2-Methyllactonitrile.P070
2-Methyllactonitrile 75-86-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Aldicarb.P071
Aldicarb 116-06-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Methyl parathion.P072
Methyl parathion 298-00-0 0.014 4.6
1-Naphthyl-2-thiourea.P073
1-Naphthyl-2-thiourea 86-88-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Nickel carbonyl.P074
Nickel 7440-02-0 3.98 11 mg/ℓ TCLP
Nickel cyanide.P075
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
Nicotine and salts.P076
Nicotine and salts 54-11-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Nitric oxide.P077
Nitric oxide 10102-43-9 ADGAS ADGAS
p-Nitroaniline.P078
p-Nitroaniline 100-01-6 0.028 28
Nitrogen dioxide.P081
Nitrogen dioxide 10102-44-0 ADGAS ADGAS
Nitroglycerin.P082
Nitroglycerin 55-63-0 CHOXD; CHRED; CARBN; BIODG or CMBST CHOXD; CHRED; or CMBST
N-Nitrosodimethylamine.P084
N-Nitrosodimethylamine 62-75-9 0.40 2.3
N-Nitrosomethylvinylamine.P085
N-Nitrosomethylvinylamine 4549-40-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Octamethylpyrophosphoramide.P087
Octamethylpyrophosphoramide 152-16-9 CARBN; or CMBST CMBST
Osmium tetroxide.P088
Osmium tetroxide 20816-12-0 RMETL; or RTHRM RMETL; or RTHRM
Endothall.P089
Endothall 145-73-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Parathion.P092
Parathion 56-38-2 0.014 4.6
P092 (phenyl mercuric acetate) nonwastewaters, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC.P092
Mercury 7439-97-6 NA IMERC; or RMERC
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.P092
Mercury 7439-97-6 NA RMERC
P092 (phenyl mercuric acetate) nonwastewaters that are residues from RMERC and contain less than 260 mg/kg total mercury.P092
Mercury 7439-97-6 NA 0.20 mg/ℓ TCLP
P092 (phenyl mercuric acetate) nonwastewaters that are incinerator residues and contain less than 260 mg/kg total mercury.P092
Mercury 7439-97-6 NA 0.025 mg/ℓ TCLP
All P092 (phenyl mercuric acetate) wastewaters.P093
Mercury 7439-97-6 0.15 NA
Phenylthiourea.P094
Phenylthiourea 103-85-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Phorate.P095
Phorate 298-02-2 0.021 4.6
Phosgene.P096
Phosgene 75-44-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Phosphine.P097
Phosphine 7803-51-2 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST
Famphur.P098
Famphur 52-85-7 0.017 15
Potassium cyanide.P099
Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30
Potassium silver cyanide.P101
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
Ethyl cyanide (Propanenitrile).P102
Ethyl cyanide (Propanenitrile) 107-12-0 0.24 360
Propargyl alcohol.P103
Propargyl alcohol 107-19-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Selenourea.P104
Selenium 7782-49-2 0.82 5.7 mg/ℓ TCLP
Silver cyanide.P105
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
Sodium azide.P106
Sodium azide 26628-22-8 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST
Sodium cyanide.P108
Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30
Strychnine and salts.P109
Strychnine and salts 57-24-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Tetraethyldithiopyrophosphate.P110
Tetraethyldithiopyrophosphate 3689-24-5 CARBN; or CMBST CMBST
Tetraethyl lead.P111
Lead 7439-92-1 0.69 0.75 mg/ℓ TCLP
Tetraethylpyrophosphate.P112
Tetraethylpyrophosphate 107-49-3 CARBN; or CMBST CMBST
Tetranitromethane.P113
Tetranitromethane 509-14-8 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST
Thallic oxide.P114
Thallium (measured in wastewaters only) 7440-28-0 1.4 RTHRM; or STABL
Thallium selenite.P115
Selenium 7782-49-2 0.82 5.7 mg/ℓ TCLP
Thallium (I) sulfate.P116
Thallium (measured in wastewaters only) 7440-28-0 1.4 RTHRM; or STABL
Thiosemicarbazide.P118
Thiosemicarbazide 79-19-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Trichloromethanethiol.P119
Trichloromethanethiol 75-70-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Ammonium vanadate.P120
Vanadium (measured in wastewaters only) 7440-62-2 4.3 STABL
Vanadium pentoxide.P121
Vanadium (measured in wastewaters only) 7440-62-2 4.3 STABL
Zinc cyanide.P122
Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30
Zinc phosphide Zn3P2, when present at concentrations greater than 10 percent.P123
Zinc Phosphide 1314-84-7 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST
Toxaphene.P127
Toxaphene 8001-35-2 0.0095 2.6
Carbofuran.10P128
Carbofuran 1563-66-2 0.006; or CMBST, CHOXD, BIODG or CARBN 0.14; or CMBST
Mexacarbate.10P185
Mexacarbate 315-18-4 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Tirpate.10P188
Tirpate 26419-73-8 0.056; or CMBST, CHOXD, BIODG or CARBN 0.28; or CMBST
Physostigimine salicylate.10P189
Physostigmine salicylate 57-64-7 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Carbosulfan.10P190
Carbosulfan 55285-14-8 0.028; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Metolcarb.10P191
Metolcarb 1129-41-5 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Dimetilan.10P192
Dimetilan 644-64-4 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Isolan.10P194
Isolan 119-38-0 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Oxamyl.10P196
Oxamyl 23135-22-0 0.056; or CMBST, CHOXD, BIODG or CARBN 0.28; or CMBST
Manganese dimethyldithiocarbamates (total).10P197
Dithiocarbamates (total) NA 0.028; or CMBST, CHOXD, BIODG or CARBN 28; or CMBST
Formparanate.10P198
Formparanate 17702-57-7 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Formetanate hydrochloride.10P199
Formetanate hydrochloride 23422-53-9 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Methiocarb.10P201
Methiocarb 2032-65-7 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Promecarb.10P202
Promecarb 2631-37-0 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
m-Cumenyl methylcarbamate.10P203
m-Cumenyl methylcarbamate 64-00-6 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Aldicarb sulfone.10P204
Aldicarb sulfone 1646-88-4 0.056; or CMBST, CHOXD, BIODG or CARBN 0.28; or CMBST
Physostigmine.10P205
Physostigmine 57-47-6 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Ziram.10U001
Dithiocarbamates (total) NA 0.028; or CMBST, CHOXD, BIODG or CARBN 28; or CMBST
Acetaldehyde.U002
Acetaldehyde 75-07-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Acetone.U003
Acetone 67-64-1 0.28 160
Acetonitrile.U004
Acetonitrile 75-05-8 5.6 CMBST Acetonitrile; alternate6 standard for nonwastewaters only 75-05-8 NA 38
Acetophenone.U005
Acetophenone 98-86-2 0.010 9.7
2-Acetylaminofluorene.U006
2-Acetylaminofluorene 53-96-3 0.059 140
Acetyl chloride.U007
Acetyl chloride 75-36-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Acrylamide.U008
Acrylamide 79-06-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Acrylic acid.U009
Acrylic acid 79-10-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Acrylonitrile.U010
Acrylonitrile 107-13-1 0.24 84
Mitomycin C.U011
Mitomycin C 50-07-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Amitrole.U012
Amitrole 61-82-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Aniline.U014
Aniline 62-53-3 0.81 14
Auramine.U015
Auramine 492-80-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Azaserine.U016
Azaserine 115-02-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Benz(c)acridine.U017
Benz(c)acridine 225-51-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Benzal chloride.U018
Benzal chloride 98-87-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Benz(a)anthracene.U019
Benz(a)anthracene 56-55-3 0.059 3.4
Benzene.U020
Benzene 71-43-2 0.14 10
Benzenesulfonyl chloride.U021
Benzenesulfonyl chloride 98-09-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Benzidine.U022
Benzidine 92-87-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Benzo(a)pyrene.U023
Benzo(a)pyrene 50-32-8 0.061 3.4
Benzotrichloride.U024
Benzotrichloride 98-07-7 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST
bis(2-Chloroethoxy)methane.U025
bis(2-Chloroethoxy)methane 111-91-1 0.036 7.2
bis(2-Chloroethyl) ether.U026
bis(2-Chloroethyl) ether 111-44-4 0.033 6.0
Chlornaphazine.U027
Chlornaphazine 494-03-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
bis(2-Chloroisopropyl) ether.U028
bis(2-Chloroisopropyl) ether 39638-32-9 0.055 7.2
bis(2-Ethylhexyl) phthalate.U029
bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28
Methyl bromide (Bromomethane).U030
Methyl bromide (Bromomethane) 74-83-9 0.11 15
4-Bromophenyl phenyl ether.U031
4-Bromophenyl phenyl ether 101-55-3 0.055 15
n-Butyl alcohol.U032
n-Butyl alcohol 71-36-3 5.6 2.6
Calcium chromate.U033
Chromium (Total) 7440-47-3 2.77 0.60 mg/ℓ TCLP
Carbon oxyfluoride.U034
Carbon oxyfluoride 353-50-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Trichloroacetaldehyde (Chloral).U035
Trichloroacetaldehyde (Chloral) 75-87-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Chlorambucil.U036
Chlorambucil 305-03-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Chlordane.U037
Chlordane (a and c isomers) 57-74-9 0.0033 0.26
Chlorobenzene.U038
Chlorobenzene 108-90-7 0.057 6.0
Chlorobenzilate.U039
Chlorobenzilate 510-15-6 0.10 CMBST
p-Chloro-m-cresol.U041
p-Chloro-m-cresol 59-50-7 0.018 14
Epichlorohydrin (1-Chloro-2,3-epoxypropane).U042
Epichlorohydrin (1-Chloro-2,3-epoxypropane) 106-89-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
2-Chloroethyl vinyl ether.U043
2-Chloroethyl vinyl ether 110-75-8 0.062 CMBST
Vinyl chloride.U044
Vinyl chloride 75-01-4 0.27 6.0
Chloroform.U045
Chloroform 67-66-3 0.046 6.0
Chloromethane (Methyl chloride).U046
Chloromethane (Methyl chloride) 74-87-3 0.19 30
Chloromethyl methyl ether.U047
Chloromethyl methyl ether 107-30-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
2-Chloronaphthalene.U048
2-Chloronaphthalene 91-58-7 0.055 5.6
2-Chlorophenol.U049
2-Chlorophenol 95-57-8 0.044 5.7
4-Chloro-o-toluidine hydrochloride.U050
4-Chloro-o-toluidine hydrochloride 3165-93-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Chrysene.U051
Chrysene 218-01-9 0.059 3.4
Creosote.U052
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
Cresols (Cresylic acid).U053
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
Crotonaldehyde.U055
Crotonaldehyde 4170-30-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Cumene.U056
Cumene 98-82-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Cyclohexane.U057
Cyclohexane 110-82-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Cyclohexanone.U058
Cyclohexanone 108-94-1 0.36 CMBST Cyclohexanone; alternate6 standard for nonwastewaters only 108-94-1 NA 0.75 mg/ℓ TCLP
Cyclophosphamide.U059
Cyclophosphamide 50-18-0 CARBN; or CMBST CMBST
Daunomycin.U060
Daunomycin 20830-81-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
DDD.U061
o,p'-DDD 53-19-0 0.023 0.087 p,p'-DDD 72-54-8 0.023 0.087
DDT.U062
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
Diallate.U063
Diallate 2303-16-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Dibenz(a,h)anthracene.U064
Dibenz(a,h)anthracene 53-70-3 0.055 8.2
Dibenz(a,i)pyrene.U066
Dibenz(a,i)pyrene 189-55-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
1,2-Dibromo-3-chloropropane.U067
1,2-Dibromo-3-chloropropane 96-12-8 0.11 15
Ethylene dibromide (1,2-Dibromoethane).U068
Ethylene dibromide (1,2-Dibromoethane) 106-93-4 0.028 15
Dibromomethane.U069
Dibromomethane 74-95-3 0.11 15
Di-n-butyl phthalate.U070
Di-n-butyl phthalate 84-74-2 0.057 28
o-Dichlorobenzene.U071
o-Dichlorobenzene 95-50-1 0.088 6.0
m-Dichlorobenzene.U072
m-Dichlorobenzene 541-73-1 0.036 6.0
p-Dichlorobenzene.U073
p-Dichlorobenzene 106-46-7 0.090 6.0
3,3'-Dichlorobenzidine.U074
3,3'-Dichlorobenzidine 91-94-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
1,4-Dichloro-2-butene.U075
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
Dichlorodifluoromethane.U076
Dichlorodifluoromethane 75-71-8 0.23 7.2
1,1-Dichloroethane.U077
1,1-Dichloroethane 75-34-3 0.059 6.0
1,2-Dichloroethane.U078
1,2-Dichloroethane 107-06-2 0.21 6.0
1,1-Dichloroethylene.U079
1,1-Dichloroethylene 75-35-4 0.025 6.0
1,2-Dichloroethylene.U080
trans-1,2-Dichloroethylene 156-60-5 0.054 30
Methylene chloride.U081
Methylene chloride 75-09-2 0.089 30
2,4-Dichlorophenol.U082
2,4-Dichlorophenol 120-83-2 0.044 14
2,6-Dichlorophenol.U083
2,6-Dichlorophenol 87-65-0 0.044 14
1,2-Dichloropropane.U084
1,2-Dichloropropane 78-87-5 0.85 18
1,3-Dichloropropylene.U085
cis-1,3-Dichloropropylene 10061-01-5 0.036 18 trans-1,3-Dichloropropylene 10061-02-6 0.036 18
1,2,3,4-DiepoxybutaneU086
1,2,3,4-Diepoxybutane 1464-53-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
N,N'-Diethylhydrazine.U087
N,N'-Diethylhydrazine 1615-80-1 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST
O,O-Diethyl-S-methyldithiophosphate.U088
O,O-Diethyl-S-methyldithiophosphate 3288-58-2 CARBN; or CMBST CMBST
Diethyl phthalate.U089
Diethyl phthalate 84-66-2 0.20 28
Diethyl stilbestrol.U090
Diethyl stilbestrol 56-53-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Dihydrosafrole.U091
Dihydrosafrole 94-58-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
3,3'-Dimethoxybenzidine.U092
3,3'-Dimethoxybenzidine 119-90-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Dimethylamine.U093
Dimethylamine 124-40-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
p-Dimethylaminoazobenzene.U094
p-Dimethylaminoazobenzene 60-11-7 0.13 CMBST
7,12-Dimethylbenz(a)anthracene.U095
7,12-Dimethylbenz(a)anthracene 57-97-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
3,3'-Dimethylbenzidine.U096
3,3'-Dimethylbenzidine 119-93-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
a, a-Dimethyl benzyl hydroperoxide.U097
a, a-Dimethyl benzyl hydroperoxide 80-15-9 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST
Dimethylcarbamoyl chloride.U098
Dimethylcarbamoyl chloride 79-44-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
1,1-Dimethylhydrazine.U099
1,1-Dimethylhydrazine 57-14-7 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST
1,2-Dimethylhydrazine.U101
1,2-Dimethylhydrazine 540-73-8 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST
2,4-Dimethylphenol.U102
2,4-Dimethylphenol 105-67-9 0.036 14
Dimethyl phthalate.U103
Dimethyl phthalate 131-11-3 0.047 28
Dimethyl sulfate.U105
Dimethyl sulfate 77-78-1 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST
2,4-Dinitrotoluene.U106
2,4-Dinitrotoluene 121-14-2 0.32 140
2,6-Dinitrotoluene.U107
2,6-Dinitrotoluene 606-20-2 0.55 28
Di-n-octyl phthalate.U108
Di-n-octyl phthalate 117-84-0 0.017 28
1,4-Dioxane.U109
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
1,2-Diphenylhydrazine.U110
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
Dipropylamine.U111
Dipropylamine 142-84-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Di-n-propylnitrosamine.U112
Di-n-propylnitrosamine 621-64-7 0.40 14
Ethyl acetate.U113
Ethyl acetate 141-78-6 0.34 33
Ethyl acrylate.U114
Ethyl acrylate 140-88-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Ethylenebisdithiocarbamic acid salts and esters.U115
Ethylenebisdithiocarbamic acid 111-54-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Ethylene oxide.U116
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
Ethylene thiourea.U117
Ethylene thiourea 96-45-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Ethyl ether.U118
Ethyl ether 60-29-7 0.12 160
Ethyl methacrylate.U119
Ethyl methacrylate 97-63-2 0.14 160
Ethyl methane sulfonate.U120
Ethyl methane sulfonate 62-50-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Fluoranthene.U121
Fluoranthene 206-44-0 0.068 3.4
Trichloromonofluoromethane.U122
Trichloromonofluoromethane 75-69-4 0.020 30
Formaldehyde.U123
Formaldehyde 50-00-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Formic acid.U124
Formic acid 64-18-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Furan.U125
Furan 110-00-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Furfural.U126
Furfural 98-01-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Glycidylaldehyde.U127
Glycidylaldehyde 765-34-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Hexachlorobenzene.U128
Hexachlorobenzene 118-74-1 0.055 10
Hexachlorobutadiene.U129
Hexachlorobutadiene 87-68-3 0.055 5.6
Lindane.U130
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
Hexachlorocyclopentadiene.U131
Hexachlorocyclopentadiene 77-47-4 0.057 2.4
Hexachloroethane.U132
Hexachloroethane 67-72-1 0.055 30
Hexachlorophene.U133
Hexachlorophene 70-30-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Hydrazine.U134
Hydrazine 302-01-2 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST
Hydrogen fluoride.U135
Fluoride (measured in wastewaters only) 7664-39-3 35 ADGAS fb NEUTR; or NEUTR
Hydrogen sulfide.U136
Hydrogen sulfide 7783-06-4 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST
Cacodylic acid.U137
Arsenic 7440-38-2 1.4 5.0 mg/ℓ TCLP
Indeno(1,2,3-cd)pyrene.U138
Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4
Iodomethane.U140
Iodomethane 74-88-4 0.19 65
Isobutyl alcohol.U141
Isobutyl alcohol 78-83-1 5.6 170
Isosafrole.U142
Isosafrole 120-58-1 0.081 2.6
Kepone.U143
Kepone 143-50-8 0.0011 0.13
Lasiocarpine.U144
Lasiocarpine 303-34-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Lead acetate.U145
Lead 7439-92-1 0.69 0.75 mg/ℓ TCLP
Lead phosphate.U146
Lead 7439-92-1 0.69 0.75 mg/ℓ TCLP
Lead subacetate.U147
Lead 7439-92-1 0.69 0.75 mg/ℓ TCLP
Maleic anhydride.U148
Maleic anhydride 108-31-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Maleic hydrazide.U149
Maleic hydrazide 123-33-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Malononitrile.U150
Malononitrile 109-77-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Melphalan.U151
Melphalan 148-82-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
U151 (mercury) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.U151
Mercury 7439-97-6 NA RMERC
U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are residues from RMERC only.U151
Mercury 7439-97-6 NA 0.20 mg/ℓ TCLP
U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are not residues from RMERC only.U151
Mercury 7439-97-6 NA 0.025 mg/ℓ TCLP
All U151 (mercury) wastewater.U151
Mercury 7439-97-6 0.15 NA
Elemental Mercury Contaminated with Radioactive Materials.U152
Mercury 7439-97-6 NA AMLGM
Methacrylonitrile.U153
Methacrylonitrile 126-98-7 0.24 84
Methanethiol.U154
Methanethiol 74-93-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Methanol.U155
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
Methapyrilene.U156
Methapyrilene 91-80-5 0.081 1.5
Methyl chlorocarbonate.U157
Methyl chlorocarbonate 79-22-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
3-Methylcholanthrene.U158
3-Methylcholanthrene 56-49-5 0.0055 15
4,4'-Methylene bis(2-chloroaniline).U159
4,4'-Methylene bis(2-chloroaniline) 101-14-4 0.50 30
Methyl ethyl ketone.U160
Methyl ethyl ketone 78-93-3 0.28 36
Methyl ethyl ketone peroxide.U161
Methyl ethyl ketone peroxide 1338-23-4 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST
Methyl isobutyl ketone.U162
Methyl isobutyl ketone 108-10-1 0.14 33
Methyl methacrylate.U163
Methyl methacrylate 80-62-6 0.14 160
N-Methyl-N'-nitro-N-nitrosoguanidine.U164
N-Methyl-N'-nitro-N-nitrosoguanidine 70-25-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Methylthiouracil.U165
Methylthiouracil 56-04-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Naphthalene.U166
Naphthalene 91-20-3 0.059 5.6
1,4-Naphthoquinone.U167
1,4-Naphthoquinone 130-15-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
1-Naphthylamine.U168
1-Naphthylamine 134-32-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
2-Naphthylamine.U169
2-Naphthylamine 91-59-8 0.52 CMBST
Nitrobenzene.U170
Nitrobenzene 98-95-3 0.068 14
p-Nitrophenol.U171
p-Nitrophenol 100-02-7 0.12 29
2-Nitropropane.U172
2-Nitropropane 79-46-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
N-Nitrosodi-n-butylamine.U173
N-Nitrosodi-n-butylamine 924-16-3 0.40 17
N-Nitrosodiethanolamine.U174
N-Nitrosodiethanolamine 1116-54-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
N-Nitrosodiethylamine.U176
N-Nitrosodiethylamine 55-18-5 0.40 28
N-Nitroso-N-ethylurea.U177
N-Nitroso-N-ethylurea 759-73-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
N-Nitroso-N-methylurea.U178
N-Nitroso-N-methylurea 684-93-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
N-Nitroso-N-methylurethane.U179
N-Nitroso-N-methylurethane 615-53-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
N-Nitrosopiperidine.U180
N-Nitrosopiperidine 100-75-4 0.013 35
N-Nitrosopyrrolidine.U181
N-Nitrosopyrrolidine 930-55-2 0.013 35
5-Nitro-o-toluidine.U182
5-Nitro-o-toluidine 99-55-8 0.32 28
Paraldehyde.U183
Paraldehyde 123-63-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Pentachlorobenzene.U184
Pentachlorobenzene 608-93-5 0.055 10
Pentachloroethane.U185
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
Pentachloronitrobenzene.U186
Pentachloronitrobenzene 82-68-8 0.055 4.8
1,3-Pentadiene.U187
1,3-Pentadiene 504-60-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Phenacetin.U188
Phenacetin 62-44-2 0.081 16
Phenol.U189
Phenol 108-95-2 0.039 6.2
Phosphorus sulfide.U190
Phosphorus sulfide 1314-80-3 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST
Phthalic anhydride.U191
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
2-Picoline.U192
2-Picoline 109-06-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Pronamide.U193
Pronamide 23950-58-5 0.093 1.5
1,3-Propane sultone.U194
1,3-Propane sultone 1120-71-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
n-Propylamine.U196
n-Propylamine 107-10-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Pyridine.U197
Pyridine 110-86-1 0.014 16
p-Benzoquinone.U200
p-Benzoquinone 106-51-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Reserpine.U201
Reserpine 50-55-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Resorcinol.U203
Resorcinol 108-46-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Safrole.U204
Safrole 94-59-7 0.081 22
Selenium dioxide.U205
Selenium 7782-49-2 0.82 5.7 mg/ℓ TCLP
Selenium sulfide.U206
Selenium 7782-49-2 0.82 5.7 mg/ℓ TCLP
Streptozotocin.U207
Streptozotocin 18883-66-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
1,2,4,5-Tetrachlorobenzene.U208
1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14
1,1,1,2-Tetrachloroethane.U209
1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0
1,1,2,2-Tetrachloroethane.U210
1,1,2,2-Tetrachloroethane 79-34-5 0.057 6.0
Tetrachloroethylene.U211
Tetrachloroethylene 127-18-4 0.056 6.0
Carbon tetrachloride.U213
Carbon tetrachloride 56-23-5 0.057 6.0
Tetrahydrofuran.U214
Tetrahydrofuran 109-99-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Thallium (I) acetate.U215
Thallium (measured in wastewaters only) 7440-28-0 1.4 RTHRM; or STABL
Thallium (I) carbonate.U216
Thallium (measured in wastewaters only) 7440-28-0 1.4 RTHRM; or STABL
Thallium (I) chloride.U217
Thallium (measured in wastewaters only) 7440-28-0 1.4 RTHRM; or STABL
Thallium (I) nitrate.U218
Thallium (measured in wastewaters only) 7440-28-0 1.4 RTHRM; or STABL
Thioacetamide.U219
Thioacetamide 62-55-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Thiourea.U220
Thiourea 62-56-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Toluene.U221
Toluene 108-88-3 0.080 10
Toluenediamine.U222
Toluenediamine 25376-45-8 CARBN; or CMBST CMBST
o-Toluidine hydrochloride.U223
o-Toluidine hydrochloride 636-21-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Toluene diisocyanate.U225
Toluene diisocyanate 26471-62-5 CARBN; or CMBST CMBST
Bromoform (Tribromomethane).U226
Bromoform (Tribromomethane) 75-25-2 0.63 15
1,1,1-Trichloroethane.U227
1,1,1-Trichloroethane 71-55-6 0.054 6.0
1,1,2-Trichloroethane.U228
1,1,2-Trichloroethane 79-00-5 0.054 6.0
Trichloroethylene.U234
Trichloroethylene 79-01-6 0.054 6.0
1,3,5-Trinitrobenzene.U235
1,3,5-Trinitrobenzene 99-35-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
tris-(2,3-Dibromopropyl)-phosphate.U236
tris-(2,3-Dibromopropyl)-phosphate 126-72-7 0.11 0.10
Trypan Blue.U237
Trypan Blue 72-57-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Uracil mustard.U238
Uracil mustard 66-75-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Urethane (Ethyl carbamate).U239
Urethane (Ethyl carbamate) 51-79-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Xylenes.U240
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene concentrations)1330-20-7 0.32 30
2,4-D (2,4-Dichlorophenoxyacetic acid).U243
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
Hexachloropropylene.U244
Hexachloropropylene 1888-71-7 0.035 30
Thiram.U246
Thiram 137-26-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Cyanogen bromide.U247
Cyanogen bromide 506-68-3 CHOXD; WETOX; or CMBST CHOXD; WETOX; or CMBST
Methoxychlor.U248
Methoxychlor 72-43-5 0.25 0.18
Warfarin, & salts, when present at concentrations of 0.3 percent or less.U249
Warfarin 81-81-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST
Zinc phosphide, Zn3P2, when present at concentrations of 10 percent or less.U271
Zinc Phosphide 1314-84-7 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST
Benomyl.10U278
Benomyl 17804-35-2 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Bendiocarb.10U279
Bendiocarb 22781-23-3 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Carbaryl.10U280
Carbaryl 63-25-2 0.006; or CMBST, CHOXD, BIODG or CARBN 0.14; or CMBST
Barban.10U328
Barban 101-27-9 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
o-Toluidine.U353
o-Toluidine 95-53-4 CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN CMBST
p-Toluidine.U359
p-Toluidine 106-49-0 CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN CMBST
2-Ethoxyethanol.U364
2-Ethoxyethanol 110-80-5 CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN CMBST
Bendiocarb phenol.10U367
Bendiocarb phenol 22961-82-6 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Carbofuran phenol.10U372
Carbofuran phenol 1563-38-8 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Carbendazim.10U373
Carbendazim 10605-21-7 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Propham.10U387
Propham 122-42-9 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Prosulfocarb.10U389
Prosulfocarb 52888-80-9 0.042; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Triallate.10U394
Triallate 2303-17-5 0.042; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
A2213.10
A2213 30558-43-1 0.042; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
U395
Diethylene glycol, dicarbamate.10U404
Diethylene glycol, dicarbamate 5952-26-1 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Triethylamine.10U409
Triethylamine 121-44-8 0.081; or CMBST, CHOXD, BIODG or CARBN 1.5; or CMBST
Thiophanate-methyl.10U410
Thiophanate-methyl 23564-05-8 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Thiodicarb.10U411
Thiodicarb 59669-26-0 0.019; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST
Propoxur.10Notes:
Propoxur 114-26-1 0.056; or CMBST, CHOXD, BIODG or CARBN 1.4; or CMBST 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)
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.
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 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)