721.101 | Purpose and Scope |
721.102 | Definition of Solid Waste |
721.103 | Definition of Hazardous Waste |
721.104 | Exclusions |
721.105 | Special Requirements for Hazardous Waste Generated by Small Quantity Generators (Repealed) |
721.106 | Requirements for Recyclable Materials |
721.107 | Residues of Hazardous Waste in Empty Containers |
721.108 | PCB Wastes Regulated under TSCA |
721.109 | Requirements for Universal Waste |
SUBPART B: CRITERIA FOR IDENTIFYING THE CHARACTERISTICS OF HAZARDOUS WASTE AND FOR LISTING HAZARDOUS WASTES
721.110 | Criteria for Identifying the Characteristics of Hazardous Waste |
721.111 | Criteria for Listing Hazardous Waste |
SUBPART C: CHARACTERISTICS OF HAZARDOUS WASTE
721.120 | General |
721.121 | Characteristic of Ignitability |
721.122 | Characteristic of Corrosivity |
721.123 | Characteristic of Reactivity |
721.124 | Toxicity Characteristic |
SUBPART D: LISTS OF HAZARDOUS WASTE
721.130 | General |
721.131 | Hazardous Wastes from Nonspecific Sources |
721.132 | Hazardous Waste from Specific Sources |
721.133 | Discarded Commercial Chemical Products, Off-Specification Species, Container Residues, and Spill Residues Thereof |
721.135 | Wood Preserving Wastes |
SUBPART E: EXCLUSIONS AND EXEMPTIONS
721.138 | Exclusion of Comparable Fuel and Syngas Fuel (Repealed) |
721.139 | Conditional Exclusion for Used, Broken CRTs and Processed CRT Glass Undergoing Recycling |
721.140 | Conditional Exclusion for Used, Intact CRTs Exported for Recycling |
721.141 | Notification and Recordkeeping for Used, Intact CRTs Exported for Reuse |
SUBPART H: FINANCIAL REQUIREMENTS FOR MANAGEMENT OF EXCLUDED HAZARDOUS SECONDARY MATERIALS
721.240 | Applicability |
721.241 | Definitions of Terms as Used in This Subpart |
721.242 | Cost Estimate |
721.243 | Financial Assurance Condition |
721.247 | Liability Requirements |
721.248 | Incapacity of Owners or Operators, Guarantors, or Financial Institutions |
721.249 | Use of State-Required Mechanisms |
721.250 | State Assumption of Responsibility |
721.251 | Wording of the Instruments |
SUBPART I: USE AND MANAGEMENT OF CONTAINERS
Section | |
721.270 | Applicability |
721.271 | Condition of Containers |
721.272 | Compatibility of Hazardous Secondary Materials with Containers |
721.273 | Management of Containers |
721.275 | Secondary Containment |
721.276 | Special Requirements for Ignitable or Reactive Hazardous Secondary Material |
721.277 | Special Requirements for Incompatible Materials |
721.279 | Air Emission Standards |
SUBPART J: TANK SYSTEMS
Section | |
721.290 | Applicability |
721.291 | Assessment of Existing Tank System’s Integrity |
721.293 | Containment and Detection of Releases |
721.294 | General Operating Requirements |
721.296 | Response to Leaks or Spills and Disposition of Leaking or Unfit-for-Use Tank Systems |
721.297 | Termination of Remanufacturing Exclusion |
721.298 | Special Requirements for Ignitable or Reactive Materials |
721.299 | Special Requirements for Incompatible Materials |
721.300 | Air Emission Standards |
SUBPART M: EMERGENCY PREPAREDNESS AND RESPONSE FOR MANAGEMENT OF EXCLUDED HAZARDOUS SECONDARY MATERIALS
Section | |
721.500 | Applicability |
721.510 | Preparedness and Prevention |
721.511 | Emergency Procedures for Facilities Generating or Accumulating 6,000 kg or Less of Hazardous Secondary Material |
721.520 | Contingency Planning and Emergency Procedures for Facilities Generating or Accumulating More Than 6,000 kg of Hazardous Secondary Material |
SUBPART AA: AIR EMISSION STANDARDS FOR PROCESS VENTS
Section | |
721.930 | |
Applicability | |
721.931 | |
Definitions | |
721.932 | |
Standards: Process Vents | |
721.933 | |
Standards: Closed-Vent Systems and Control Devices | |
721.934 | |
Test Methods and Procedures |
SUBPART BB: AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS
Section | |
721.950 | Applicability |
721.951 | Definitions |
721.952 | Standards: Pumps in Light Liquid Service |
721.953 | Standards: Compressors |
721.954 | Standards: Pressure Relief Devices in Gas/Vapor Service |
721.955 | Standards: Sampling Connection Systems |
721.956 | Standards: Open-Ended Valves or Lines |
721.957 | Standards: Valves in gas/Vapor Service or in Light Liquid Service |
721.958 | Standards: Pumps and Valves in Heavy Liquid Service, Pressure Relief Devices in Light Liquid or Heavy Liquid Service, and Flanges and Other Connectors |
721.959 | Standards: Delay of Repair |
721.960 | Standards: Closed-Vent Systems and Control Devices |
721.961 | Alternative Standards for Valves in Gas/Vapor Service or in Light Liquid Service: Percentage of Valves Allowed to Leak |
721.962 | Alternative Standards for Valves in Gas/Vapor Service or in Light Liquid Service: Skip Period Leak Detection and Repair |
721.963 | Test Methods and Procedures |
721.964 | Recordkeeping Requirements |
SUBPART CC: AIR EMISSION STANDARDS FOR TANKS AND CONTAINERS
721.APPENDIX A | Representative Sampling Methods |
721.APPENDIX B | |
Method 1311 Toxicity Characteristic Leaching Procedure (TCLP) (Repealed) | |
721.APPENDIX C | |
Chemical Analysis Test Methods (Repealed) | |
721.TABLE A | Analytical Characteristics of Organic Chemicals (Repealed) |
721.TABLE B | Analytical Characteristics of Inorganic Species (Repealed) |
721.TABLE C | Sample Preparation/Sample Introduction Techniques (Repealed) |
721.APPENDIX G | |
Basis for Listing Hazardous Wastes | |
721.APPENDIX H | |
Hazardous Constituents | |
721.APPENDIX I | Wastes Excluded by Administrative Action |
721.TABLE A | Wastes Excluded by USEPA pursuant to 40 CFR 260.20 and 260.22 from Non-Specific Sources |
721.TABLE B | Wastes Excluded by USEPA pursuant to 40 CFR 260.20 and 260.22 from Specific Sources |
721.TABLE C | Wastes Excluded by USEPA pursuant to 40 CFR 260.20 and 260.22 from Commercial Chemical Products, Off-Specification Species, Container Residues, and Soil Residues Thereof |
721.TABLE D | Wastes Excluded by the Board by Adjusted Standard |
721.APPENDIX J | Method of Analysis for Chlorinated Dibenzo-p-Dioxins and Dibenzofurans (Repealed) |
721.APPENDIX Y | |
Table to Section 721.138: Maximum Contaminant Concentration and Minimum Detection Limit Values for Comparable Fuel Specification (Repealed) | |
721.APPENDIX Z | |
Table to Section 721.102: Recycled Materials that Are Solid Waste |
AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].
SOURCE: Adopted in R81-22 at 5 Ill. Reg. 9781, effective May 17, 1982; amended and codified in R81-22 at 6 Ill. Reg. 4828, effective May 17, 1982; amended in R82-18 at 7 Ill. Reg. 2518, effective February 22, 1983; amended in R82-19 at 7 Ill. Reg. 13999, effective October 12, 1983; amended in R84-34, 61 at 8 Ill. Reg. 24562, effective December 11, 1984; amended in R84-9 at 9 Ill. Reg. 11834, effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 998, effective January 2, 1986; amended in R85-2 at 10 Ill. Reg. 8112, effective May 2, 1986; amended in R86-1 at 10 Ill. Reg. 14002, effective August 12, 1986; amended in R86-19 at 10 Ill. Reg. 20647, effective December 2, 1986; amended in R86-28 at 11 Ill. Reg. 6035, effective March 24, 1987; amended in R86-46 at 11 Ill. Reg. 13466, effective August 4, 1987; amended in R87-32 at 11 Ill. Reg. 16698, effective September 30, 1987; amended in R87-5 at 11 Ill. Reg. 19303, effective November 12, 1987; amended in R87-26 at 12 Ill. Reg. 2456, effective January 15, 1988; amended in R87-30 at 12 Ill. Reg. 12070, effective July 12, 1988; amended in R87-39 at 12 Ill. Reg. 13006, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 382, effective December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18300, effective November 13, 1989; amended in R90-2 at 14 Ill. Reg. 14401, effective August 22, 1990; amended in R90-10 at 14 Ill. Reg. 16472, effective September 25, 1990; amended in R90-17 at 15 Ill. Reg. 7950, effective May 9, 1991; amended in R90-11 at 15 Ill. Reg. 9332, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14473, effective September 30, 1991; amended in R91-12 at 16 Ill. Reg. 2155, effective January 27, 1992; amended in R91-26 at 16 Ill. Reg. 2600, effective February 3, 1992; amended in R91-13 at 16 Ill. Reg. 9519, effective June 9, 1992; amended in R92-1 at 16 Ill. Reg. 17666, effective November 6, 1992; amended in R92-10 at 17 Ill. Reg. 5650, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20568, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6741, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12175, effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17490, effective November 23, 1994; amended in R95-6 at 19 Ill. Reg. 9522, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 10963, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 275, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7615, effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17531, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1718, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9135, effective July 26, 1999; amended in R00-13 at 24 Ill. Reg. 9481, effective June 20, 2000; amended in R01-3 at 25 Ill. Reg. 1281, effective January 11, 2001; amended in R01-21/R01-23 at 25 Ill. Reg. 9108, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. 6584, effective April 22, 2002; amended in R03-18 at 27 Ill. Reg. 12760, effective July 17, 2003; amended in R04-16 at 28 Ill. Reg. 10693, effective July 19, 2004; amended in R05-8 at 29 Ill. Reg. 6003, effective April 13, 2005; amended in R06-5/R06-6/R06-7 at 30 Ill. Reg. 2992, effective February 23, 2006; amended in R06-16/R06-17/R06-18 at 31 Ill. Reg. 791, effective December 20, 2006; amended in R07-5/R07-14 at 32 Ill. Reg. 11786, effective July 14, 2008; amended in R09-3 at 33 Ill. Reg. 986, effective December 30, 2008; amended in R09-16/R10-4 at 34 Ill. Reg. 18611, effective November 12, 2010; amended in R11-2/R11-16 at 35 Ill. Reg. 17734, effective October 14, 2011; amended in R13-5 at 37 Ill. Reg. 3213, effective March 4, 2013; amended in R14-13 at 38 Ill. Reg. 12442, effective May 27, 2014; amended in R15-1 at 39 Ill. Reg. 1607, effective January 12, 2015; amended in R16-7 at 40 Ill. Reg. 11367, effective August 9, 2016; amended in R17-14/R17-15/R18-12/R18-31 at 42 Ill. Reg. 21673, effective November 19, 2018; amended in R19-3 at 43 Ill. Reg. 496, effective December 6, 2018; amended in R19-11 at 43 Ill. Reg. 5884, effective May 2, 2019; amended in R20-8/R20-16 at 44 Ill. Reg. ________, effective September 3, 2020.
Section 721.101 Purpose and Scope |
a) | This Part identifies those solid wastes that are subject to regulation as hazardous wastes under 35 Ill. Adm. Code 702, 703, and 722 through 728, and which are subject to the notification requirements of Section 3010 of the Resource Conservation and Recovery Act (RCRA) (42 USC 6901 et seq.). In this Part: |
1) | Subpart A of this Part defines the terms “solid waste” and “hazardous waste,” identifies those wastes that are excluded from regulation under 35 Ill. Adm. Code 702, 703, and 722 through 728, and establishes special management requirements for hazardous waste produced by conditionally exempt small quantity generators and hazardous waste that is recycled. |
2) | Subpart B of this Part sets forth the criteria used to identify characteristics of hazardous waste and to list particular hazardous wastes. |
3) | Subpart C of this Part identifies characteristics of hazardous wastes. |
4) | Subpart D of this Part lists particular hazardous wastes. |
b) | Limitations on definition of solid waste. |
1) | The definition of solid waste contained in this Part applies only to wastes that also are hazardous for purposes of the regulations implementing Subtitle C of RCRA. For example, it does not apply to materials (such as non-hazardous scrap, paper, textiles or rubber) that are not otherwise hazardous wastes and that are recycled. |
2) | This Part identifies only some of the materials that are solid wastes and hazardous wastes under Sections 1004(5), 1004(27) and 7003 of RCRA. A material that is not defined as a solid waste in this Part, or is not a hazardous waste identified or listed in this Part, is still a hazardous waste for purposes of those Sections if, in the case of Section 7003 of RCRA, the statutory elements are established. |
c) | For the purposes of Sections 721.102 and 721.106 the following definitions apply: |
1) | A “spent material” is any material that has been used and as a result of contamination can no longer serve the purpose for which it was produced without processing. |
2) | “Sludge” has the same meaning used in 35 Ill. Adm. Code 720.110. |
3) | A “by-product” is a material that is not one of the primary products of a production process and is not solely or separately produced by the production process. Examples are process residues such as slags or distillation column bottoms. The term does not include a co-product that is produced for the general public’s use and is ordinarily used in the form it is produced by the process. |
4) | A material is “reclaimed” if it is processed to recover a usable product, or if it is regenerated. Examples are recovery of lead values from spent batteries and regeneration of spent solvents. In addition, for purposes of Sections 721.102(a)(2)(B) and 721.104(a)(23) and (a)(24) smelting, melting, and refining furnaces are considered to be solely engaged in metals reclamation if the metal recovery from the hazardous secondary materials meets the same requirements as those specified for metals recovery from hazardous waste found in 35 Ill. Adm. Code 726.200(d)(1) through (d)(3), and if the residuals meet the requirements specified in 35 Ill. Adm. Code 726.212. |
5) | A material is “used or reused” if either of the following is true: |
A) | It is employed as an ingredient (including use as an intermediate) in an industrial process to make a product (for example, distillation bottoms from one process used as feedstock in another process). However, a material will not satisfy this condition if distinct components of the material are recovered as separate end products (as when metals are recovered from metal-containing secondary materials); or |
B) | It is employed in a particular function or application as an effective substitute for a commercial product (for example, spent pickle liquor used as phosphorus precipitant and sludge conditioner in wastewater treatment). |
6) | “Scrap metal” is bits and pieces of metal parts (e.g., bars, turnings, rods, sheets, or wire) or metal pieces that may be combined together with bolts or soldering (e.g., radiators, scrap automobiles, or railroad box cars) that when worn or superfluous can be recycled. |
7) | A material is “recycled” if it is used, reused, or reclaimed. |
8) | A material is “accumulated speculatively” if it is accumulated before being recycled. A material is not accumulated speculatively, however, if the person accumulating it can show that the material is potentially recyclable and has a feasible means of being recycled; and that, during the calendar year (commencing on January 1), the amount of material that is recycled, or transferred to a different site for recycling, equals at least 75 percent by weight or volume of the amount of that material accumulated at the beginning of the period. In calculating the percentage of turnover, the 75 percent requirement is to be applied to each material of the same type (e.g., slags from a single smelting process) that is recycled in the same way (i.e., from which the same material is recovered or that is used in the same way). Materials accumulating in units that would be exempt from regulation under Section 721.104(c) are not to be included in making the calculation. (Materials that are already defined as solid wastes also are not to be included in making the calculation.) Materials are no longer in this category once they are removed from accumulation for recycling, however. |
9) | “Excluded scrap metal” is processed scrap metal, unprocessed home scrap metal, and unprocessed prompt scrap metal. |
10) | “Processed scrap metal” is scrap metal that has been manually or physically altered to either separate it into distinct materials to enhance economic value or to improve the handling of materials. Processed scrap metal includes, but is not limited to, scrap metal that has been baled, shredded, sheared, chopped, crushed, flattened, cut, melted, or separated by metal type (i.e., sorted), and fines, drosses and related materials that have been agglomerated. (Note: shredded circuit boards being sent for recycling are not considered processed scrap metal. They are covered under the exclusion from the definition of solid waste for shredded circuit boards being recycled (Section 721.104(a)(14))). |
11) | “Home scrap metal” is scrap metal as generated by steel mills, foundries, and refineries, such as turnings, cuttings, punchings, and borings. |
12) | “Prompt scrap metal” is scrap metal as generated by the metal working/fabrication industries, and it includes such scrap metal as turnings, cuttings, punchings, and borings. Prompt scrap metal is also known as industrial or new scrap metal. |
d) | The Agency has inspection authority pursuant to Section 3007 of RCRA and Section 4 of the Environmental Protection Act [415 ILCS 5/4]. |
e) | 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. |
a) | Solid waste. |
1) | A solid waste is any discarded material that is not excluded pursuant to Section 721.104(a) or that is not excluded pursuant to 35 Ill. Adm. Code 720.130 and 720.131 or 35 Ill. Adm. Code 720.130 and 720.134. |
2) | Discarded material. |
i) | It is abandoned, as described in subsection (b) of this Section; |
ii) | It is recycled, as described in subsection (c) of this Section; |
iii) | It is considered inherently waste-like, as described in subsection (d) of this Section; or |
iv) | It is a military munition identified as a solid waste in 35 Ill. Adm. Code 726.302. |
B) | A hazardous secondary material is not discarded if each of the following is true with respect to the waste: |
i) | It is generated and reclaimed under the control of the generator, as defined in 35 Ill. Adm. Code 720.110; |
ii) | It is not speculatively accumulated, as defined in Section 721.101(c)(8); |
iii) | It is handled only in non-land-based units and is contained in such units; |
iv) | It is generated and reclaimed within the United States and its territories; |
v) | It is not otherwise subject to material-specific management conditions pursuant to Section 721.104(a) when reclaimed; |
vi) | It is not a spent lead acid battery (see 35 Ill. Adm. Code 726.180 and 733.102); |
vii) | It does not meet either of the listing descriptions for K171 or K172 waste in Section 721.132; and |
viii) | The reclamation of the material is legitimate, as determined pursuant to 35 Ill. Adm. Code 720.143. |
b) | A material is a solid waste if it is abandoned in one of the following ways: |
1) | It is disposed of; |
2) | It is burned or incinerated; or |
3) | It is accumulated, stored, or treated (but not recycled) before or in lieu of being abandoned by being disposed of, burned, or incinerated. |
c) | A material is a solid waste if it is recycled—or accumulated, stored, or treated before recycling—as specified in subsections (c)(1) through (c)(4) of this Section, if one of the following occurs with regard to the material: |
1) | The material is used in a manner constituting disposal. |
A) | A material that is noted with a “yes” in column 1 of the table in Appendix Z of this Part is a solid waste when one of the following occurs: |
i) | The material is applied to or placed on the land in a manner that constitutes disposal; or |
ii) | The material is used to produce products that are applied to or placed on the land or are otherwise contained in products that are applied to or placed on the land (in which cases the product itself remains a solid waste). |
B) | However, a commercial chemical product that is listed in Section 721.133 is not a solid waste if it is applied to the land and that is its ordinary manner of use. |
2) | The material is burned for energy recovery. |
A) | A material that is noted with a “yes” in column 2 of the table in Appendix Z of this Part is a solid waste when one of the following occurs: |
i) | It is burned to recover energy; |
ii) | It is used to produce a fuel or is otherwise contained in fuels (in which case the fuel itself remains a solid waste); |
iii) | It is contained in fuels (in which case the fuel itself remains a solid waste). |
B) | However, a commercial chemical product that is listed in Section 721.133 is not a solid waste if it is itself a fuel. |
3) | Reclaimed. A material noted with a “No“ in column 3 of the table in Appendix Z of this Part is not a solid waste when reclaimed (except as provided under Section 721.104(a)(17)). A material noted with a “Yes” in column 3 of Appendix Z of this Part is a solid waste when reclaimed, unless it meets the requirements of Section 721.102(a)(2)(B) or 721.104(a)(17), (a)(23), (a)(24), or (a)(25). |
4) | Accumulated speculatively. A material noted with “yes” in column 4 of the table in Appendix Z of this Part is a solid waste when accumulated speculatively. |
d) | Inherently waste-like materials. The following materials are solid wastes when they are recycled in any manner: |
1) | Hazardous waste numbers F020, F021 (unless used as an ingredient to make a product at the site of generation), F022, F023, F026, and F028. |
2) | A secondary material fed to a halogen acid furnace that exhibits a characteristic of a hazardous waste or which is listed as a hazardous waste, as defined in Subpart C or D of this Part, except for brominated material that meets the following criteria: |
A) | The material must contain a bromine concentration of at least 45 percent; |
B) | The material must contain less than a total of one percent of toxic organic compounds listed in Appendix H of this Part; and |
C) | The material is processed continually on-site in the halogen acid furnace via direct conveyance (hard piping). |
3) | The following criteria are used to add wastes to the list: |
A) | Disposal method or toxicity. |
i) | The material is ordinarily disposed of, burned, or incinerated; or |
ii) | The material contains toxic constituents listed in Appendix H of this Part and these constituents are not ordinarily found in raw materials or products for which the material substitutes (or are found in raw materials or products in smaller concentrations) and is not used or reused during the recycling process; and |
B) | The material may pose a substantial hazard to human health and the environment when recycled. |
e) | Materials that are not solid waste when recycled. |
1) | A material is not a solid waste when it can be shown to be recycled by fulfilling one of the following conditions: |
A) | It is used or reused as an ingredient in an industrial process to make a product, provided the material is not being reclaimed; or |
B) | It is used or reused as effective substitutes for commercial products; or |
C) | It is returned to the original process from which it is generated, without first being reclaimed or land disposed. The material must be returned as a substitute for feedstock materials. In cases where the original process to which the material is returned is a secondary process, the material must be managed in such a manner that there is no placement on the land. In cases where the material is generated and reclaimed within the primary mineral processing industry, the conditions of the exclusion found at Section 721.104(a)(17) apply rather than this provision. |
2) | The following materials are solid wastes, even if the recycling involves use, reuse, or return to the original process (described in subsections (e)(1)(A) through (e)(1)(C) of this Section): |
A) | A material used in a manner constituting disposal or used to produce a product that is applied to the land; or |
B) | A material burned for energy recovery, used to produce a fuel, or contained in fuels; or |
C) | A material accumulated speculatively; or |
D) | A material listed in subsections (d)(1) and (d)(2) of this Section. |
f) | Documentation of claims that a material is not a solid waste or is conditionally exempt from regulation. A respondent in an action to enforce regulations implementing Subtitle C of RCRA or Section 21 of the Environmental Protection Act that raises a claim that a certain material is not a solid waste or that the material is conditionally exempt from regulation must demonstrate that there is a known market or disposition for the material and that the material meets the terms of the exclusion or exemption. In doing so, the person must provide appropriate documentation (such as contracts showing that a second person uses the material as an ingredient in a production process) to demonstrate that the material is not a waste or that the material is exempt from regulation. In addition, an owner or operator of a facility claiming that it actually is recycling a material must show that it has the necessary equipment to recycle that material. |
a) | A solid waste, as defined in Section 721.102, is a hazardous waste if the following is true of the waste: |
1) | It is not excluded from regulation as a hazardous waste pursuant to Section 721.104(b); and |
2) | It meets any of the following criteria: |
A) | It exhibits any of the characteristics of hazardous waste identified in Subpart C of this Part. However, any mixture of a waste from the extraction, beneficiation, and processing of ores and minerals excluded pursuant to Section 721.104(b)(7) and any other solid waste exhibiting a characteristic of hazardous waste pursuant to Subpart C of this Part is a hazardous waste only if it exhibits a characteristic that would not have been exhibited by the excluded waste alone if such mixture had not occurred, or if the mixture continues to exhibit any of the characteristics exhibited by the non-excluded wastes prior to mixture. Further, for the purposes of applying the toxicity characteristic to such mixtures, the mixture is also a hazardous waste if it exceeds the maximum concentration for any contaminant listed in Section 721.124 that would not have been exceeded by the excluded waste alone if the mixture had not occurred or if it continues to exceed the maximum concentration for any contaminant exceeded by the nonexempt waste prior to mixture. |
B) | It is listed in Subpart D of this Part and has not been excluded from the lists in Subpart D of this Part pursuant to 35 Ill. Adm. Code 720.120 and 720.122. |
C) | This subsection (a)(2)(B) corresponds with 40 CFR 261.3(a)(2)(iii), which USEPA removed and marked as “reserved” at 66 Fed. Reg. 27266 (May 16, 2001). This statement maintains structural consistency with the federal regulations. |
D) | It is a mixture of solid waste and one or more hazardous wastes listed in Subpart D of this Part and has not been excluded from this subsection (a)(2) pursuant to 35 Ill. Adm. Code 720.120 and 720.122, subsection (g) of this Section, or subsection (h) of this Section; however, the following mixtures of solid wastes and hazardous wastes listed in Subpart D of this Part are not hazardous wastes (except by application of subsection (a)(2)(A) or (a)(2)(B) of this Section) if the generator demonstrates that the mixture consists of wastewater the discharge of which is subject to regulation under either 35 Ill. Adm. Code 309 or 310 (including wastewater at facilities that have eliminated the discharge of wastewater) and the following is true of the waste: |
i) | It is one or more of the following solvents listed in Section 721.131: benzene, carbon tetrachloride, tetrachloroethylene, trichloroethylene or the scrubber waters derived from the combustion of these spent solvents, provided that the maximum total weekly usage of these solvents (other than the amounts that can be demonstrated not to be discharged to wastewater) divided by the average weekly flow of wastewater into the headworks of the facility’s wastewater treatment or pretreatment system does not exceed 1 part per million, or the total measured concentration of these solvents entering the headworks of the facility’s wastewater treatment system (at a facility that is subject to regulation under the federal Clean Air Act new source performance standards or national emission standards for hazardous air pollutants of 40 CFR 60, 61, or 63 or at a facility that is subject to an enforceable limit in a federal operating permit that minimizes fugitive emissions) does not exceed 1 part per million on an average weekly basis. Any facility that uses benzene as a solvent and claims this exemption must use an aerated biological wastewater treatment system and must use only lined surface impoundments or tanks prior to secondary clarification in the wastewater treatment system. A facility that chooses to measure concentration levels must file a copy of its sampling and analysis plan with the Agency. A facility must file a copy of a revised sampling and analysis plan only if the initial plan is rendered inaccurate by changes in the facility’s operations. The sampling and analysis plan must include the monitoring point location (headworks), the sampling frequency and methodology, and a list of constituents to be monitored. A facility is eligible for the direct monitoring option once it receives confirmation that the sampling and analysis plan has been received by the Agency. The Agency must reject the sampling and analysis plan if it determines that the sampling and analysis plan fails to include the information required by this subsection (a)(2)(D)(i) or that the plan parameters would not enable the facility to calculate the weekly average concentration of these chemicals accurately. If the Agency rejects the sampling and analysis plan, or if the Agency determines that the facility is not following the sampling and analysis plan, the Agency must notify the facility to cease the use of the direct monitoring option until such time as the bases for rejection are corrected; |
ii) | It is one or more of the following spent solvents listed in Section 721.131: methylene chloride, 1,1,1-trichloroethane, chlorobenzene, o-dichlorobenzene, cresols, cresylic acid, nitrobenzene, toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, spent chlorofluorocarbon solvents, 2- ethoxyethanol, or the scrubber waters derived-from the combustion of these spent solvents, provided that the maximum total weekly usage of these solvents (other than the amounts that can be demonstrated not to be discharged to wastewater) divided by the average weekly flow of wastewater into the headworks of the facility’s wastewater treatment or pretreatment system does not exceed 25 parts per million, or the total measured concentration of these solvents entering the headworks of the facility’s wastewater treatment system (at a facility that is subject to regulation under the federal Clean Air Act new source performance standards or national emission standards for hazardous air pollutants of 40 CFR 60, 61, or 63 or at a facility that is subject to an enforceable limit in a federal operating permit that minimizes fugitive emissions) does not exceed 25 parts per million on an average weekly basis. A facility that chooses to measure concentration levels must file a copy of its sampling and analysis plan with the Agency. A facility must file a copy of a revised sampling and analysis plan only if the initial plan is rendered inaccurate by changes in the facility’s operations. The sampling and analysis plan must include the monitoring point location (headworks), the sampling frequency and methodology, and a list of constituents to be monitored. A facility is eligible for the direct monitoring option once it receives confirmation that the sampling and analysis plan has been received by the Agency. The Agency must reject the sampling and analysis plan if it determines that the sampling and analysis plan fails to include the information required by this subsection (a)(2)(D)(ii) or that the plan parameters would not enable the facility to calculate the weekly average concentration of these chemicals accurately. If the Agency rejects the sampling and analysis plan, or if the Agency determines that the facility is not following the sampling and analysis plan, the Agency must notify the facility to cease the use of the direct monitoring option until such time as the bases for rejection are corrected; |
iii) | It is one of the following wastes listed in Section 721.132, provided that the wastes are discharged to the refinery oil recovery sewer before primary oil/water/solids separation: heat exchanger bundle cleaning sludge from the petroleum refining industry (USEPA hazardous waste number K050), crude oil storage tank sediment from petroleum refining operations (USEPA hazardous waste number K169), clarified slurry oil tank sediment or in-line filter/separation solids from petroleum refining operations (USEPA hazardous waste number K170), spent hydrotreating catalyst (USEPA hazardous waste number K171), and spent hydrorefining catalyst (USEPA hazardous waste number K172); |
iv) | It is a discarded hazardous waste, commercial chemical product or chemical intermediate listed in Section 721.121, 721.132, or 721.133 arising from de minimis losses of these materials. For purposes of this subsection (a)(2)(D)(iv), “de minimis” losses are inadvertent releases to a wastewater treatment system, including those from normal material handling operations (e.g., spills from the unloading or transfer of materials from bins or other containers, leaks from pipes, valves, or other devices used to transfer materials); minor leaks of process equipment, storage tanks, or containers; leaks from well-maintained pump packings and seals; sample purgings; relief device discharges; discharges from safety showers and rinsing and cleaning of personal safety equipment; and rinsate from empty containers or from containers that are rendered empty by that rinsing. Any manufacturing facility that claims an exemption for de minimis quantities of a waste listed in Section 721.131 or 721.132, or any nonmanufacturing facility that claims an exemption for de minimis quantities of wastes listed in Subpart D of this Part, must either have eliminated the discharge of wastewaters or have included in its federal Clean Water Act (33 USC 1251 et seq.) permit application or wastewater pretreatment submission to the Agency or the wastewater pretreatment Control Authority pursuant to 35 Ill. Adm. Code 307 of the constituents for which each waste was listed (in Appendix G of this Part); and the constituents in Table T to 35 Ill. Adm. Code 728 for which each waste has a treatment standard ( i.e. , land disposal restriction constituents). A facility is eligible to claim the exemption once the Agency or Control Authority has been notified of possible de minimis releases via the Clean Water Act permit application or the wastewater pretreatment submission. A copy of the Clean Water Act permit application or the wastewater pretreatment submission must be placed in the facility’s on-site files; |
v) | It is wastewater resulting from laboratory operations containing toxic (T) wastes listed in Subpart D of this Part, provided that the annualized average flow of laboratory wastewater does not exceed one percent of total wastewater flow into the headworks of the facility’s wastewater treatment or pretreatment system or provided that the wastes’ combined annualized average concentration does not exceed one part per million in the headworks of the facility’s wastewater treatment or pretreatment facility. Toxic (T) wastes used in laboratories that are demonstrated not to be discharged to wastewater are not to be included in this calculation; |
vi) | It is one or more of the following wastes listed in Section 721.132: wastewaters from the production of carbamates and carbamoyl oximes (USEPA hazardous waste number K157), provided that the maximum weekly usage of formaldehyde, methyl chloride, methylene chloride, and triethylamine (including all amounts that cannot be demonstrated to be reacted in the process, destroyed through treatment, or recovered, i.e., what is discharged or volatilized) divided by the average weekly flow of process wastewater prior to any dilutions into the headworks of the facility’s wastewater treatment system does not exceed a total of 5 parts per million by weight, or the total measured concentration of these chemicals entering the headworks of the facility’s wastewater treatment system (at a facility that is subject to regulation under the federal Clean Air Act new source performance standards or national emission standards for hazardous air pollutants of 40 CFR 60, 61, or 63 or at a facility that is subject to an enforceable limit in a federal operating permit that minimizes fugitive emissions) does not exceed 5 parts per million on an average weekly basis. A facility that chooses to measure concentration levels must file a copy of its sampling and analysis plan with the Agency. A facility must file a copy of a revised sampling and analysis plan only if the initial plan is rendered inaccurate by changes in the facility’s operations. The sampling and analysis plan must include the monitoring point location (headworks), the sampling frequency and methodology, and a list of constituents to be monitored. A facility is eligible for the direct monitoring option once it receives confirmation that the sampling and analysis plan has been received by the Agency. The Agency must reject the sampling and analysis plan if it determines that the sampling and analysis plan fails to include the information required by this subsection (a)(2)(D)(vi) or that the plan parameters would not enable the facility to calculate the weekly average concentration of these chemicals accurately. If the Agency rejects the sampling and analysis plan, or if the Agency determines that the facility is not following the sampling and analysis plan, the Agency must notify the facility to cease the use of the direct monitoring option until such time as the bases for rejection are corrected; or |
vii) | It is wastewater derived from the treatment of one or more of the following wastes listed in Section 721.132: organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes (USEPA hazardous waste number K156), provided that the maximum concentration of formaldehyde, methyl chloride, methylene chloride, and triethylamine prior to any dilutions into the headworks of the facility’s wastewater treatment system does not exceed a total of 5 milligrams per liter, or the total measured concentration of these chemicals entering the headworks of the facility’s wastewater treatment system (at a facility that is subject to regulation under the federal Clean Air Act new source performance standards or national emission standards for hazardous air pollutants of 40 CFR 60, 61, or 63 or at a facility that is subject to an enforceable limit in a federal operating permit that minimizes fugitive emissions) does not exceed 5 milligrams per liter on an average weekly basis. A facility that chooses to measure concentration levels must file a copy of its sampling and analysis plan with the Agency. A facility must file a copy of a revised sampling and analysis plan only if the initial plan is rendered inaccurate by changes in the facility’s operations. The sampling and analysis plan must include the monitoring point location (headworks), the sampling frequency and methodology, and a list of constituents to be monitored. A facility is eligible for the direct monitoring option once it receives confirmation that the sampling and analysis plan has been received by the Agency. The Agency must reject the sampling and analysis plan if it determines that the sampling and analysis plan fails to include the information required by this subsection (a)(2)(D)(vii) or that the plan parameters would not enable the facility to calculate the weekly average concentration of these chemicals accurately. If the Agency rejects the sampling and analysis plan, or if the Agency determines that the facility is not following the sampling and analysis plan, the Agency must notify the facility to cease the use of the direct monitoring option until such time as the bases for rejection are corrected. |
E) | Rebuttable presumption for used oil. Used oil containing more than 1,000 ppm total halogens is presumed to be a hazardous waste because it has been mixed with halogenated hazardous waste listed in Subpart D of this Part. Persons may rebut this presumption by demonstrating that the used oil does not contain hazardous waste (for example, to show that the used oil does not contain significant concentrations of halogenated hazardous constituents listed in Appendix H of this Part). |
i) | The rebuttable presumption does not apply to a metalworking oil or fluid containing chlorinated paraffins if it is processed through a tolling arrangement, as described in 35 Ill. Adm. Code 739.124(c), to reclaim metalworking oils or fluids. The presumption does apply to a metalworking oil or fluid if such an oil or fluid is recycled in any other manner, or disposed of. |
ii) | The rebuttable presumption does not apply to a used oil contaminated with chlorofluorocarbons (CFCs) removed from refrigeration units where the CFCs are destined for reclamation. The rebuttable presumption does apply to a used oil contaminated with CFCs that have been mixed with used oil from a source other than a refrigeration unit. |
b) | A solid waste that is not excluded from regulation pursuant to subsection (a)(1) of this Section becomes a hazardous waste when any of the following events occur: |
1) | In the case of a waste listed in Subpart D of this Part, when the waste first meets the listing description set forth in Subpart D of this Part. |
2) | In the case of a mixture of solid waste and one or more listed hazardous wastes, when a hazardous waste listed in Subpart D of this Part is first added to the solid waste. |
3) | In the case of any other waste (including a waste mixture), when the waste exhibits any of the characteristics identified in Subpart C of this Part. |
c) | Unless and until it meets the criteria of subsection (e) of this Section, a hazardous waste will remain a hazardous waste. |
d) | Any solid waste described in subsection (e) of this Section is not a hazardous waste if it meets the following criteria: |
1) | In the case of any solid waste, it does not exhibit any of the characteristics of hazardous waste identified in Subpart C of this Part. (However, wastes that exhibit a characteristic at the point of generation may still be subject to 35 Ill. Adm. Code 728, even if they no longer exhibit a characteristic at the point of land disposal.) |
2) | In the case of a waste that is a listed waste pursuant to Subpart D of this Part, a waste that contains a waste listed pursuant to Subpart D of this Part, or a waste that is derived from a waste listed in Subpart D of this Part, it also has been excluded from subsection (e) of this Section pursuant to 35 Ill. Adm. Code 720.120 and 720.122. |
e) | Specific inclusions and exclusions. |
1) | Except as otherwise provided in subsection (e)(2), (g), or (h) of this Section, any solid waste generated from the treatment, storage, or disposal of a hazardous waste, including any sludge, spill residue, ash, emission control dust, or leachate (but not including precipitation run-off), is a hazardous waste. (However, materials that are reclaimed from solid wastes and that are used beneficially are not solid wastes and hence are not hazardous wastes under this provision unless the reclaimed material is burned for energy recovery or used in a manner constituting disposal.) |
2) | The following solid wastes are not hazardous even though they are generated from the treatment, storage, or disposal of a hazardous waste, unless they exhibit one or more of the characteristics of hazardous waste: |
A) | Waste pickle liquor sludge generated by lime stabilization of spent pickle liquor from the iron and steel industry (SIC Codes 331 and 332). |
B) | Wastes from burning any of the materials exempted from regulation by Section 721.106(a)(3)(C) and (a)(3)(D). |
C) | Nonwastewater residues, such as slag, resulting from high temperature metal recovery (HTMR) processing of K061, K062, or F006 waste in the units identified in this subsection (e)(2) that are disposed of in non-hazardous waste units, provided that these residues meet the generic exclusion levels identified in the tables in this subsection (e)(2)(C) for all constituents and the residues exhibit no characteristics of hazardous waste. The types of units identified are rotary kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors, rotary hearth furnace/electric furnace combinations, or the following types of industrial furnaces (as defined in 35 Ill. Adm. Code 720.110): blast furnaces; smelting, melting, and refining furnaces (including pyrometallurgical devices such as cupolas, reverberator furnaces, sintering machines, roasters, and foundry furnaces); and other furnaces designated by the Agency pursuant to that definition. |
i) | Testing requirements must be incorporated in a facility’s waste analysis plan or a generator’s self-implementing waste analysis plan; at a minimum, composite samples of residues must be collected and analyzed quarterly and when the process or operation generating the waste changes. |
ii) | Persons claiming this exclusion in an enforcement action will have the burden of proving by clear and convincing evidence that the material meets all of the exclusion requirements. The generic exclusion levels are the following: |
Constituent | Maximum for any single composite sample (mg/ℓ) |
Antimony | 0.10
|
Arsenic | 0.50
|
Barium | 7.6
|
Beryllium | 0.010
|
Cadmium | 0.050
|
Chromium (total) | 0.33
|
Lead | 0.15
|
Mercury | 0.009
|
Nickel | 1.0
|
Selenium | 0.16
|
Silver | 0.30
|
Thallium | 0.020
|
Vanadium | 1.26
|
Zinc | 70
|
Constituent | Maximum for any single composite sample (mg/ℓ) |
Antimony | 0.10
|
Arsenic | 0.50
|
Barium | 7.6
|
Beryllium | 0.010
|
Cadmium | 0.050
|
Chromium (total) | 0.33
|
Cyanide (total) (mg/kg) | 1.8
|
Lead | 0.15
|
Mercury | 0.009
|
Nickel | 1.0
|
Selenium | 0.16
|
Silver | 0.30
|
Thallium | 0.020
|
Zinc | 70
|
Section 721.104 Exclusions
a) Materials That Are Not Solid Wastes. The following materials are not solid wastes for the purpose of this Part:
1) Sewage.
A) Domestic sewage (untreated sanitary wastes that pass through a sewer system); and
B) Any mixture of domestic sewage and other waste that passes through a sewer system to publicly-owned treatment works for treatment, except as prohibited by 35 Ill. Adm. Code 726.605 and 40 CFR 403.5(b), incorporated by reference in 35 Ill. Adm. Code 720.111.
2) Industrial wastewater discharges that are point source discharges with National Pollutant Discharge Elimination System (NPDES) permits issued by the Agency under Section 12(f) of the Act and 35 Ill. Adm. Code 309.
BOARD NOTE: This exclusion applies only to the actual point source discharge. It does not exclude industrial wastewaters while they are being collected, stored, or treated before discharge, nor does it exclude sludges that are generated by industrial wastewater treatment.
3) Irrigation return flows.
4) Source, by-product, or special nuclear material, as defined by section 11 of the Atomic Energy Act of 1954, as amended (42 USC 2014), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
5) Materials subjected to in-situ mining techniques that are not removed from the ground as part of the extraction process.
6) Pulping liquors (i.e., black liquors) that are reclaimed in a pulping liquor recovery furnace and then reused in the pulping process, unless it is accumulated speculatively, as defined in Section 721.101(c).
7) Spent sulfuric acid used to produce virgin sulfuric acid, provided it is not accumulated speculatively, as defined in Section 721.101(c).
8) Secondary materials that are reclaimed and returned to the original process or processes in which they were generated, if they are reused in the production process, provided that the following is true:
A) Only tank storage is involved, and the entire process through completion of reclamation is closed by being entirely connected with pipes or other comparable enclosed means of conveyance;
B) Reclamation does not involve controlled flame combustion (such as occurs in boilers, industrial furnaces, or incinerators);
C) The secondary materials are never accumulated in such tanks for over 12 months without being reclaimed; and
D) The reclaimed material is not used to produce a fuel or used to produce products that are used in a manner constituting disposal.
9) Wood preserving wastes.
A) Spent wood preserving solutions that have been used and that are reclaimed and reused for their original intended purpose;
B) Wastewaters from the wood preserving process that have been reclaimed and that are reused to treat wood; and
C) Prior to reuse, the wood preserving wastewaters and spent wood preserving solutions described in subsections (a)(9)(A) and (a)(9)(B), so long as they meet all of the following conditions:
i) The wood preserving wastewaters and spent wood preserving solutions are reused on-site at water-borne plants in the production process for their original intended purpose;
ii) Prior to reuse, the wastewaters and spent wood preserving solutions are managed to prevent release to either land or groundwater or both;
iii) Any unit used to manage wastewaters or spent wood preserving solutions prior to reuse can be visually or otherwise determined to prevent such releases;
iv) Any drip pad used to manage the wastewaters or spent wood preserving solutions prior to reuse complies with the standards in Subpart W of 35 Ill. Adm. Code 725, regardless of whether the plant generates a total of less than 100 kg/month of hazardous waste; and
v) Prior to operating under this exclusion, the plant owner or operator prepares a one-time notification to the Agency stating that the plant intends to claim the exclusion, giving the date on which the plant intends to begin operating under the exclusion, and containing the following language: “I have read the applicable regulation establishing an exclusion for wood preserving wastewaters and spent wood preserving solutions and understand it requires me to comply at all times with the conditions set out in the regulation.” The plant must maintain a copy of that document in its on-site records until closure of the facility. The exclusion applies only so long as the plant meets all of the conditions. If the plant goes out of compliance with any condition, it may apply to the Agency for reinstatement. The Agency must reinstate the exclusion in writing if it finds that the plant has returned to compliance with all conditions and that the violations are not likely to recur. If the Agency denies an application, it must transmit to the applicant specific, detailed statements in writing as to the reasons it denied the application. The applicant under this subsection (a)(9)(C)(v) may appeal the Agency’s determination to deny the reinstatement, to grant the reinstatement with conditions, or to terminate a reinstatement before the Board under Section 40 of the Act.
10) USEPA hazardous waste numbers K060, K087, K141, K142, K143, K144, K145, K147, and K148, and any wastes from the coke by-products processes that are hazardous only because they exhibit the toxicity characteristic specified in Section 721.124, when subsequent to generation these materials are recycled to coke ovens, to the tar recovery process as a feedstock to produce coal tar, or are mixed with coal tar prior to the tar’s sale or refining. This exclusion is conditioned on there being no land disposal of the waste from the point it is generated to the point it is recycled to coke ovens, to tar recovery, to the tar refining processes, or prior to when it is mixed with coal.
11) Nonwastewater splash condenser dross residue from the treatment of USEPA hazardous waste number K061 in high temperature metals recovery units, provided it is shipped in drums (if shipped) and not land disposed before recovery.
12) Certain oil-bearing hazardous secondary materials and recovered oil, as follows:
A) Oil-bearing hazardous secondary materials (i.e., sludges, by-products, or spent materials) that are generated at a petroleum refinery (standard industrial classification (SIC) code 2911) and are inserted into the petroleum refining process (SIC code 2911: including, but not limited to, distillation, catalytic cracking, fractionation, or thermal cracking units (i.e., cokers)), unless the material is placed on the land, or speculatively accumulated before being so recycled. Materials inserted into thermal cracking units are excluded under this subsection (a)(12), provided that the coke product also does not exhibit a characteristic of hazardous waste. Oil-bearing hazardous secondary materials may be inserted into the same petroleum refinery where they are generated or sent directly to another petroleum refinery and still be excluded under this provision. Except as provided in subsection (a)(12)(B), oil-bearing hazardous secondary materials generated elsewhere in the petroleum industry (i.e., from sources other than petroleum refineries) are not excluded under this Section. Residuals generated from processing or recycling materials excluded under this subsection (a)(12)(A), if the materials as generated would have otherwise met a listing under Subpart D, are designated as USEPA hazardous waste number F037 listed wastes when disposed of or intended for disposal.
B) Recovered oil that is recycled in the same manner and with the same conditions as described in subsection (a)(12)(A). Recovered oil is oil that has been reclaimed from secondary materials (including wastewater) generated from normal petroleum industry practices, including refining, exploration and production, bulk storage, and transportation incident thereto (SIC codes 1311, 1321, 1381, 1382, 1389, 2911, 4612, 4613, 4922, 4923, 4789, 5171, and 5172). Recovered oil does not include oil-bearing hazardous wastes listed in Subpart D; however, oil recovered from such wastes may be considered recovered oil. Recovered oil does not include used oil, as defined in 35 Ill. Adm. Code 739.100.
13) Excluded scrap metal (processed scrap metal, unprocessed home scrap metal, and unprocessed prompt scrap metal) being recycled.
14) Shredded circuit boards being recycled, provided that they meet the following conditions:
A) The circuit boards are stored in containers sufficient to prevent a release to the environment prior to recovery; and
B) The circuit boards are free of mercury switches, mercury relays, nickel-cadmium batteries, and lithium batteries.
15) Condensates derived from the overhead gases from kraft mill steam strippers that are used to comply with federal Clean Air Act regulation 40 CFR 63.446(e). The exemption applies only to combustion at the mill generating the condensates.
16) This subsection (a)(16) corresponds with 40 CFR 261.4(a)(16), marked “reserved” by USEPA. This statement maintains structural consistency with the federal regulations.
17) Spent materials (as defined in Section 721.101) (other than hazardous wastes listed in Subpart D) generated within the primary mineral processing industry from which minerals, acids, cyanide, water, or other values are recovered by mineral processing or by beneficiation, provided that the following is true:
A) The spent material is legitimately recycled to recover minerals, acids, cyanide, water, or other values;
B) The spent material is not accumulated speculatively;
C) Except as provided in subsection (a)(17)(D), the spent material is stored in tanks, containers, or buildings that meet the following minimum integrity standards: a building must be an engineered structure with a floor, walls, and a roof all of which are made of non-earthen materials providing structural support (except that smelter buildings may have partially earthen floors, provided that the spent material is stored on the non-earthen portion), and have a roof suitable for diverting rainwater away from the foundation; a tank must be free standing, not be a surface impoundment (as defined in 35 Ill. Adm. Code 720.110), and be manufactured of a material suitable for containment of its contents; a container must be free standing and be manufactured of a material suitable for containment of its contents. If a tank or container contains any particulate that may be subject to wind dispersal, the owner or operator must operate the unit in a manner that controls fugitive dust. A tank, container, or building must be designed, constructed, and operated to prevent significant releases to the environment of these materials.
D) The Agency must allow by permit in writing that solid mineral processing spent materials only may be placed on pads, rather than in tanks, containers, or buildings if the facility owner or operator can demonstrate the following: the solid mineral processing secondary materials do not contain any free liquid; the pads are designed, constructed, and operated to prevent significant releases of the spent material into the environment; and the pads provide the same degree of containment afforded by the non-RCRA tanks, containers, and buildings eligible for exclusion.
i) The Agency must also consider whether storage on pads poses the potential for significant releases via groundwater, surface water, and air exposure pathways. Factors to be considered for assessing the groundwater, surface water, and air exposure pathways must include the following: the volume and physical and chemical properties of the spent material, including its potential for migration off the pad; the potential for human or environmental exposure to hazardous constituents migrating from the pad via each exposure pathway; and the possibility and extent of harm to human and environmental receptors via each exposure pathway.
ii) Pads must meet the following minimum standards: they must be designed of non-earthen material that is compatible with the chemical nature of the mineral processing spent material; they must be capable of withstanding physical stresses associated with placement and removal; they must have run-on and run-off controls; they must be operated in a manner that controls fugitive dust; and they must have integrity assurance through inspections and maintenance programs.
iii) Before making a determination under this subsection (a)(17)(D), the Agency must provide notice and the opportunity for comment to all persons potentially interested in the determination. This can be accomplished by placing notice of this action in major local newspapers, or broadcasting notice over local radio stations.
BOARD NOTE: See Subpart D of 35 Ill. Adm. Code 703 for the RCRA Subtitle C permit public notice requirements.
E) The owner or operator provides a notice to the Agency, providing the following information: the types of materials to be recycled, the type and location of the storage units and recycling processes, and the annual quantities expected to be placed in land-based units. This notification must be updated when there is a change in the type of materials recycled or the location of the recycling process.
F) For purposes of subsection (b)(7), mineral processing spent materials must be the result of mineral processing and may not include any listed hazardous wastes. Listed hazardous wastes and characteristic hazardous wastes generated by non-mineral processing industries are not eligible for the conditional exclusion from the definition of solid waste.
18) Petrochemical recovered oil from an associated organic chemical manufacturing facility, if the oil is to be inserted into the petroleum refining process (SIC code 2911) along with normal petroleum refinery process streams, provided that both of the following conditions are true of the oil:
A) The oil is hazardous only because it exhibits the characteristic of ignitability (as defined in Section 721.121) or toxicity for benzene (Section 721.124, USEPA hazardous waste number D018);
B) The oil generated by the organic chemical manufacturing facility is not placed on the land, or speculatively accumulated before being recycled into the petroleum refining process. An “associated organic chemical manufacturing facility” is a facility for which all of the following is true: its primary SIC code is 2869, but its operations may also include SIC codes 2821, 2822, and 2865; it is physically co-located with a petroleum refinery; and the petroleum refinery to which the oil being recycled is returned also provides hydrocarbon feedstocks to the organic chemical manufacturing facility. “Petrochemical recovered oil” is oil that has been reclaimed from secondary materials (i.e., sludges, by-products, or spent materials, including wastewater) from normal organic chemical manufacturing operations, as well as oil recovered from organic chemical manufacturing processes.
19) Spent caustic solutions from petroleum refining liquid treating processes used as a feedstock to produce cresylic or naphthenic acid, unless the material is placed on the land or accumulated speculatively, as defined in Section 721.101(c).
20) Hazardous secondary materials used to make zinc fertilizers, provided that the following conditions are satisfied:
A) Hazardous secondary materials used to make zinc micronutrient fertilizers must not be accumulated speculatively, as defined in Section 721.101(c)(8).
B) A generator or intermediate handler of zinc-bearing hazardous secondary materials that are to be incorporated into zinc fertilizers must fulfill the following conditions:
i) It must submit a one-time notice to the Agency that contains the name, address, and USEPA identification number of the generator or intermediate handler facility, that provides a brief description of the secondary material that will be subject to the exclusion, and that identifies when the manufacturer intends to begin managing excluded zinc-bearing hazardous secondary materials under the conditions specified in this subsection (a)(20).
ii) It must store the excluded secondary material in tanks, containers, or buildings that are constructed and maintained in a way that prevents releases of the secondary materials into the environment. At a minimum, any building used for this purpose must be an engineered structure made of non-earthen materials that provide structural support, and it must have a floor, walls, and a roof that prevent wind dispersal and contact with rainwater. A tank used for this purpose must be structurally sound and, if outdoors, it must have a roof or cover that prevents contact with wind and rain. A container used for this purpose must be kept closed, except when it is necessary to add or remove material, and it must be in sound condition. Containers that are stored outdoors must be managed within storage areas that fulfill the conditions of subsection (a)(20)(F).
iii) With each off-site shipment of excluded hazardous secondary materials, it must provide written notice to the receiving facility that the material is subject to the conditions of this subsection (a)(20).
iv) It must maintain records at the generator’s or intermediate handler’s facility, for no less than three years, of all shipments of excluded hazardous secondary materials. For each shipment these records must, at a minimum, contain the information specified in subsection (a)(20)(G).
C) A manufacturer of zinc fertilizers or zinc fertilizer ingredients made from excluded hazardous secondary materials must fulfill the following conditions:
i) It must store excluded hazardous secondary materials in accordance with the storage requirements for generators and intermediate handlers, as specified in subsection (a)(20)(B)(ii).
ii) It must submit a one-time notification to the Agency that, at a minimum, specifies the name, address, and USEPA identification number of the manufacturing facility and that identifies when the manufacturer intends to begin managing excluded zinc-bearing hazardous secondary materials under the conditions specified in this subsection (a)(20).
iii) It must maintain for a minimum of three years records of all shipments of excluded hazardous secondary materials received by the manufacturer, which must at a minimum identify for each shipment the name and address of the generating facility, the name of transporter, and the date on which the materials were received, the quantity received, and a brief description of the industrial process that generated the material.
iv) It must submit an annual report to the Agency that identifies the total quantities of all excluded hazardous secondary materials that were used to manufacture zinc fertilizers or zinc fertilizer ingredients in the previous year, the name and address of each generating facility, and the industrial processes from which the hazardous secondary materials were generated.
D) Nothing in this Section preempts, overrides, or otherwise negates the provision in 35 Ill. Adm. Code 722.111 that requires any person who generates a solid waste to determine if that waste is a hazardous waste.
E) Interim status and permitted storage units that have been used to store only zinc-bearing hazardous wastes prior to the submission of the one-time notice described in subsection (a)(20)(B)(i), and that afterward will be used only to store hazardous secondary materials excluded under this subsection (a)(20), are not subject to the closure requirements of 35 Ill. Adm. Code 724 and 725.
F) A container used to store excluded secondary material must fulfill the following conditions:
i) It must have containment structures or systems sufficiently impervious to contain leaks, spills, and accumulated precipitation;
ii) It must provide for effective drainage and removal of leaks, spills, and accumulated precipitation; and
iii) It must prevent run-on into the containment system.
BOARD NOTE: Subsections (a)(20)(F)(i) through (a)(20)(F)(iii) are derived from 40 CFR 261.4(a)(20)(ii)(B)(1) through (a)(20)(ii)(B)(3). The Board added the preamble to these federal paragraphs as subsection (a)(20)(F) to comport with Illinois Administrative Code codification requirements.
G) Required records of shipments of excluded hazardous secondary materials must, at a minimum, contain the following information:
i) The name of the transporter and date of the shipment;
ii) The name and address of the facility that received the excluded material, along with documentation confirming receipt of the shipment; and
iii) The type and quantity of excluded secondary material in each shipment.
BOARD NOTE: Subsections (a)(20)(G)(i) through (a)(20)(G)(iii) are derived from 40 CFR 261.4(a)(20)(ii)(D)(1) through (a)(20)(ii)(D)(3). The Board added the preamble to these federal paragraphs as subsection (a)(20)(G) to comport with Illinois Administrative Code codification requirements.
21) Zinc fertilizers made from hazardous wastes or hazardous secondary materials that are excluded under subsection (a)(20), provided that the following conditions are fulfilled:
A) The fertilizers meet the following contaminant limits:
i) For metal contaminants:
Constituent | Maximum Allowable Total Concentration in Fertilizer, per Unit (1%) of Zinc (ppm) |
Arsenic | 0.3
|
Cadmium | 1.4
|
Chromium | 0.6
|
Lead | 2.8
|
Mercury | 0.3
|
B) The manufacturer performs sampling and analysis of the fertilizer product to determine compliance with the contaminant limits for metals no less frequently than once every six months, and for dioxins no less frequently than once every 12 months. Testing must also be performed whenever changes occur to manufacturing processes or ingredients that could significantly affect the amounts of contaminants in the fertilizer product. The manufacturer may use any reliable analytical method to demonstrate that no constituent of concern is present in the product at concentrations above the applicable limits. It is the responsibility of the manufacturer to ensure that the sampling and analysis are unbiased, precise, and representative of the products introduced into commerce.
C) The manufacturer maintains, for no less than three years, records of all sampling and analyses performed for purposes of determining compliance with subsection (a)(21)(B). Such records must at a minimum include the following:
i) The dates and times product samples were taken, and the dates the samples were analyzed;
ii) The names and qualifications of the persons taking the samples;
iii) A description of the methods and equipment used to take the samples;
iv) The name and address of the laboratory facility at which analyses of the samples were performed;
v) A description of the analytical methods used, including any cleanup and sample preparation methods; and
vi) All laboratory analytical results used to determine compliance with the contaminant limits specified in this subsection (a)(21).
22) Used CRTs
A) Used, intact CRTs, as defined in 35 Ill. Adm. Code 720.110, are not solid waste within the United States, unless they are disposed of or speculatively accumulated, as defined in Section 721.101(c)(8), by a CRT collector or glass processor.
B) Used, intact CRTs, as defined in 35 Ill. Adm. Code 720.110, are not solid waste when exported for recycling, provided that they meet the requirements of Section 721.140.
C) Used, broken CRTs, as defined in 35 Ill. Adm. Code 720.110, are not solid waste, provided that they meet the requirements of Section 721.139.
D) Glass removed from CRTs is not a solid waste provided that it meets the requirements of Section 721.139(c).
23) Hazardous Secondary Materials Reclaimed under the Control of the Generator. Hazardous secondary material generated and legitimately reclaimed within the United States or its territories and under the control of the generator, provided that the material complies with subsections (a)(23)(A) and (a)(23)(B):
A) Excluded Hazardous Secondary Materials
i) The hazardous secondary material is generated and reclaimed at the generating facility. (For purposes of this subsection (a)(23)(A)(i), “generating facility” means all contiguous property owned, leased, or otherwise controlled by the hazardous secondary material generator.);
ii) The hazardous secondary material is generated and reclaimed at different facilities, if the reclaiming facility is controlled by the generator or if both the generating facility and the reclaiming facility are controlled by a person as defined in 35 Ill. Adm. Code 720.110, and if the generator provides one of the following certifications:
“On behalf of [insert generator facility name], I certify that this facility will send the indicated hazardous secondary material to [insert reclaimer facility name], which is controlled by [insert generator facility name] and that [insert name of either facility] has acknowledged full responsibility for the safe management of the hazardous secondary material.”
or
“On behalf of [insert generator facility name], I certify that this facility will send the indicated hazardous secondary material to [insert reclaimer facility name], that both facilities are under common control, and that [insert name of either facility] has acknowledged full responsibility for the safe management of the hazardous secondary material.”
For purposes of this subsection (a)(23)(A)(ii), “control” means the power to direct the policies of the facility, whether by the ownership of stock, voting rights, or otherwise, except that contractors who operate facilities on behalf of a different person, as defined in 35 Ill. Adm. Code 720.110, cannot be deemed to “control” such facilities. The generating and receiving facilities must both maintain at their facilities, for no less than three years, records of hazardous secondary materials sent or received under this exclusion. In both cases, the records must contain the name of the transporter, the date of the shipment, and the type and quantity of the hazardous secondary material shipped or received under the exclusion. These requirements may be satisfied by routine business records (e.g., financial records, bills of lading, copies of USDOT shipping papers, or electronic confirmations); or
iii) The hazardous secondary material is generated under a written contract between a tolling contractor and a toll manufacturer and is reclaimed by the tolling contractor, if the tolling contractor certifies as follows:
“On behalf of [insert tolling contractor name], I certify that [insert tolling contractor name] has a written contract with [insert toll manufacturer name] to manufacture [insert name of product or intermediate] which is made from specified unused materials, and that [insert tolling contractor name] will reclaim the hazardous secondary materials generated during this manufacture. On behalf of [insert tolling contractor name], I also certify that [insert tolling contractor name] retains ownership of, and responsibility for, the hazardous secondary materials that are generated during the course of the manufacture, including any releases of hazardous secondary materials that occur during the manufacturing process.”
The tolling contractor must maintain at its facility, for no less than three years, records of hazardous secondary materials received under its written contract with the tolling manufacturer, and the tolling manufacturer must maintain at its facility, for no less than three years, records of hazardous secondary materials shipped under its written contract with the tolling contractor. In both cases, the records must contain the name of the transporter, the date of the shipment, and the type and quantity of the hazardous secondary material shipped or received under the written contract. These requirements may be satisfied by routine business records (e.g., financial records, bills of lading, copies of USDOT shipping papers, or electronic confirmations). For purposes of this subsection (a)(23)(A)(ii), “tolling contractor” means a person who arranges for the production of a product or intermediate made from specified unused materials through a written contract with a toll manufacturer. “Toll manufacturer” means a person who produces a product or intermediate made from specified unused materials under a written contract with a tolling contractor.
B) Management of Hazardous Secondary Materials
i) The hazardous secondary material is contained, as defined in 35 Ill. Adm. Code 720.110. A hazardous secondary material released to the environment is discarded material and a solid waste unless it is immediately recovered for the purpose of reclamation. Hazardous secondary material managed in a unit with leaks or other continuing or intermittent unpermitted releases is discarded material and a solid waste;
ii) The hazardous secondary material is not speculatively accumulated, as defined in Section 721.101(c)(8);
iii) Notice is provided, as required by 35 Ill. Adm. Code 720.142;
iv) The hazardous secondary material is not otherwise subject to material-specific management conditions under subsection (a) when reclaimed, and it is not a spent lead acid battery (see 35 Ill. Adm. Code 726.180 and 733.102);
v) Persons performing the recycling of hazardous secondary materials under this exclusion must maintain documentation of their legitimacy determination on-site. Documentation must be a written description of how the recycling meets all three factors in 35 Ill. Adm. Code 720.143(a) and how the factor in 35 Ill. Adm. Code 720.143(b) was considered. Documentation must be maintained for three years after the recycling operation has ceased; and
vi) The emergency preparedness and response requirements found in Subpart M are met.
24) Hazardous Secondary Materials Transferred for Off-Site Reclamation. Hazardous secondary material that is generated and then transferred to another person for the purpose of reclamation is not a solid waste if the management of the material fulfills the conditions of subsections (a)(24)(A) through (a)(24)(G):
A) The hazardous secondary material must not be speculatively accumulated, as defined in Section 721.101(c)(8).
B) No person or facility other than the hazardous secondary material generator, the transporter, an intermediate facility, or a reclaimer manages the material; the hazardous secondary material must not be stored for more than ten days at a transfer facility, as defined in Section 721.110; and the hazardous secondary material must be packaged according to applicable USDOT regulations codified as 49 CFR 173, 178, and 179, incorporated by reference in 35 Ill. Adm. Code 720.111, while in transport.
C) The hazardous secondary material must not otherwise be subject to material-specific management conditions under other provisions of this subsection (a) when reclaimed, and the hazardous secondary material must not be a spent lead-acid battery (see 35 Ill. Adm. Code 726.180 and 733.102).
D) The reclamation of the hazardous secondary material must be legitimate, as determined under 35 Ill. Adm. Code 720.143.
E) The hazardous secondary material generator must satisfy each of the following conditions:
i) The hazardous secondary material must be contained as defined in 35 Ill. Adm. Code 720.110. A hazardous secondary material released to the environment is discarded and a solid waste unless it is immediately recovered for the purpose of recycling. Hazardous secondary material managed in a unit that leaks or that otherwise continuously releases hazardous secondary material is discarded material and a solid waste.
ii) Prior to arranging for transport of hazardous secondary materials to a reclamation facility where the hazardous secondary material is managed in a unit that is not subject to a RCRA permit or interim status standards, the hazardous secondary material generator must make reasonable efforts to ensure that each reclaimer intends to properly and legitimately reclaim the hazardous secondary material and not discard it, and that each reclaimer will manage the hazardous secondary material in a manner that is protective of human health and the environment. If the hazardous secondary material will pass through an intermediate facility where the hazardous secondary materials is managed at that facility in a unit that is not subject to a RCRA permit or interim status standards, the hazardous secondary material generator must make contractual arrangements with the intermediate facility to ensure that the hazardous secondary material is sent to the reclamation facility identified by the hazardous secondary material generator, and the hazardous secondary material generator must perform reasonable efforts to ensure that the intermediate facility will manage the hazardous secondary material in a manner that is protective of human health and the environment. Reasonable efforts must be repeated at a minimum of every three years for the hazardous secondary material generator to claim the exclusion and to send the hazardous secondary materials to each reclaimer and any intermediate facility. In making these reasonable efforts, the generator may use any credible evidence available, including information gathered by the hazardous secondary material generator, provided by the reclaimer or intermediate facility, or provided by a third party. The hazardous secondary material generator must affirmatively answer all of the questions in subsection (a)(24)(H) for each reclamation facility and any intermediate facility.
BOARD NOTE: The Board moved the required generator inquiries of 40 CFR 261.4(a)(24)(v)(B)(1) through (a)(24)(v)(B)(5) to subsection (a)(24)(H) to comply with codification requirements.
iii) The hazardous secondary material generator must maintain for a minimum of three years documentation and certification that reasonable efforts were made for each reclamation facility and, if applicable, intermediate facility where the facility manages the hazardous secondary materials in a unit that is not subject to a RCRA permit or interim status standards prior to transferring hazardous secondary material. Documentation and certification must be made available upon request by USEPA or the Agency within 72 hours, or within a longer period of time as specified by USEPA or the Agency. The certification statement must include the printed name and official title of an authorized representative of the hazardous secondary material generator company, the authorized representative’s signature, and the date signed. The certification statement must also incorporate the following language:
“I hereby certify in good faith and to the best of my knowledge that, prior to arranging for transport of excluded hazardous secondary materials to [insert name(s) of reclamation facility and any intermediate facility], reasonable efforts were made in accordance with 35 Ill. Adm. Code 721.104(a)(24)(E)(ii) to ensure that the hazardous secondary materials would be recycled legitimately, and otherwise managed in a manner that is protective of human health and the environment, and that such efforts were based on current and accurate information.”
BOARD NOTE: The Board combined the documentation, certification, and records retention requirements of corresponding 40 CFR 261.4(a)(24)(v)(C)(1) through (a)(24)(v)(C)(3) into subsection (a)(24)(E)(iii) to comply with codification requirements.
iv) The hazardous secondary material generator must maintain certain records at the generating facility for a minimum of three years that document every off-site shipment of hazardous secondary materials. The documentation for each shipment must, at a minimum, include the following information about the shipment: the name of the transporter and date of the shipment; the name and address of each reclaimer and intermediate facility to which the hazardous secondary material was sent; and the type and quantity of hazardous secondary material in the shipment.
BOARD NOTE: The Board combined and moved the shipping documentation and records retention requirements of corresponding 40 CFR 261.4(a)(24)(v)(C) and (a)(24)(v)(C)(1) through (a)(24)(v)(C)(3) to this single subsection (a)(24)(E)(iv). This combination allowed compliance with codification requirements relating to the maximum permissible indent level.
v) The hazardous secondary material generator must maintain at the generating facility, for a minimum of three years, for every off-site shipment of hazardous secondary materials, confirmations of receipt from each reclaimer and intermediate facility to which its hazardous secondary materials were sent. Each confirmation of receipt must include the name and address of the reclaimer (or intermediate facility), the type and quantity of the hazardous secondary materials received, and the date on which the facility received the hazardous secondary materials. The generator may satisfy this requirement using routine business records (e.g., financial records, bills of lading, copies of USDOT shipping papers, or electronic confirmations of receipt).
vi) The hazardous secondary material generator must comply with the emergency preparedness and response conditions in Subpart M.
BOARD NOTE: The Board intends that “RCRA permit” in subsections (a)(24)(E)(ii) and (a)(24)(E)(iii) include a permit issued by USEPA or a sister state under section 3005 of RCRA (42 USC 6925).
F) The reclaimer of hazardous secondary material or any intermediate facility, as defined in 35 Ill. Adm. Code 720.110, that manages material that is excluded from regulation under this subsection (a)(24) must satisfy all of the following conditions:
i) The owner or operator of a reclamation or intermediate facility must maintain at its facility for a minimum of three years records of every shipment of hazardous secondary material that the facility received and, if applicable, for every shipment of hazardous secondary material that the facility received and subsequently sent off-site from the facility for further reclamation. For each shipment, these records must, at a minimum, contain the following information: the name of the transporter and date of the shipment; the name and address of the hazardous secondary material generator and, if applicable, the name and address of the reclaimer or intermediate facility from which the facility received the hazardous secondary materials; the type and quantity of hazardous secondary material in the shipment; and, for hazardous secondary materials that the facility subsequently transferred off-site for further reclamation after receiving it, the name and address of the (subsequent) reclaimer and any intermediate facility to which the facility sent the hazardous secondary material.
BOARD NOTE: The Board combined the provisions from 40 CFR 261.4(a)(24)(vi)(A) and (a)(24)(vi)(A)(1) through (a)(24)(vi)(A)(3) that enumerate the required information into this single subsection (a)(24)(F)(i). This combination allowed compliance with codification requirements relating to the maximum permissible indent level.
ii) The intermediate facility must send the hazardous secondary material to the reclaimers designated by the generator of the hazardous secondary materials.
iii) The reclaimer or intermediate facility that receives a shipment of hazardous secondary material must send a confirmation of receipt to the hazardous secondary material generator for each off-site shipment of hazardous secondary materials. A confirmation of receipt must include the name and address of the reclaimer (or intermediate facility), the type and quantity of the hazardous secondary materials received, and the date on which the facility received the hazardous secondary materials. The reclaimer or intermediate facility may satisfy this requirement using routine business records (e.g., financial records, bills of lading, copies of USDOT shipping papers, or electronic confirmations of receipt).
iv) The reclaimer or intermediate facility must manage the hazardous secondary material in a manner that is at least as protective of human health and the environment as that employed for analogous raw material, and the material must be contained. An “analogous raw material” is a raw material for which the hazardous secondary material substitutes and that serves the same function and has similar physical and chemical properties as the hazardous secondary material.
v) A reclaimer of hazardous secondary materials must manage any residuals that are generated from its reclamation processes in a manner that is protective of human health and the environment. If any residuals of the reclamation process exhibit a characteristic of hazardous waste, as defined in Subpart C, or if the residuals themselves are specifically listed as hazardous waste in Subpart D, those residuals are hazardous waste. The reclaimer and any subsequent persons must manage that hazardous waste in accordance with the applicable requirements of 35 Ill. Adm. Code: Subtitle G or similar regulations authorized by USEPA as equivalent to 40 CFR 260 through 272.
vi) The reclaimer and intermediate facility must have financial assurance that satisfies the requirements of Subpart H.
G) In addition, any person claiming the exclusion for recycled hazardous secondary material under this subsection (a)(24) must provide notification as required by 35 Ill. Adm. Code 720.142.
H) For the purposes of the reasonable inquiries required by subsection (a)(24)(E)(ii), the hazardous secondary material generator must affirmatively answer all of the following questions for each reclamation facility and any intermediate facility:
i) Does the available information indicate that the reclamation process is legitimate under 35 Ill. Adm. Code 720.143? In answering this question, the hazardous secondary material generator can rely on its existing knowledge of the physical and chemical properties of the hazardous secondary material, as well as information from other sources (e.g., the reclamation facility, audit reports, etc.) about the reclamation process.
ii) Does the publicly available information indicate that the reclamation facility and any intermediate facility that is used by the hazardous secondary material generator notified the appropriate authorities of hazardous secondary materials reclamation activities under 35 Ill. Adm. Code 720.142, and have they notified the appropriate authorities that the financial assurance condition is satisfied per subsection (a)(24)(F)(vi)? In answering these questions, the hazardous secondary material generator can rely on the available information documenting the reclamation facility’s and any intermediate facility’s compliance with the notification requirements per 35 Ill. Adm. Code 720.142, including the requirement in 35 Ill. Adm. Code 720.142(a)(5) to notify USEPA or the Agency whether the reclaimer or intermediate facility has financial assurance.
iii) Does publicly available information indicate that the reclamation facility or any intermediate facility that is used by the hazardous secondary material generator has not had any formal enforcement actions taken against the facility in the previous three years for violations of the RCRA hazardous waste regulations and has not been classified as a significant noncomplier with RCRA Subtitle C? In answering this question, the hazardous secondary material generator can rely on the publicly available information from USEPA or the state. If the reclamation facility or any intermediate facility that is used by the hazardous secondary material generator has had a formal enforcement action taken against the facility in the previous three years for violations of the RCRA hazardous waste regulations and has been classified as a significant non-complier with RCRA Subtitle C, does the hazardous secondary material generator have credible evidence that the facility will manage the hazardous secondary materials properly? In answering this question, the hazardous secondary material generator can obtain additional information from USEPA, the state, or the facility itself that the facility has addressed the violations, taken remedial steps to address the violations and prevent future violations, or that the violations are not relevant to the proper management of the hazardous secondary materials.
iv) Does the available information indicate that the reclamation facility and any intermediate facility that is used by the hazardous secondary material generator have the equipment and trained personnel to safely recycle the hazardous secondary material? In answering this question, the generator may rely on a description by the reclamation facility or by an independent third party of the equipment and trained personnel to be used to recycle the generator’s hazardous secondary material.
v) If residuals are generated from the reclamation of the excluded hazardous secondary materials, does the reclamation facility have the permits required (if any) to manage the residuals? If not, does the reclamation facility have a contract with an appropriately permitted facility to dispose of the residuals? If not, does the hazardous secondary material generator have credible evidence that the residuals will be managed in a manner that is protective of human health and the environment? In answering these questions, the hazardous secondary material generator can rely on publicly available information from USEPA or the state, or information provided by the facility itself.
BOARD NOTE: The Board moved the required generator inquiries into a reclamation or intermediate facility of 40 CFR 261.4(a)(24)(v)(B) and (a)(24)(v)(B)(1) through (a)(24)(v)(B)(5) to this subsection (a)(24)(H) to comply with codification requirements.
25) Hazardous secondary material that is exported from the United States and reclaimed at a reclamation facility located in a foreign country is not a solid waste, provided that the hazardous secondary material generator complies with the applicable requirements of subsections (a)(24)(A) through (a)(24)(E) and (a)(24)(H) (excepting subsection (a)(24)(H)(ii) for foreign reclaimers and foreign intermediate facilities), and that the hazardous secondary material generator also complies with the following requirements:
A) The generator must notify USEPA of an intended export before the hazardous secondary material is scheduled to leave the United States. The generator must submit a complete notification at least 60 days before the initial shipment is intended to be shipped off-site. This notification may cover export activities extending over a 12-month or lesser period. The notification must be in writing, signed by the hazardous secondary material generator, and include the following information:
i) The name, mailing address, telephone number and USEPA identification number (if applicable) of the hazardous secondary material generator;
ii) A description of the hazardous secondary material and the USEPA hazardous waste number that would apply if the hazardous secondary material were managed as hazardous waste and the USDOT proper shipping name, hazard class and identification number (UN or NA) for each hazardous secondary material as identified in the hazardous materials table in 49 CFR 172.101, incorporated by reference in 35 Ill. Adm. Code 720.111;
iii) The estimated frequency or rate at which the hazardous secondary material is to be exported and the period of time over which the hazardous secondary material is to be exported;
iv) The estimated total quantity of hazardous secondary material;
v) All points of entry to and departure from each foreign country through which the hazardous secondary material will pass;
vi) A description of the means by which each shipment of the hazardous secondary material will be transported (e.g., mode of transportation vehicle (air, highway, rail, water, etc.), types of container (drums, boxes, tanks, etc.), etc.);
vii) A description of the manner in which the hazardous secondary material will be reclaimed in the country of import;
viii) The name and address of the reclaimer, any intermediate facility, and any alternate reclaimer and intermediate facilities; and
ix) The name of any countries of transit through which the hazardous secondary material will be sent and a description of the approximate length of time it will remain in such countries and the nature of its handling while there (for purposes of this Section, the terms “USEPA Acknowledgement of Consent”, “country of import”, and “country of transit” are used as defined in 35 Ill. Adm. Code 722.181 with the exception that the terms in this Section refer to hazardous secondary materials, rather than hazardous waste).
B) The generator must submit notifications electronically using USEPA’s Waste Import Export Tracking System (WIETS).
C) Except for changes to the telephone number required in subsection (a)(25)(A)(i) and decreases in the quantity of hazardous secondary material indicated under subsection (a)(25)(A)(iv), when the conditions specified on the original notification change (including any exceedance of the estimate of the quantity of hazardous secondary material specified in the original notification), the hazardous secondary material generator must provide USEPA with a written renotification of the change. The shipment must not occur until consent of the country of import to the changes (except for changes to subsection (a)(25)(A)(ix) and in the ports of entry to and departure from countries of transit under subsection (a)(25)(A)(v)) has been obtained and the hazardous secondary material generator receives from USEPA a USEPA Acknowledgment of Consent reflecting the country of import’s consent to the changes.
D) Upon request by USEPA, the hazardous secondary material generator must furnish to USEPA any additional information that a country of import requests in order to respond to a notification.
E) USEPA will provide a complete notification to the country of import and any countries of transit. A notification is complete when USEPA receives a notification that USEPA determines satisfies the requirements of subsection (a)(25)(A). When a claim of confidentiality is asserted with respect to any notification information required by subsection (a)(25)(A), USEPA may find the notification not complete until any such claim is resolved in accordance with 35 Ill. Adm. Code 720.102.
F) The export of hazardous secondary material under this subsection (a)(25) is prohibited unless the country of import consents to the intended export. When the country of import consents in writing to the receipt of the hazardous secondary material, USEPA will send an USEPA Acknowledgment of Consent to the hazardous secondary material generator. When the country of import objects to receipt of the hazardous secondary material or withdraws a prior consent, USEPA will notify the hazardous secondary material generator in writing. USEPA will also notify the hazardous secondary material generator of any responses from countries of transit.
G) For exports to OECD member countries, the receiving country may respond to the notification using tacit consent. If no objection has been lodged by any country of import or countries of transit to a notification provided under subsection (a)(25)(A) within 30 days after the date of issuance of the acknowledgement of receipt of notification by the competent authority of the country of import, the transboundary movement may commence. In such cases, USEPA will send a USEPA Acknowledgment of Consent to inform the hazardous secondary material generator that the country of import and any relevant countries of transit have not objected to the shipment and are thus presumed to have consented tacitly. Tacit consent expires one calendar year after the close of the 30-day period; renotification and renewal of all consents is required for exports after that date.
H) A copy of the USEPA Acknowledgment of Consent must accompany the shipment. The shipment must conform to the terms of the USEPA Acknowledgment of Consent.
I) If the shipment cannot be delivered for any reason to the reclaimer, intermediate facility or the alternate reclaimer or alternate intermediate facility, the hazardous secondary material generator must re-notify USEPA of a change in the conditions of the original notification to allow shipment to a new reclaimer in accordance with subsection (a)(25)(C) of this Section and obtain another USEPA Acknowledgment of Consent.
J) Hazardous secondary material generators must keep a copy of each notification of intent to export and each USEPA Acknowledgment of Consent for a period of three years following receipt of the USEPA Acknowledgment of Consent. They may satisfy this recordkeeping requirement by retaining electronically submitted notifications or electronically generated Acknowledgements in their account on USEPA’s WIETS, provided that such copies are readily available for viewing and production if requested by any USEPA or Agency inspector. No hazardous secondary material generator may be held liable for the inability to produce a notification or Acknowledgement for inspection under this Section if it can demonstrate that the inability to produce such copies is due exclusively to technical difficulty with USEPA’s WIETS for which the hazardous secondary material generator bears no responsibility.
K) Hazardous secondary material generators must file with USEPA, no later than March 1 of each year, a report summarizing the types, quantities, frequency and ultimate destination of all hazardous secondary materials exported during the previous calendar year. Annual reports must be submitted electronically using USEPA’s WIETS. Such reports must include the following information:
i) Name, mailing and site address, and USEPA identification number (if applicable) of the hazardous secondary material generator;
ii) The calendar year covered by the report;
iii) The name and site address of each reclaimer and intermediate facility;
iv) By reclaimer and intermediate facility, for each hazardous secondary material exported, a description of the hazardous secondary material and the USEPA hazardous waste number that would apply if the hazardous secondary material were managed as hazardous waste; the USDOT hazard class, incorporated by reference in 35 Ill. Adm. Code 720.111; the name and USEPA identification number (if applicable) for each transporter used, the total amount of hazardous secondary material shipped, and the number of shipments under each notification; and
v) A certification signed by the hazardous secondary material generator that states as follows:
“I certify under penalty of law that I have personally examined and am familiar with the information submitted in this and all attached documents, and that, based on my inquiry of those individuals immediately responsible for obtaining the information, I believe that the submitted information is true, accurate, and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment.”
L) Any person claiming an exclusion under this subsection (a)(25) must provide notification as required by 35 Ill. Adm. Code 720.142.
26) Solvent-contaminated wipes that are sent for cleaning and reuse are not solid wastes from the point of generation, provided that all of the following conditions are fulfilled:
A) The solvent-contaminated wipes, when accumulated, stored, and transported, are contained in non-leaking, closed containers that are labeled “Excluded Solvent-Contaminated Wipes”. The containers must be able to contain free liquids, should free liquids occur. During accumulation, a container is considered closed when there is complete contact between the fitted lid and the rim, except when it is necessary to add or remove solvent-contaminated wipes. When the container is full, when the solvent-contaminated wipes are no longer being accumulated, or when the container is being transported, the container must be sealed with all lids properly and securely affixed to the container and all openings tightly bound or closed sufficiently to prevent leaks and emissions;
B) The solvent-contaminated wipes may be accumulated by the generator for up to 180 days from the start date of accumulation for each container prior to being sent for cleaning;
C) At the point of being sent for cleaning on-site or at the point of being transported off-site for cleaning, the solvent-contaminated wipes must contain no free liquids, as defined in 35 Ill. Adm. Code 720.110;
D) Free liquids removed from the solvent-contaminated wipes or from the container holding the wipes must be managed according to the applicable regulations found in this Part and 35 Ill. Adm. Code 720, 722 through 728, and 733;
E) Generators must maintain at their site the following documentation:
i) The name and address of the laundry or dry cleaner that is receiving the solvent-contaminated wipes;
ii) The documentation that the 180-day accumulation time limit in 35 Ill. Adm. Code 721.104(a)(26)(B) is being met; and
iii) A description of the process the generator is using to ensure that the solvent-contaminated wipes contain no free liquids at the point of being laundered or dry cleaned on-site or at the point of being transported off-site for laundering or dry cleaning; and
F) The solvent-contaminated wipes are sent to a laundry or dry cleaner whose discharge, if any, is regulated under sections 301 and 402 or section 307 of the federal Clean Water Act (33 USC 1311 and 1341 or 33 USC 1317) or equivalent Illinois or sister-state requirements approved by USEPA under 33 USC 1311 through 1346 and 1370.
27) Hazardous secondary material that is generated and then transferred to another person for the purpose of remanufacturing is not a solid waste, provided that the following conditions are fulfilled:
BOARD NOTE: The North American Industrial Classification System (NAICS) codes used in this subsection (a)(27) are defined in the NAICS Manual, available from the Office of Management and Budget and incorporated by reference in 35 Ill. Adm. Code 720.111.
A) The hazardous secondary material consists of one or more of the following spent solvents: toluene, xylenes, ethylbenzene, 1,2,4-trimethylbenzene, chlorobenzene, n-hexane, cyclohexane, methyl tert-butyl ether, acetonitrile, chloroform, chloromethane, dichloromethane, methyl isobutyl ketone, N,N-dimethylformamide, tetrahydrofuran, n-butyl alcohol, ethanol, or methanol.
B) The hazardous secondary material originated from using one or more of the solvents listed in subsection (a)(27)(A) in a commercial grade for reacting, extracting, purifying, or blending chemicals (or for rinsing out the process lines associated with these functions) in the pharmaceutical manufacturing (NAICS 325412), basic organic chemical manufacturing (NAICS 325199), plastics and resins manufacturing (NAICS 325211), or the paints and coatings manufacturing sectors (NAICS 325510).
C) The hazardous secondary material generator sends the hazardous secondary material spent solvents listed in subsection (a)(27)(A) to a remanufacturer in the pharmaceutical manufacturing (NAICS 325412), basic organic chemical manufacturing (NAICS 325199), plastics and resins manufacturing (NAICS 325211), or the paints and coatings manufacturing sectors (NAICS 325510).
D) After remanufacturing one or more of the solvents listed in subsection (a)(27)(A), the use of the remanufactured solvent must be limited to reacting, extracting, purifying, or blending chemicals (or for rinsing out the process lines associated with these functions) in the pharmaceutical manufacturing (NAICS 325412), basic organic chemical manufacturing (NAICS 325199), plastics and resins manufacturing (NAICS 325211), and the paints and coatings manufacturing sectors (NAICS 325510) or to using them as ingredients in a product. These allowed uses correspond to chemical functional uses enumerated in 40 CFR 711.15(b)(4)(i)(C) (Reporting Information to EPA), incorporated by reference in 35 Ill. Adm. Code 720.111, including Industrial Function Category Codes U015 (solvents consumed in a reaction to produce other chemicals) and U030 (solvents that become part of the mixture).
BOARD NOTE: The Board observes that the citation to Toxic Substances Control Act function categories and use of the word “including” to preface specific example Industrial Function Category Codes does not expand the range of permissible uses beyond the express limitations recited in the first segment of this subsection (a)(27)(D) and subsection (a)(27)(E).
E) After remanufacturing one or more of the solvents listed in subsection (a)(27)(i), the use of the remanufactured solvent does not involve cleaning or degreasing oil, grease, or similar material from textiles, glassware, metal surfaces, or other articles. (These disallowed continuing uses correspond to chemical functional uses in Industrial Function Category Code U029 (solvents (for cleaning and degreasing)) in 40 CFR 711.15(b)(4)(i)(C), incorporated by reference in 35 Ill. Adm. Code 720.111.
F) Both the hazardous secondary material generator and the remanufacturer must fulfill the following requirements:
i) The generator and remanufacturer must notify USEPA Region 5 and the Agency, and update the notification every two years per 35 Ill. Adm. Code 720.142;
ii) The generator and remanufacturer must develop and maintain an up-to-date remanufacturing plan that identifies the information enumerated in subsection (a)(27)(G);
BOARD NOTE: The Board moved corresponding 40 CFR 261.4(a)(27)(vi)(B)(1) through (a)(27)(vi)(B)(1) to appear as subsections (a)(27)(G)(i) through (a)(27)(G)(v) to comport with codification requirements.
iii) The generator and remanufacturer must maintain records of shipments and confirmations of receipts for a period of three years from the dates of the shipments;
iv) The generator and remanufacturer must, prior to remanufacturing, store the hazardous spent solvents in tanks or containers that meet technical standards found in Subparts I and J, with the tanks and containers being labeled or otherwise having an immediately available record of the material being stored;
v) The generator and remanufacturer must, during remanufacturing, and during storage of the hazardous secondary materials prior to remanufacturing, the remanufacturer certifies that the remanufacturing equipment, vents, and tanks are equipped with and are operating air emission controls in compliance with the applicable Clean Air Act regulations of 40 CFR 60, 61 and 63, incorporated by reference in 35 Ill. Adm. Code 720.111; or, absent such Clean Air Act standards for the particular operation or piece of equipment covered by the remanufacturing exclusion, are in compliance with the appropriate standards in Subparts AA (vents), BB (equipment) and CC (tank storage); and
vi) The generator and remanufacturer must meet the requirements prohibiting speculative accumulation in Section 721.101(c)(8).
G) The following information items are required elements for a remanufacturing plan.
i) The name, address and USEPA ID number of the generators and the remanufacturers;
ii) The types and estimated annual volumes of spent solvents to be remanufactured;
iii) The processes and industry sectors that generate the spent solvents;
iv) The specific uses and industry sectors for the remanufactured solvents; and
v) A certification from the remanufacturer stating as follows:
“On behalf of [insert remanufacturer facility name], I certify that this facility is a remanufacturer under pharmaceutical manufacturing (NAICS 325412), basic organic chemical manufacturing (NAICS 325199), plastics and resins manufacturing (NAICS 325211), and/or the paints and coatings manufacturing sectors (NAICS 325510), and will accept the spent solvent(s) for the sole purpose of remanufacturing into commercial-grade solvent(s) that will be used for reacting, extracting, purifying, or blending chemicals (or for rinsing out the process lines associated with these functions) or for use as product ingredient(s). I also certify that the remanufacturing equipment, vents, and tanks are equipped with and are operating air emission controls in compliance with the appropriate Clean Air Act regulations under 40 CFR 60, 61 or 63, or, absent such Clean Air Act standards for the particular operation or piece of equipment covered by the remanufacturing exclusion, are in compliance with the appropriate standards in Subparts AA (vents), BB (equipment) and CC (tank storage).”
BOARD NOTE: Subsections (a)(27)(G)(i) through (a)(27)(G)(v) correspond with 40 CFR 261.4(a)(27)(vi)(B)(1) through (a)(27)(vi)(B)(1), moved to this subsection (a)(27)(G) to comport with codification requirements.
b) Solid Wastes That Are Not Hazardous Wastes. The following solid wastes are not hazardous wastes:
1) Household waste, including household waste that has been collected, transported, stored, treated, disposed of, recovered (e.g., refuse-derived fuel), or reused. “Household waste” means any waste material (including garbage, trash, and sanitary wastes in septic tanks) derived from households (including single and multiple residences, hotels, and motels, bunkhouses, ranger stations, crew quarters, campgrounds, picnic grounds, and day-use recreation areas). A resource recovery facility managing municipal solid waste must not be deemed to be treating, storing, disposing of, or otherwise managing hazardous wastes for the purposes of regulation under this Part, if the following describe the facility:
A) The facility receives and burns only the following waste:
i) Household waste (from single and multiple dwellings, hotels, motels, and other residential sources); or
ii) Solid waste from commercial or industrial sources that does not contain hazardous waste; and
B) The facility does not accept hazardous waste and the owner or operator of such facility has established contractual requirements or other appropriate notification or inspection procedures to assure that hazardous wastes are not received at or burned in such facility.
BOARD NOTE: The U.S. Supreme Court determined, in City of Chicago v. Environmental Defense Fund, Inc., 511 U.S. 328, 114 S. Ct. 1588, 128 L. Ed. 2d 302 (1994), that this exclusion and RCRA section 3001(i) (42 USC 6921(i)) do not exclude the ash from facilities covered by this subsection (b)(1) from regulation as a hazardous waste. At 59 Fed. Reg. 29372 (June 7, 1994), USEPA granted facilities managing ash from such facilities that is determined a hazardous waste under Subpart C until December 7, 1994 to file a Part A permit application under 35 Ill. Adm. Code 703.181. At 60 Fed. Reg. 6666 (Feb. 3, 1995), USEPA stated that it interpreted that the point at which ash becomes subject to RCRA Subtitle C regulation is when that material leaves the combustion building (including connected air pollution control equipment).
2) Solid wastes generated by any of the following that are returned to the soil as fertilizers:
A) The growing and harvesting of agricultural crops; or
B) The raising of animals, including animal manures.
3) Mining overburden returned to the mine site.
4) Coal and Fossil Fuel Combustion Waste
A) Fly ash waste, bottom ash waste, slag waste, and flue gas emission control waste generated primarily from the combustion of coal or other fossil fuels, except as provided in 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste.
B) The following wastes generated primarily from processes that support the combustion of coal or other fossil fuels that are co-disposed with the wastes in subsection (b)(4)(A), except as provided by 35 Ill. Adm. Code 726.112 for facilities that burn or process hazardous waste:
i) Coal Pile Run-Off. For purposes of this subsection (b)(4), “coal pile run-off” means any precipitation that drains off coal piles.
ii) Boiler Cleaning Solutions. For purposes of this subsection (b)(4), “boiler cleaning solutions” means water solutions and chemical solutions used to clean the fire-side and waterside of the boiler.
iii) Boiler Blowdown. For purposes of this subsection (b)(4), “boiler blowdown” means water purged from boilers used to generate steam.
iv) Process Water Treatment and Demineralizer Regeneration Wastes. For purposes of this subsection (b)(4), “process water treatment and demineralizer regeneration wastes” means sludges, rinses, and spent resins generated from processes to remove dissolved gases, suspended solids, and dissolved chemical salts from combustion system process water.
v) Cooling Tower Blowdown. For purposes of this subsection (b)(4), “cooling tower blowdown” means water purged from a closed cycle cooling system. Closed cycle cooling systems include cooling towers, cooling ponds, or spray canals.
vi) Air Heater and Precipitator Washes. For purposes of this subsection (b)(4), “air heater and precipitator washes” means wastes from cleaning air preheaters and electrostatic precipitators.
vii) Effluents from Floor and Yard Drains and Sumps. For purposes of this subsection (b)(4), “effluents from floor and yard drains and sumps” means wastewaters, such as wash water, collected by or from floor drains, equipment drains, and sumps located inside the power plant building; and wastewaters, such as rain run-off, collected by yard drains and sumps located outside the power plant building.
viii) Wastewater Treatment Sludges. For purposes of this subsection (b)(4), “wastewater treatment sludges” refers to sludges generated from the treatment of wastewaters specified in subsections (b)(4)(B)(i) through (b)(4)(B)(vi).
5) Drilling fluids, produced waters, and other wastes associated with the exploration, development, or production of crude oil, natural gas, or geothermal energy.
6) Chromium Wastes
A) Wastes that fail the test for the toxicity characteristic (Section 721.124 and Appendix B) because chromium is present or that are listed in Subpart D due to the presence of chromium, that do not fail the test for the toxicity characteristic for any other constituent or that are not listed due to the presence of any other constituent, and that do not fail the test for any other characteristic, if the waste generator shows the following:
i) The chromium in the waste is exclusively (or nearly exclusively) trivalent chromium;
ii) The waste is generated from an industrial process that uses trivalent chromium exclusively (or nearly exclusively) and the process does not generate hexavalent chromium; and
iii) The waste is typically and frequently managed in non-oxidizing environments.
B) The following are specific wastes that meet the standard in subsection (b)(6)(A) (so long as they do not fail the test for the toxicity characteristic for any other constituent and do not exhibit any other characteristic):
i) Chrome (blue) trimmings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling;
ii) Chrome (blue) shavings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling;
iii) Buffing dust generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue;
iv) Sewer screenings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling;
v) Wastewater treatment sludges generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling;
vi) Wastewater treatment sludges generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, and through-the-blue;
vii) Waste scrap leather from the leather tanning industry, the shoe manufacturing industry, and other leather product manufacturing industries; and
viii) Wastewater treatment sludges from the production of titanium dioxide pigment using chromium-bearing ores by the chloride process.
7) Solid waste from the extraction, beneficiation, and processing of ores and minerals (including coal, phosphate rock, and overburden from the mining of uranium ore), except as provided by 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste.
A) For purposes of this subsection (b)(7), beneficiation of ores and minerals is restricted to the following activities: crushing; grinding; washing; dissolution; crystallization; filtration; sorting; sizing; drying; sintering; pelletizing; briquetting; calcining to remove water or carbon dioxide; roasting; autoclaving or chlorination in preparation for leaching (except if the roasting (or autoclaving or chlorination) and leaching sequence produces a final or intermediate product that does not undergo further beneficiation or processing); gravity concentration; magnetic separation; electrostatic separation; floatation; ion exchange; solvent extraction; electrowinning; precipitation; amalgamation; and heap, dump, vat tank, and in situ leaching.
B) For the purposes of this subsection (b)(7), solid waste from the processing of ores and minerals includes only the following wastes as generated:
i) Slag from primary copper processing;
ii) Slag from primary lead processing;
iii) Red and brown muds from bauxite refining;
iv) Phosphogypsum from phosphoric acid production;
v) Slag from elemental phosphorus production;
vi) Gasifier ash from coal gasification;
vii) Process wastewater from coal gasification;
viii) Calcium sulfate wastewater treatment plant sludge from primary copper processing;
ix) Slag tailings from primary copper processing;
x) Fluorogypsum from hydrofluoric acid production;
xi) Process wastewater from hydrofluoric acid production;
xii) Air pollution control dust or sludge from iron blast furnaces;
xiii) Iron blast furnace slag;
xiv) Treated residue from roasting and leaching of chrome ore;
xv) Process wastewater from primary magnesium processing by the anhydrous process;
xvi) Process wastewater from phosphoric acid production;
xvii) Basic oxygen furnace and open-hearth furnace air pollution control dust or sludge from carbon steel production;
xviii) Basic oxygen furnace and open-hearth furnace slag from carbon steel production;
xix) Chloride processing waste solids from titanium tetrachloride production; and
xx) Slag from primary zinc production.
C) A residue derived from co-processing mineral processing secondary materials with normal beneficiation raw materials or with normal mineral processing raw materials remains excluded under this subsection (b) if the following conditions are fulfilled:
i) The owner or operator processes at least 50 percent by weight normal beneficiation raw materials or normal mineral processing raw materials; and
ii) The owner or operator legitimately reclaims the secondary mineral processing materials.
8) Cement kiln dust waste, except as provided by 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste.
9) Solid waste that consists of discarded arsenical-treated wood or wood products that fails the test for the toxicity characteristic for USEPA hazardous waste numbers D004 through D017 and that is not a hazardous waste for any other reason if the waste is generated by persons that utilize the arsenical-treated wood and wood products for these materials’ intended end use.
10) Petroleum-contaminated media and debris that fail the test for the toxicity characteristic of Section 721.124 (USEPA hazardous waste numbers D018 through D043 only) and that are subject to corrective action regulations under 35 Ill. Adm. Code 731.
11) This subsection (b)(11) corresponds with 40 CFR 261.4(b)(11), which expired by its own terms on January 25, 1993. This statement maintains structural parity with USEPA regulations.
12) Used chlorofluorocarbon refrigerants from totally enclosed heat transfer equipment, including mobile air conditioning systems, mobile refrigeration, and commercial and industrial air conditioning and refrigeration systems, that use chlorofluorocarbons as the heat transfer fluid in a refrigeration cycle, provided the refrigerant is reclaimed for further use.
13) Non-terne plated used oil filters that are not mixed with wastes listed in Subpart D, if these oil filters have been gravity hot-drained using one of the following methods:
A) Puncturing the filter anti-drain back valve or the filter dome end and hot-draining;
B) Hot-draining and crushing;
C) Dismantling and hot-draining; or
D) Any other equivalent hot-draining method that will remove used oil.
14) Used oil re-refining distillation bottoms that are used as feedstock to manufacture asphalt products.
15) Leachate or gas condensate collected from landfills where certain solid wastes have been disposed of, under the following circumstances:
A) The following conditions must be fulfilled:
i) The solid wastes disposed of would meet one or more of the listing descriptions for the following USEPA hazardous waste numbers that are generated after the effective date listed for the waste:
USEPA Hazardous Waste Numbers | Listing Effective Date |
K169, K170, K171, and K172 | February 8, 1999 |
K174 and K175 | May 7, 2001 |
K176, K177, and K178 | May 20, 2002 |
K181 | August 23, 2005 |
iii) The leachate or gas condensate does not exhibit any characteristic of hazardous waste nor is derived from any other listed hazardous waste; and
iv) Discharge of the leachate or gas condensate, including leachate or gas condensate transferred from the landfill to a POTW by truck, rail, or dedicated pipe, is subject to regulation under section 307(b) or 402 of the federal Clean Water Act (33 USC 1317(b) or 1342).
B) Leachate or gas condensate derived from K169, K170, K171, K172, K176, K177, K178, or K181 waste will no longer be exempt if it is stored or managed in a surface impoundment prior to discharge. There is one exception: if the surface impoundment is used to temporarily store leachate or gas condensate in response to an emergency situation (e.g., shutdown of wastewater treatment system), provided the impoundment has a double liner, and provided the leachate or gas condensate is removed from the impoundment and continues to be managed in compliance with the conditions of this subsection (b)(15) after the emergency ends.
16) This subsection (b)(16) corresponds with 40 CFR 261.4(b)(16), which USEPA has marked “reserved”. This statement maintains structural parity with USEPA regulations.
17) This subsection (b)(17) corresponds with 40 CFR 261.4(b)(17), which pertains exclusively to waste generated by a specific facility outside Illinois. This statement maintains structural parity with USEPA regulations.
18) Solvent-contaminated wipes, except for wipes that are hazardous waste due to the presence of trichloroethylene, that are sent for disposal are not hazardous wastes from the point of generation provided that all of the following conditions are fulfilled:
A) The solvent-contaminated wipes, when accumulated, stored, and transported, are contained in non-leaking, closed containers that are labeled “Excluded Solvent-Contaminated Wipes”. The containers must be able to contain free liquids, should free liquids occur. During accumulation, a container is considered closed when there is complete contact between the fitted lid and the rim, except when it is necessary to add or remove solvent-contaminated wipes. When the container is full, when the solvent-contaminated wipes are no longer being accumulated, or when the container is being transported, the container must be sealed with all lids properly and securely affixed to the container and all openings tightly bound or closed sufficiently to prevent leaks and emissions;
B) The solvent-contaminated wipes may be accumulated by the generator for up to 180 days from the start date of accumulation for each container prior to being sent for disposal;
C) At the point of being transported for disposal, the solvent-contaminated wipes must contain no free liquids, as defined in 35 Ill. Adm. Code 720.110;
D) Free liquids removed from the solvent-contaminated wipes or from the container holding the wipes must be managed according to the applicable regulations found in this Part and 35 Ill. Adm. Code 720, 722 through 728, and 733;
E) Generators must maintain at their site the following documentation:
i) The name and address of the landfill or combustor that is receiving the solvent-contaminated wipes;
ii) The documentation that the 180-day accumulation time limit in 35 Ill. Adm. Code 721.104(b)(18)(B) is being met; and
iii) A description of the process the generator is using to ensure that the solvent-contaminated wipes contain no free liquids at the point of being transported for disposal; and
F) The solvent-contaminated wipes are sent for disposal at one of the following facilities:
i) A municipal solid waste landfill regulated under RCRA Subtitle D regulations: 35 Ill. Adm. Code 810 through 815, including the landfill design criteria of 35 Ill. Adm. Code 811.303 through 811.309, 811.315 through 811.317, and Subpart E of 35 Ill. Adm. Code 811 or 35 Ill. Adm. Code 814.302 and 814.402; 40 CFR 258, including the landfill design criteria of 40 CFR 258.40; or equivalent regulations of a sister state that USEPA has approved under 42 USC 6943 and 6947; or
ii) A hazardous waste landfill regulated under RCRA Subtitle C regulations: 35 Ill. Adm. Code 724 or 725; 40 CFR 264 or 265; or equivalent regulations of a sister state that USEPA has approved under 42 USC 6926; or
iii) A municipal waste combustor or other combustion facility regulated under section 129 of the Clean Air Act (42 USC 7429) or equivalent Illinois or sister-state regulations approved by USEPA under 42 USC 7429; or
iv) A hazardous waste combustor, boiler, or industrial furnace regulated under RCRA Subtitle C regulations: 35 Ill. Adm. Code 724 or 725 or Subpart H of 35 Ill. Adm. Code 726; 40 CFR 264 or 265 or subpart H of 40 CFR 266; or equivalent regulations of a sister state that USEPA has approved under 42 USC 6926.
c) Hazardous wastes that are exempted from certain regulations. A hazardous waste that is generated in a product or raw material storage tank, a product or raw material transport vehicle or vessel, a product or raw material pipeline, or in a manufacturing process unit, or an associated non-waste-treatment manufacturing unit, is not subject to regulation under 35 Ill. Adm. Code 702, 703, and 722 through 728 or to the notification requirements of section 3010 of RCRA (42 USC 6930) until it exits the unit in which it was generated, unless the unit is a surface impoundment, or unless the hazardous waste remains in the unit more than 90 days after the unit ceases to be operated for manufacturing or for storage or transportation of product or raw materials.
d) Samples
1) Except as provided in subsections (d)(2) and (d)(4), a sample of solid waste or a sample of water, soil, or air that is collected for the sole purpose of testing to determine its characteristics or composition is not subject to any requirements of this Part or 35 Ill. Adm. Code 702, 703, and 722 through 728. The sample qualifies when it fulfills one of the following conditions:
A) The sample is being transported to a laboratory for the purpose of testing;
B) The sample is being transported back to the sample collector after testing;
C) The sample is being stored by the sample collector before transport to a laboratory for testing;
D) The sample is being stored in a laboratory before testing;
E) The sample is being stored in a laboratory for testing but before it is returned to the sample collector; or
F) The sample is being stored temporarily in the laboratory after testing for a specific purpose (for example, until conclusion of a court case or enforcement action if further testing of the sample may be necessary).
2) In order to qualify for the exemption in subsection (d)(1)(A) or (d)(1)(B), a sample collector shipping samples to a laboratory and a laboratory returning samples to a sample collector must do the following:
A) Comply with USDOT, U.S. Postal Service (USPS), or any other applicable shipping requirements; or
B) Comply with the following requirements if the sample collector determines that USDOT, USPS, or other shipping requirements do not apply to the shipment of the sample:
i) Assure that the following information accompanies the sample: The sample collector’s name, mailing address, and telephone number; the laboratory’s name, mailing address, and telephone number; the quantity of the sample; the date of the shipment; and a description of the sample; and
ii) Package the sample so that it does not leak, spill, or vaporize from its packaging.
3) This exemption does not apply if the laboratory determines that the waste is hazardous, but the laboratory is no longer meeting any of the conditions stated in subsection (d)(1).
4) In order to qualify for the exemption in subsections (d)(1)(A) and (d)(1)(B), the mass of a sample that will be exported to a foreign laboratory or that will be imported to a U.S. laboratory from a foreign source must additionally not exceed 25 kg.
e) Treatability Study Samples
1) Except as is provided in subsections (e)(2) and (e)(4), a person that generates or collects samples for the purpose of conducting treatability studies, as defined in 35 Ill. Adm. Code 720.110, are not subject to any requirement of 35 Ill. Adm. Code 721 through 723 or to the notification requirements of section 3010 of RCRA (42 USC 6930). Nor are such samples included in the quantity determinations of 35 Ill. Adm. Code 722.114 and 722.116 when:
A) The sample is being collected and prepared for transportation by the generator or sample collector;
B) The sample is being accumulated or stored by the generator or sample collector prior to transportation to a laboratory or testing facility; or
C) The sample is being transported to the laboratory or testing facility for the purpose of conducting a treatability study.
2) The exemption in subsection (e)(1) is applicable to samples of hazardous waste being collected and shipped for the purpose of conducting treatability studies provided that the following conditions are fulfilled:
A) The generator or sample collector uses (in “treatability studies”) no more than 10,000 kg of media contaminated with non-acute hazardous waste, 1,000 kg of non-acute hazardous waste other than contaminated media, 1 kg of acute hazardous waste, or 2,500 kg of media contaminated with acute hazardous waste for each process being evaluated for each generated waste stream;
B) The mass of each shipment does not exceed 10,000 kg; the 10,000 kg quantity may be all media contaminated with non-acute hazardous waste, or may include 2,500 kg of media contaminated with acute hazardous waste, 1,000 kg of hazardous waste, and 1 kg of acute hazardous waste;
C) The sample must be packaged so that it does not leak, spill, or vaporize from its packaging during shipment and the requirements of subsection (e)(2)(C)(i) or (e)(2)(C)(ii) are met.
i) The transportation of each sample shipment complies with USDOT, USPS, or any other applicable shipping requirements; or
ii) If the USDOT, USPS, or other shipping requirements do not apply to the shipment of the sample, the following information must accompany the sample: The name, mailing address, and telephone number of the originator of the sample; the name, address, and telephone number of the facility that will perform the treatability study; the quantity of the sample; the date of the shipment; and, a description of the sample, including its USEPA hazardous waste number;
D) The sample is shipped to a laboratory or testing facility that is exempt under subsection (f), or has an appropriate RCRA permit or interim status;
E) The generator or sample collector maintains the following records for a period ending three years after completion of the treatability study:
i) Copies of the shipping documents;
ii) A copy of the contract with the facility conducting the treatability study; and
iii) Documentation showing the following: The amount of waste shipped under this exemption; the name, address, and USEPA identification number of the laboratory or testing facility that received the waste; the date the shipment was made; and whether or not unused samples and residues were returned to the generator; and
F) The generator reports the information required in subsection (e)(2)(E)(iii) in its report under 35 Ill. Adm. Code 722.141.
3) The Agency may grant requests on a case-by-case basis for up to an additional two years for treatability studies involving bioremediation. The Agency may grant requests, on a case-by-case basis, for quantity limits in excess of those specified in subsections (e)(2)(A), (e)(2)(B), and (f)(4), for up to an additional 5,000 kg of media contaminated with non-acute hazardous waste, 500 kg of non-acute hazardous waste, 2,500 kg of media contaminated with acute hazardous waste, and 1 kg of acute hazardous waste under the circumstances set forth in either subsection (e)(3)(A) or (e)(3)(B), subject to the limitations of subsection (e)(3)(C):
A) In response to requests for authorization to ship, store, and conduct further treatability studies on additional quantities in advance of commencing treatability studies. Factors to be considered in reviewing such requests include the nature of the technology, the type of process (e.g., batch versus continuous), the size of the unit undergoing testing (particularly in relation to scale-up considerations), the time or quantity of material required to reach steady-state operating conditions, or test design considerations, such as mass balance calculations.
B) In response to requests for authorization to ship, store, and conduct treatability studies on additional quantities after initiation or completion of initial treatability studies when the following occurs: There has been an equipment or mechanical failure during the conduct of the treatability study, there is need to verify the results of a previously-conducted treatability study, there is a need to study and analyze alternative techniques within a previously-evaluated treatment process, or there is a need to do further evaluation of an ongoing treatability study to determine final specifications for treatment.
C) The additional quantities and timeframes allowed in subsections (e)(3)(A) and (e)(3)(B) are subject to all the provisions in subsections (e)(1) and (e)(2)(B) through (e)(2)(F). The generator or sample collector must apply to the Agency and provide in writing the following information:
i) The reason why the generator or sample collector requires additional time or quantity of sample for the treatability study evaluation and the additional time or quantity needed;
ii) Documentation accounting for all samples of hazardous waste from the waste stream that have been sent for or undergone treatability studies, including the date each previous sample from the waste stream was shipped, the quantity of each previous shipment, the laboratory or testing facility to which it was shipped, what treatability study processes were conducted on each sample shipped, and the available results of each treatability study;
iii) A description of the technical modifications or change in specifications that will be evaluated and the expected results;
iv) If such further study is being required due to equipment or mechanical failure, the applicant must include information regarding the reason for the failure or breakdown and also include what procedures or equipment improvements have been made to protect against further breakdowns; and
v) Such other information as the Agency determines is necessary.
4) In order to qualify for the exemption in subsection (e)(1)(A), the mass of a sample that will be exported to a foreign laboratory or testing facility, or that will be imported to a U.S. laboratory or testing facility from a foreign source must additionally not exceed 25 kg.
5) Final Agency determinations under this subsection (e) may be appealed to the Board.
f) Samples undergoing treatability studies at laboratories or testing facilities. Samples undergoing treatability studies and the laboratory or testing facility conducting such treatability studies (to the extent such facilities are not otherwise subject to RCRA requirements) are not subject to any requirement of this Part, or of 35 Ill. Adm. Code 702, 703, 722 through 726, and 728 or to the notification requirements of section 3010 of RCRA (42 USC 6930), provided that the requirements of subsections (f)(1) through (f)(11) are met. A mobile treatment unit may qualify as a testing facility subject to subsections (f)(1) through (f)(11). Where a group of mobile treatment units are located at the same site, the limitations specified in subsections (f)(1) through (f)(11) apply to the entire group of mobile treatment units collectively as if the group were one mobile treatment unit.
1) No less than 45 days before conducting treatability studies, the facility notifies the Agency in writing that it intends to conduct treatability studies under this subsection (f).
2) The laboratory or testing facility conducting the treatability study has a USEPA identification number.
3) No more than a total of 10,000 kg of “as received” media contaminated with non-acute hazardous waste, 2,500 kg of media contaminated with acute hazardous waste, or 250 kg of other “as received” hazardous waste is subject to initiation of treatment in all treatability studies in any single day. “As received” waste refers to the waste as received in the shipment from the generator or sample collector.
4) The quantity of “as received” hazardous waste stored at the facility for the purpose of evaluation in treatability studies does not exceed 10,000 kg, the total of which can include 10,000 kg of media contaminated with non-acute hazardous waste, 2,500 kg of media contaminated with acute hazardous waste, 1,000 kg of non-acute hazardous wastes other than contaminated media, and 1 kg of acute hazardous waste. This quantity limitation does not include treatment materials (including non-hazardous solid waste) added to “as received” hazardous waste.
5) No more than 90 days have elapsed since the treatability study for the sample was completed, or no more than one year (two years for treatability studies involving bioremediation) has elapsed since the generator or sample collector shipped the sample to the laboratory or testing facility, whichever date first occurs. Up to 500 kg of treated material from a particular waste stream from treatability studies may be archived for future evaluation up to five years from the date of initial receipt. Quantities of materials archived are counted against the total storage limit for the facility.
6) The treatability study does not involve the placement of hazardous waste on the land or open burning of hazardous waste.
7) The facility maintains records for three years following completion of each study that show compliance with the treatment rate limits and the storage time and quantity limits. The following specific information must be included for each treatability study conducted:
A) The name, address, and USEPA identification number of the generator or sample collector of each waste sample;
B) The date the shipment was received;
C) The quantity of waste accepted;
D) The quantity of “as received” waste in storage each day;
E) The date the treatment study was initiated and the amount of “as received” waste introduced to treatment each day;
F) The date the treatability study was concluded;
G) The date any unused sample or residues generated from the treatability study were returned to the generator or sample collector or, if sent to a designated facility, the name of the facility and the USEPA identification number.
8) The facility keeps, on-site, a copy of the treatability study contract and all shipping papers associated with the transport of treatability study samples to and from the facility for a period ending three years from the completion date of each treatability study.
9) The facility prepares and submits a report to the Agency, by March 15 of each year, that includes the following information for the previous calendar year:
A) The name, address, and USEPA identification number of the facility conducting the treatability studies;
B) The types (by process) of treatability studies conducted;
C) The names and addresses of persons for whom studies have been conducted (including their USEPA identification numbers);
D) The total quantity of waste in storage each day;
E) The quantity and types of waste subjected to treatability studies;
F) When each treatability study was conducted; and
G) The final disposition of residues and unused sample from each treatability study.
10) The facility determines whether any unused sample or residues generated by the treatability study are hazardous waste under Section 721.103 and, if so, are subject to 35 Ill. Adm. Code 702, 703, and 721 through 728, unless the residues and unused samples are returned to the sample originator under the exemption of subsection (e).
11) The facility notifies the Agency by letter when the facility is no longer planning to conduct any treatability studies at the site.
g) Dredged Material That Is Not a Hazardous Waste. Dredged material that is subject to the requirements of a permit that has been issued under section 404 of the Federal Water Pollution Control Act (33 USC 1344) is not a hazardous waste. For the purposes of this subsection (g), the following definitions apply:
“Dredged material” has the meaning ascribed it in 40 CFR 232.2 (Definitions), incorporated by reference in 35 Ill. Adm. Code 720.111(b).
“Permit” means any of the following:
A permit issued by the U.S. Army Corps of Engineers (Army Corps) under section 404 of the Federal Water Pollution Control Act (33 USC 1344);
A permit issued by the Army Corps under section 103 of the Marine Protection, Research, and Sanctuaries Act of 1972 (33 USC 1413); or
In the case of Army Corps civil works projects, the administrative equivalent of the permits referred to in the preceding two paragraphs of this definition, as provided for in Army Corps regulations (for example, see 33 CFR 336.1, 336.2, and 337.6).
h) Carbon Dioxide Stream Injected for Geologic Sequestration. Carbon dioxide streams that are captured and transported for purposes of injection into an underground injection well subject to the requirements for Class VI carbon sequestration injection wells, including the requirements in 35 Ill. Adm. Code 704 and 730, are not a hazardous waste, provided the following conditions are met:
1) Transportation of the carbon dioxide stream must be in compliance with U.S. Department of Transportation requirements, including the pipeline safety laws (chapter 601 of subtitle VIII of 49 USC, incorporated by reference in 35 Ill. Adm. Code 720.111) and regulations (49 CFR 190 through 199, incorporated by reference in 35 Ill. Adm. Code 720.111) of the U.S. Department of Transportation, and pipeline safety regulations adopted and administered by a state authority under a certification under 49 USC 60105, incorporated by reference in 35 Ill. Adm. Code 720.111, and 49 CFR 171 through 180, incorporated by reference in 35 Ill. Adm. Code 720.111, as applicable;
BOARD NOTE: The parenthetical language relating to pipeline transportation does not preclude transportation by air, water, highway, or rail that complies with U.S. Department of Transportation regulations at 49 CFR 171 through 180. For this reason, the Board has added citations of those regulations.
2) Injection of the carbon dioxide stream must comply with the applicable requirements for Class VI carbon sequestration injection wells, including the applicable requirements in 35 Ill. Adm. Code 704 and 730;
3) No hazardous wastes may be mixed with, or otherwise co-injected with, the carbon dioxide stream; and
4) Required Certifications
A) Any generator of a carbon dioxide stream, who claims that a carbon dioxide stream is excluded under this subsection (h), must have an authorized representative (as defined in 35 Ill. Adm. Code 720.110) sign a certification statement worded as follows:
“I certify under penalty of law that the carbon dioxide stream that I am claiming to be excluded under 35 Ill. Adm. Code 721.104(h) has not been mixed with hazardous wastes, and I have transported the carbon dioxide stream in compliance with (or have contracted with a pipeline operator or transporter to transport the carbon dioxide stream in compliance with) U.S. Department of Transportation requirements, including the pipeline safety laws (49 USC 60101 et seq.) and regulations (49 CFR Parts 190 through 199) of the U.S. Department of Transportation, and the pipeline safety regulations adopted and administered by a state authority pursuant to a certification under 49 USC 60105, as applicable, for injection into a well subject to the requirements for the Class VI Underground Injection Control Program of the federal Safe Drinking Water Act (42 USC 300f et seq.).”
B) Any Class VI carbon sequestration injection well owner or operator, who claims that a carbon dioxide stream is excluded under this subsection (h), must have an authorized representative (as defined in 35 Ill. Adm. Code 720.110) sign a certification statement worded as follows:
“I certify under penalty of law that the carbon dioxide stream that I am claiming to be excluded under 35 Ill. Adm. Code 721.104(h) has not been mixed with, or otherwise co-injected with, hazardous waste at the UIC Class VI permitted facility, and that injection of the carbon dioxide stream is in compliance with the applicable requirements for UIC Class VI wells, including the applicable requirements in 35 Ill. Adm. Code 704 and 730.”
C) The signed certification statement must be kept on-site, for no less than three years, and must be made available within 72 hours after a written request from the Agency or USEPA, or their designee. The signed certification statement must be renewed every year that the exclusion is claimed, by having an authorized representative (as defined in 35 Ill. Adm. Code 720.110) annually prepare and sign a new copy of the certification statement within one year after the date of the previous statement. The signed certification statement must also be readily accessible on the facility’s publicly-available website (if such website exists) as a public notification with the title of “Carbon Dioxide Stream Certification” at the time the exclusion is claimed.
i) This subsection corresponds with 40 CFR 261.4(i), which USEPA marked “Reserved”. This statement maintains structural consistency with the federal regulation.
j) Airbag Waste
1) At the airbag waste handler or during transport to an airbag waste collection facility or designated facility, airbag waste is not subject to regulation under 35 Ill. Adm. Code 702, 703, and 722 through 728 and is not subject to the notification requirements of section 3010 of RCRA provided that the airbag waste handler or transporter fulfills the following conditions:
A) The airbag waste handler or transporter accumulates the airbag waste in a quantity of no more than 250 airbag modules or airbag inflators for no longer than 180 days;
B) The airbag waste handler or transporter packages the airbag waste in a container designed to address the risk posed by the airbag waste and labeled “Airbag Waste—Do Not Reuse”;
C) The airbag waste handler or transporter sends the airbag waste directly to either of the following facilities:
i) An airbag waste collection facility in the United States that is under the control of a vehicle manufacturer or its authorized representative or that is under the control of a person authorized to administer a remedy program in response to a vehicle safety recall under 49 USC 30120; or
ii) A designated facility, as defined in 35 Ill. Adm. Code 720.110;
D) The transport of the airbag waste complies with all applicable USDOT regulations in 49 CFR 171 through 180 during transit; and
E) The airbag waste handler maintains at the handler facility, for no less than three years, records of each off-site shipment of airbag waste and each confirmation of receipt from the receiving facility. For each shipment, these records must, at a minimum, contain the name of the transporter, the date of the shipment, the name and address of the receiving facility, and the type and quantity of airbag waste (i.e., airbag modules or airbag inflators) in the shipment. A confirmation of receipt must include the name and address of the receiving facility, the type and quantity of the airbag waste (i.e., airbag modules and airbag inflators) received, and the date when the airbag waste collection facility received the airbag waste. The airbag waste handler must make shipping records and confirmations of receipt available for inspection and may satisfy this requirement using routine business records (e.g., electronic or paper financial records, bills of lading, copies of USDOT shipping papers, electronic confirmations of receipt, etc.).
2) Once the airbag waste arrives at an airbag waste collection facility or designated facility, it becomes subject to all applicable hazardous waste regulations. The facility receiving airbag waste is considered the hazardous waste generator for the purposes of the hazardous waste regulations and must comply with the requirements of 35 Ill. Adm. Code 722.
3) Reuse in vehicles of defective airbag modules or defective airbag inflators that are subject to a recall under 49 USC 30120 is considered sham recycling and prohibited under 35 Ill. Adm. Code 721.102(g).
BOARD NOTE: This precludes any possibility that reuse qualifies for recycling-based exclusion from the definition of solid waste. Federal law prohibits selling defective recalled motor vehicle equipment if it may reasonably be used for its original purpose. (See 42 USC 30120(j).)
(Source: Amended at 44 Ill. Reg. 15142, effective September 3, 2020)
Section 721.105 Special Requirements for Hazardous Waste Generated by Small Quantity Generators
a) A generator is a conditionally exempt small quantity generator (CESQG) in a calendar month if it generates no more than 100 kilograms of hazardous waste in that month.
b) Except for those wastes identified in subsections (e), (f), (g), and (j) of this Section, a CESQG’s hazardous wastes are not subject to regulation under 35 Ill. Adm. Code 702, 703, and 722 through 728, and the notification requirements of section 3010 of Resource Conservation and Recovery Act, provided the generator complies with subsections (f), (g), and (j) of this Section.
c) When making the quantity determinations of this Part and 35 Ill. Adm. Code 722, the generator must include all hazardous waste that it generates, except the following hazardous waste:
1) Hazardous waste that is exempt from regulation under Section 721.104(c) through (f), 721.106(a)(3), 721.107(a)(1), or 721.108;
2) Hazardous waste that is managed immediately upon generation only in on-site elementary neutralization units, wastewater treatment units, or totally enclosed treatment facilities, as defined in 35 Ill. Adm. Code 720.110;
3) Hazardous waste that is recycled, without prior storage or accumulation, only in an on-site process subject to regulation under Section 721.106(c)(2);
4) Hazardous waste that is used oil managed pursuant to Section 721.106(a)(4) and 35 Ill. Adm. Code 739;
5) Hazardous waste that is spent lead-acid batteries managed pursuant to Subpart G of 35 Ill. Adm. Code 726;
6) Hazardous waste that is universal waste managed pursuant to Section 721.109 and 35 Ill. Adm. Code 733; and
7) Hazardous waste that is an unused commercial chemical product (that is listed in Subpart D of 35 Ill. Adm. Code 721 or which exhibits one or more characteristics in Subpart C of 35 Ill. Adm. Code 721) that is generated solely as a result of a laboratory clean-out conducted at an eligible academic entity pursuant to Section 722.313. For purposes of this subsection (c)(7), the term “eligible academic entity” has the meaning given that term in 35 Ill. Adm. Code 722.300.
d) In determining the quantity of hazardous waste it generates, a generator need not include the following:
1) Hazardous waste when it is removed from on-site storage;
2) Hazardous waste produced by on-site treatment (including reclamation) of its hazardous waste so long as the hazardous waste that is treated was counted once;
3) Spent materials that are generated, reclaimed, and subsequently reused on-site, so long as such spent materials have been counted once.
e) If a generator generates acute hazardous waste in a calendar month in quantities greater than those set forth in subsections (e)(1) and (e)(2) of this Section, all quantities of that acute hazardous waste are subject to full regulation under 35 Ill. Adm. Code 702, 703, and 722 through 728, and the notification requirements of section 3010 of the Resource Conservation and Recovery Act.
1) A total of one kilogram of one or more of the acute hazardous wastes listed in Section 721.131 or 721.133(e); or
2) A total of 100 kilograms of any residue or contaminated soil, waste, or other debris resulting from the clean-up of a spill, into or on any land or water, of any one or more of the acute hazardous wastes listed in Section 721.131 or 721.133(e).
BOARD NOTE: “Full regulation” means those regulations applicable to generators of 1,000 kg or greater of hazardous waste in a calendar month.
f) In order for acute hazardous wastes generated by a generator of acute hazardous wastes in quantities equal to or less than those set forth in subsections (e)(1) or (e)(2) of this Section to be excluded from full regulation under this Section, the generator must comply with the following requirements:
1) 35 Ill. Adm. Code 722.111.
2) The generator may accumulate acute hazardous waste on-site. If the generator accumulates at any time acute hazardous wastes in quantities greater than set forth in subsection (e)(1) or (e)(2) of this Section, all of those accumulated wastes are subject to regulation under 35 Ill. Adm. Code 702, 703, and 722 through 728, and the applicable notification requirements of section 3010 of the Resource Conservation and Recovery Act. The time period of 35 Ill. Adm. Code 722.134(a), for accumulation of wastes on-site, begins when the accumulated wastes exceed the applicable exclusion limit.
3) A CESQG may either treat or dispose of its acute hazardous waste in an on-site facility or ensure delivery to an off-site treatment, storage, or disposal facility, any of which, if located in the United States, meets any of the following conditions:
A) The facility is permitted under 35 Ill. Adm. Code 702 and 703;
B) The facility has interim status under 35 Ill. Adm. Code 702, 703, and 725;
C) The facility is authorized to manage hazardous waste by a state with a hazardous waste management program approved by USEPA pursuant to 40 CFR 271;
D) The facility is permitted, licensed, or registered by a state to manage municipal solid waste and, if managed in a municipal solid waste landfill facility, the landfill is subject to 35 Ill. Adm. Code 810 through 814 or federal 40 CFR 258;
E) The facility is permitted, licensed, or registered by a state to manage non-municipal non-hazardous waste and, if managed in a non-municipal non-hazardous waste disposal unit, the unit is subject to federal 40 CFR 257.5 through 257.30;
BOARD NOTE: The Illinois non-hazardous waste landfill regulations, 35 Ill. Adm. Code 810 through 814, do not allow the disposal of hazardous waste in a landfill regulated under those rules. The Board intends that subsections (f)(3)(D) and (f)(3)(E) of this Section impose a federal requirement on the hazardous waste generator. The Board specifically does not intend that these subsections authorize any disposal of conditionally-exempt small quantity generator waste in a landfill not specifically permitted to accept the particular hazardous waste.
F) The facility is one that fulfills one of the following conditions:
i) It beneficially uses or reuses or legitimately recycles or reclaims its waste; or
ii) It treats its waste prior to beneficial use or reuse or legitimate recycling or reclamation; or
G) For universal waste managed under 35 Ill. Adm. Code 733 or federal 40 CFR 273, the facility is a universal waste handler or destination facility subject to 35 Ill. Adm. Code 733 or federal 40 CFR 273.
g) In order for hazardous waste generated by a CESQG in quantities of 100 kilograms or less kilograms of hazardous waste during a calendar month to be excluded from full regulation under this Section, the generator must comply with the following requirements:
1) 35 Ill. Adm. Code 722.111;
2) The CESQG may accumulate hazardous waste on-site. If it accumulates at any time 1,000 kilograms or greater of the generator’s hazardous waste, all of those accumulated wastes are subject to regulation pursuant to the special provisions of 35 Ill. Adm. Code 722 applicable to generators of greater than 100 kg and less than 1,000 kg of hazardous waste in a calendar month, as well as 35 Ill. Adm. Code 702, 703, and 723 through 728, and the applicable notification requirements of Section 3010 of the Resource Conservation and Recovery Act. The time period of 35 Ill. Adm. Code 722.134(d) for accumulation of wastes on-site begins for a small quantity generator when the accumulated wastes equal or exceed 1,000 kilograms;
3) A CESQG may either treat or dispose of its hazardous waste in an on-site facility or ensure delivery to an off-site treatment, storage, or disposal facility, any of which, if located in the United States, meets any of the following conditions:
A) The facility is permitted under 35 Ill. Adm. Code 702 and 703;
B) The facility has interim status under 35 Ill. Adm. Code 702, 703, and 725;
C) The facility is authorized to manage hazardous waste by a state with a hazardous waste management program approved by USEPA pursuant to 40 CFR 271;
D) The facility is permitted, licensed, or registered by a state to manage municipal solid waste and, if managed in a municipal solid waste landfill facility, the landfill is subject to 35 Ill. Adm. Code 810 through 814 or federal 40 CFR 258;
E) The facility is permitted, licensed, or registered by a state to manage non-municipal non-hazardous waste and, if managed in a non-municipal non-hazardous waste disposal unit, the unit is subject to federal 40 CFR 257.5 through 257.30;
BOARD NOTE: The Illinois non-hazardous waste landfill regulations, 35 Ill. Adm. Code 810 through 814, do not allow the disposal of hazardous waste in a landfill regulated under those rules. The Board intends that subsections (g)(3)(D) and (g)(3)(E) of this Section impose a federal requirement on the hazardous waste generator. The Board specifically does not intend that these subsections authorize any disposal of conditionally-exempt small quantity generator waste in a landfill not specifically permitted to accept the particular hazardous waste.
F) The facility is one that fulfills the following conditions:
i) It beneficially uses or re-uses, or legitimately recycles or reclaims the small quantity generator’s waste; or
ii) It treats its waste prior to beneficial use or re-use or legitimate recycling or reclamation; or
G) For universal waste managed under 35 Ill. Adm. Code 733 or federal 40 CFR 273, the facility is a universal waste handler or destination facility subject to 35 Ill. Adm. Code 733 or federal 40 CFR 273.
h) Hazardous waste subject to the reduced requirements of this Section may be mixed with non-hazardous waste and remain subject to these reduced requirements even though the resultant mixture exceeds the quantity limitations identified in this Section, unless the mixture meets any of the characteristics of hazardous wastes identified in Subpart C of this Part.
i) If a small quantity generator mixes a solid waste with a hazardous waste that exceeds a quantity exclusion level of this Section, the mixture is subject to full regulation.
j) If a CESQG’s hazardous wastes are mixed with used oil, the mixture is subject to 35 Ill. Adm. Code 739. Any material produced from such a mixture by processing, blending, or other treatment is also so regulated.
(Source: Amended at 35 Ill. Reg. 17734, effective October 14, 2011)
Section 721.106 Requirements for Recyclable Materials
a) Recyclable materials:
1) Hazardous wastes that are recycled are subject to the requirements for generators, transporters, and storage facilities of subsections (b) and (c) of this Section, except for the materials listed in subsections (a)(2) and (a)(3) of this Section. Hazardous wastes that are recycled will be known as “recyclable materials.”
2) The following recyclable materials are not subject to the requirements of this Section but are regulated under Subparts C through H of 35 Ill. Adm. Code 726 and all applicable provisions in 35 Ill. Adm. Code 702, 703, and 728.
A) Recyclable materials used in a manner constituting disposal (Subpart C of 35 Ill. Adm. Code 726);
B) Hazardous wastes burned (as defined in 35 Ill. Adm. Code 726.200(a)) in boilers and industrial furnaces that are not regulated under Subpart O of 35 Ill. Adm. Code 724 or Subpart O of this Part (Subpart H of 35 Ill. Adm. Code 726);
C) Recyclable materials from which precious metals are reclaimed (Subpart F of 35 Ill. Adm. Code 726); and
D) Spent lead-acid batteries that are being reclaimed (Subpart G of 35 Ill. Adm. Code 726).
3) The following recyclable materials are not subject to regulation under 35 Ill. Adm. Code 722 through 728, or 702 and 703 and are not subject to the notification requirements of section 3010 of the Resource Conservation and Recovery Act:
A) Industrial ethyl alcohol that is reclaimed except that, unless provided otherwise in an international agreement as specified in 35 Ill. Adm. Code 722.158, the following requirements continue to apply:
i) A person initiating a shipment for reclamation in a foreign country and any intermediary arranging for the shipment must comply with the requirements applicable to a primary exporter in 35 Ill. Adm. Code 722.153; 722.156(a)(1) through (a)(4), (a)(6), and (b); and 722.157; must export such materials only upon consent of the receiving country and in conformance with the USEPA Acknowledgment of Consent, as defined in Subpart E of 35 Ill. Adm. Code 722; and must provide a copy of the USEPA Acknowledgment of Consent to the shipment to the transporter transporting the shipment for export; and
ii) Transporters transporting a shipment for export must not accept a shipment if the transporter knows that the shipment does not conform to the USEPA Acknowledgement of Consent, must ensure that a copy of the USEPA Acknowledgement of Consent accompanies the shipment, and must ensure that it is delivered to the facility designated by the person initiating the shipment;
B) Scrap metal that is not excluded under Section 721.104(a)(13);
C) Fuels produced from the refining of oil-bearing hazardous wastes along with normal process streams at a petroleum refining facility if such wastes result from normal petroleum refining, production, and transportation practices (this exemption does not apply to fuels produced from oil recovered from oil-bearing hazardous waste where such recovered oil is already excluded under Section 721.104(a)(12));
D) Petroleum refining wastes.
i) Hazardous waste fuel produced from oil-bearing hazardous wastes from petroleum refining, production, or transportation practices or produced from oil reclaimed from such hazardous wastes, where such hazardous wastes are reintroduced into a process that does not use distillation or does not produce products from crude oil, so long as the resulting fuel meets the used oil specification under 35 Ill. Adm. Code 739.111 and so long as no other hazardous wastes are used to produce the hazardous waste fuel;
ii) Hazardous waste fuel produced from oil-bearing hazardous waste from petroleum refining production, and transportation practices, where such hazardous wastes are reintroduced into a refining process after a point at which contaminants are removed, so long as the fuel meets the used oil fuel specification under 35 Ill. Adm. Code 739.111; and
iii) Oil reclaimed from oil-bearing hazardous wastes from petroleum refining, production, and transportation practices, which reclaimed oil is burned as a fuel without reintroduction to a refining process, so long as the reclaimed oil meets the used oil fuel specification under 35 Ill. Adm. Code 739.111.
4) Used oil that is recycled and is also a hazardous waste solely because it exhibits a hazardous characteristic is not subject to the requirements of 35 Ill. Adm. Code 720 through 728, but it is regulated under 35 Ill. Adm. Code 739. Used oil that is recycled includes any used oil that is reused for any purpose following its original use (including the purpose for which the oil was originally used). Such term includes, but is not limited to, oil that is re-refined, reclaimed, burned for energy recovery, or reprocessed.
5) Hazardous waste that is exported to or imported from designated member countries of the Organization for Economic Cooperation and Development (OECD), as defined in Section 722.158(a)(1), for the purpose of recovery is subject to the requirements of Subpart H of 35 Ill. Adm. Code 722 if it is subject to either the hazardous waste manifesting requirements of 35 Ill. Adm. Code 722 or the universal waste management standards of 35 Ill. Adm. Code 733.
b) Generators and transporters of recyclable materials are subject to the applicable requirements of 35 Ill. Adm. Code 722 and 723 and the notification requirements under section 3010 of the Resource Conservation and Recovery Act, except as provided in subsection (a) of this Section.
c) Storage and recycling.
1) Owners or operators of facilities that store recyclable materials before they are recycled are regulated under all applicable provisions of Subparts A through L, AA, BB, and CC of 35 Ill. Adm. Code 724 and 725 and 35 Ill. Adm. Code 702, 703, 705, 726, 727, and 728; and the notification requirement under section 3010 of the Resource Conservation and Recovery Act, except as provided in subsection (a) of this Section. (The recycling process itself is exempt from regulation, except as provided in subsection (d) of this Section.)
2) Owners or operators of facilities that recycle recyclable materials without storing them before they are recycled are subject to the following requirements, except as provided in subsection (a) of this Section, the following requirements continue to apply:
A) Notification requirements under section 3010 of the Resource Conservation and Recovery Act,
B) 35 Ill. Adm. Code 725.171 and 725.172 (dealing with the use of the manifest and manifest discrepancies), and
C) Subsection (d) of this Section.
d) Owners or operators of facilities required to have a RCRA permit pursuant to 35 Ill. Adm. Code 703 with hazardous waste management units that recycle hazardous wastes are subject to Subparts AA and BB of 35 Ill. Adm. Code 724 or 725 or 35 Ill. Adm. Code 267.
(Source: Amended at 35 Ill. Reg. 17734, effective October 14, 2011)
Section 721.107 Residues of Hazardous Waste in Empty Containers
a) Applicability of rules.
1) Any hazardous waste remaining in either an empty container or an inner liner removed from an empty container, as defined in subsection (b), is not subject to regulation under 35 Ill. Adm. Code 702, 703, or 721 through 728, or to the notification requirements of Section 3010 of the Resource Conservation and Recovery Act.
2) Any hazardous waste in either a container that is not empty or an inner liner that is removed from a container that is not empty, as defined in subsection (b), is subject to regulations under 35 Ill. Adm. Code 702, 703, and 721 through 728 and to the notification requirements of Section 3010 of the Resource Conservation and Recovery Act.
b) Definition of “empty”:
1) A container or an inner liner removed from a container that has held any hazardous waste, except a waste that is a compressed gas or that is identified as an acute hazardous waste listed in Section 721.131 or 721.133(e), is empty if the conditions of subsections (b)(1)(A) and (b)(1)(B) exist, subject to the limitations of subsection (b)(1)(C):
A) All wastes have been removed that can be removed using the practices commonly employed to remove materials from that type of container, e.g., pouring, pumping, and aspirating, and
B) No more than 2.5 centimeters (one inch) of residue remain on the bottom of the container or inner liner, or
C) Weight Limits
i) No more than three percent by weight of the total capacity of the container remains in the container or inner liner if the container is less than or equal to 119 gallons (450 liters) in size; or
ii) No more than 0.3 percent by weight of the total capacity of the container remains in the container or inner liner if the container is greater than 119 gallons (450 liters) in size.
2) A container that has held a hazardous waste that is a compressed gas is empty when the pressure in the container approaches ambient atmospheric pressure.
3) A container or an inner liner removed from a container that has held an acute hazardous waste listed in Section 721.131 or 721.133(e) is empty if any of the following occurs:
A) The container or inner liner has been triple rinsed using a solvent capable of removing the commercial chemical product or manufacturing chemical intermediate;
B) The container or inner liner has been cleaned by another method that has been shown in the scientific literature, or by tests conducted by the generator, to achieve equivalent removal; or
C) In the case of a container, the inner liner that prevented contact of the commercial chemical product or manufacturing chemical intermediate with the container has been removed.
c) A container that held hazardous waste pharmaceuticals is determined empty under 35 Ill. Adm. Code 726.607, in lieu of under this Section, except as provided by 35 Ill. Adm. Code 726.607(c) and (d).
(Source: Amended at 44 Ill. Reg. 15142, effective September 3, 2020)
Section 721.108 PCB Wastes Regulated under TSCA
Polychlorinatedbiphenyl-(PCB-)containing dielectric fluid and electric equipment containing such fluid are exempt from regulation under 35 Ill. Adm. Code 702, 703, and 721 through 728, and from the notification requirements of Section 3010 of the Resource Conservation and Recovery Act if the following conditions are fulfilled with regard to the fluid:
a) The fluid is authorized for use and regulated pursuant to federal 40 CFR 761; and
b) The fluid is hazardous only because it fails the test for toxicity characteristic (hazardous waste codes D018 through D043 only).
(Source: Amended at 31 Ill. Reg. 791, effective December 20, 2006)
Section 721.109 Requirements for Universal Waste
The wastes listed in this Section are exempt from regulation under 35 Ill. Adm. Code 702, 703, 722 through 726, and 728, except as specified in 35 Ill. Adm. Code 733, and are therefore not fully regulated as hazardous waste. The following wastes are subject to regulation under 35 Ill. Adm. Code 733:
a) Batteries, as described in 35 Ill. Adm. Code 733.102;
b) Pesticides, as described in 35 Ill. Adm. Code 733.103;
c) Mercury-containing equipment, as described in 35 Ill. Adm. Code 733.104;
d) Lamps, as described in 35 Ill. Adm. Code 733.105; and
e) Aerosol cans, as described in 35 Ill. Adm. Code 733.106.
(Source: Amended at 44 Ill. Reg. 15142, effective September 3, 2020)
Section 721.122 Characteristic of Corrosivity
a) A solid waste exhibits the characteristic of corrosivity if a representative sample of the waste has either of the following properties:
1) It is aqueous and has a pH less than or equal to 2 or greater than or equal to 12.5, as determined by a pH meter using Method 9040C (pH Electrometric Measurement) in “Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
2) It is a liquid and corrodes steel (SAE 1020) at a rate greater than 6.35 mm (0.250 inch) per year at a test temperature of 55 °C (130 °F), as determined by Method 1110A (Corrosivity Toward Steel) in “Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods”, USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).
BOARD NOTE: The corrosivity characteristic determination currently does not apply to non-liquid wastes, as discussed by USEPA at 45 Fed. Reg. 33109, May 19, 1980 and at 55 Fed. Reg. 22549, June 1, 1990.
b) A solid waste that exhibits the characteristic of corrosivity has the USEPA hazardous waste number of D002.
(Source: Amended at 44 Ill. Reg. 15142, effective September 3, 2020)
Section 721.123 Characteristic of Reactivity
a) A solid waste exhibits the characteristic of reactivity if a representative sample of the waste has any of the following properties:
1) It is normally unstable and readily undergoes violent change without detonating.
2) It reacts violently with water.
3) It forms potentially explosive mixtures with water.
4) When mixed with water, it generates toxic gases, vapors, or fumes in a quantity sufficient to present a danger to human health or the environment.
5) It is a cyanide or sulfide bearing waste which, when exposed to pH conditions between 2 and 12.5 can generate toxic gases, vapors, or fumes in a quantity sufficient to present a danger to human health or the environment.
6) It is capable of detonation or explosive reaction if it is subjected to a strong initiating source or if heated under confinement.
7) It is readily capable of detonation or explosive decomposition or reaction at standard temperature and pressure.
8) It is a forbidden explosive, as defined in federal 49 CFR 173.54 (Forbidden Explosives) or a Division 1.1, 1.2, or 1.3 explosive, as defined in 49 CFR 173.50 (Class 1—Definitions), each incorporated by reference in 35 Ill. Adm. Code 720.111(b).
BOARD NOTE: Corresponding 40 CFR 261.23 cites to 49 CFR 173.53 (Provisions for Using Old Classifications of Explosives). That citation aids bridging obsolete USDOT rules to the current version. The Board has not included citation to 49 CFR 173.53 because it imposes no substantive requirements.
b) A solid waste that exhibits the characteristic of reactivity has the USEPA hazardous waste number of D003.
(Source: Amended at 35 Ill. Reg. 17734, effective October 14, 2011)
Section 721.124 Toxicity Characteristic
a) A solid waste (except manufactured gas plant waste) exhibits the characteristic of toxicity if, using Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number EPA-530/SW-846, as incorporated by reference in 35 Ill. Adm. Code 720.111(a), the extract from a representative sample of the waste contains any of the contaminants listed in the table in subsection (b) of this Section at a concentration equal to or greater than the respective value given in that table. Where the waste contains less than 0.5 percent filterable solids, the waste itself, after filtering using the methodology outlined in Method 1311, is considered to be the extract for the purpose of this Section.
BOARD NOTE: The reference to the “EP toxicity test” in 35 Ill. Adm. Code 808.410(b)(4) is to be understood as referencing the test required by this Section.
b) A solid waste that exhibits the characteristic of toxicity has the USEPA hazardous waste number specified in the following table that corresponds to the toxic contaminant causing it to be hazardous.
USEPA Hazardous Waste No. | Contaminant | CAS Number | Note | Regulatory Level (mg/ℓ)
|
D004 | Arsenic | 7440-38-2 | 5.0
|
|
D005 | Barium | 7440-39-3 | 100.0
|
|
D018 | Benzene | 71-43-2 | 0.5
|
|
D006 | Cadmium | 7440-43-9 | 1.0
|
|
D019 | Carbon tetrachloride | 56-23-5 | 0.5
|
|
D020 | Chlordane | 57-74-9 | 0.03
|
|
D021 | Chlorobenzene | 108-90-7 | 100.0
|
|
D022 | Chloroform | 67-66-3 | 6.0
|
|
D007 | Chromium | 7440-47-3 | 5.0
|
|
D023 | o-Cresol | 95-48-7 | 2
|
200.0
|
D024 | m-Cresol | 108-39-4 | 2
|
200.0
|
D025 | p-Cresol | 106-44-5 | 2
|
200.0
|
D026 | Cresol | 2
|
200.0
|
|
D016 | 2,4-D | 94-75-7 | 10.0
|
|
D027 | 1,4-Dichlorobenzene | 106-46-7 | 7.5
|
|
D028 | 1,2-Dichloroethane | 107-06-2 | 0.5
|
|
D029 | 1,1-Dichloroethylene | 75-35-4 | 0.7
|
|
D030 | 2,4-Dinitrotoluene | 121-14-2 | 1
|
0.13
|
D012 | Endrin | 72-20-8 | 0.02
|
|
D031 | Heptachlor (and its epoxide) | 76-44-8 | 0.008
|
|
D032 | Hexachlorobenzene | 118-74-1 | 1
|
0.13
|
D033 | Hexachlorobutadiene | 87-68-3 | 0.5
|
|
D034 | Hexachloroethane | 67-72-1 | 3.0
|
|
D008 | Lead | 7439-92-1 | 5.0
|
|
D013 | Lindane | 58-89-9 | 0.4
|
|
D009 | Mercury | 7439-97-6 | 0.2
|
|
D014 | Methoxychlor | 72-43-5 | 10.0
|
|
D035 | Methyl ethyl ketone | 78-93-3 | 200.0
|
|
D036 | Nitrobenzene | 98-95-3 | 2.0
|
|
D037 | Pentachlorophenol | 87-86-5 | 100.0
|
|
D038 | Pyridine | 110-86-1 | 1
|
5.0
|
D010 | Selenium | 7782-49-2 | 1.0
|
|
D011 | Silver | 7440-22-4 | 5.0
|
|
D039 | Tetrachloroethylene | 127-18-4 | 0.7
|
|
D015 | Toxaphene | 8001-35-2 | 0.5
|
|
D040 | Trichloroethylene | 79-01-6 | 0.5
|
|
D041 | 2,4,5-Trichlorophenol | 95-95-4 | 400.0
|
|
D042 | 2,4,6-Trichlorophenol | 88-06-2 | 2.0
|
|
D017 | 2,4,5-TP (Silvex) | 93-72-1 | 1.0
|
|
D043 | Vinyl chloride | 75-01-4 | 0.2
|
USEPA Hazardous Waste No. | Industry and Hazardous Waste | Hazard Code |
F001 | The following spent halogenated solvents used in degreasing: tetrachloroethylene, trichloroethylene, methylene chloride, 1,1,1-trichloroethane, carbon tetrachloride, and chlorinated fluorocarbons; all spent solvent mixtures and blends used in degreasing containing, before use, a total of ten percent or more (by volume) of one or more of the above halogenated solvents or those solvents listed in F002, F004, or F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. | (T) |
F002 | The following spent halogenated solvents: tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, chlorobenzene, 1,1,2-trichloro-1,2,2-trifluoroethane, orthodichlorobenzene, trichlorofluoromethane, and 1,1,2-trichloroethane; all spent solvent mixtures and blends containing, before use, a total of ten percent or more (by volume) of one or more of the above halogenated solvents or those solvents listed in F001, F004, or F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. | (T) |
F003 | The following spent non-halogenated solvents: xylene, acetone, ethyl acetate, ethyl benzene, ethyl ether, methyl isobutyl ketone, n-butyl alcohol, cyclohexanone, and methanol; all spent solvent mixtures and blends containing, before use, only the above spent non-halogenated solvents; and all spent solvent mixtures and blends containing, before use, one or more of the above non-halogenated solvents and a total of ten percent or more (by volume) of one or more of those solvents listed in F001, F002, F004, or F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. | (I) |
F004 | The following spent non-halogenated solvents: cresols and cresylic acid and nitrobenzene; all spent solvent mixtures and blends containing, before use, a total of ten percent or more (by volume) of one or more of the above non-halogenated solvents or those solvents listed in F001, F002, or F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. | (T) |
F005 | The following spent non-halogenated solvents: toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, benzene, 2-ethoxyethanol, and 2-nitropropane; all spent solvent mixtures and blends, containing, before use, a total of ten percent or more (by volume) of one or more of the above non-halogenated solvents or those solvents listed in F001, F002, or F004; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. | (I, T) |
F006 | Wastewater treatment sludges from electroplating operations except from the following processes: (1) sulfuric acid anodizing of aluminum; (2) tin plating on carbon steel; (3) zinc plating (segregated basis) on carbon steel; (4) aluminum or zinc-aluminum plating on carbon steel; (5) cleaning/stripping associated with tin, zinc, and aluminum plating on carbon steel; and (6) chemical etching and milling of aluminum. | (T) |
F007 | Spent cyanide plating bath solutions from electroplating operations. | (R, T) |
F008 | Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process. | (R, T) |
F009 | Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process. | (R, T) |
F010 | Quenching bath residues from oil baths from metal heat-treating operations where cyanides are used in the process. | (R, T) |
F011 | Spent cyanide solutions from salt bath pot cleaning from metal heat-treating operations. | (R, T) |
F012 | Quenching wastewater treatment sludges from metal heat-treating operations where cyanides are used in the process. | (T) |
F019 | Wastewater treatment sludges from the chemical conversion coating of aluminum except from zirconium phosphating in aluminum can washing when such phosphating is an exclusive conversion coating process.
Wastewater treatment sludge from the manufacturing of motor vehicles using a zinc phosphating process will not be subject to this listing at the point of generation if the waste is not placed outside on the land prior to shipment to a landfill for disposal and it is disposed of in a regulated landfill that fulfills either of the following conditions: It is located in Illinois, and it is one of the following types of landfills: It is a landfill that is a hazardous waste management unit, as defined in 35 Ill. Adm. Code 720.110; It is a municipal solid waste landfill, as defined in 35 Ill. Adm. Code 810.103; or It is a putrescible or chemical waste landfill that is subject to the requirements of Subpart C of 35 Ill. Adm. Code 811. It is located outside Illinois, and it is one of the following types of landfills: It is a RCRA Subtitle D municipal solid waste or industrial solid waste landfill unit that is equipped with a single clay liner and which is permitted, licensed or otherwise authorized by the state; or It is a landfill unit that is subject to or which otherwise meets the landfill requirements in 40 CFR 258.40, 264.301 or 265.301. For the purposes of this hazardous waste listing, “motor vehicle manufacturing” is defined in subsection (b)(4)(A) of this Section, and subsection (b)(4)(B) of this Section describes the recordkeeping requirements for motor vehicle manufacturing facilities. |
(T) |
F020 | 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 tri- or tetrachlorophenol or of intermediates used to produce their pesticide derivatives. (This listing does not include wastes from the production of hexachlorophene from highly purified 2,4,5-trichlorophenol.) | (H) |
F021 | 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 pentachlorophenol or of intermediates used to produce its derivatives. | (H) |
F022 | Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the manufacturing use (as a reactant, chemical intermediate or component in a formulating process) of tetra-, penta-, or hexachlorobenzenes under alkaline conditions. | (H) |
F023 | 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 tri- and tetrachlorophenols. (This listing does not include wastes from equipment used only for the production or use of hexachlorophene from highly purified 2,4,5-trichlorophenol.) | (H) |
F024 | Process wastes, including but not limited to, distillation residues, heavy ends, tars, and reactor cleanout 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 this Section or in Section 721.132.) | (T) |
F025 | Condensed light ends, 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. | (T) |
F026 | Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials on equipment previously used for the manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tetra-, penta-, or hexachlorobenzene under alkaline conditions. | (H) |
F027 | Discarded unused formulations containing tri-, tetra- or pentachlorophenol or discarded unused formulations containing compounds derived from these chlorophenols. (This listing does not include formulations containing hexachlorophene synthesized from prepurified 2,4,5-trichlorophenol as the sole component.) | (H) |
F028 | Residues resulting from the incineration or thermal treatment of soil contaminated with hazardous waste numbers F020, F021, F022, F023, F026, and F027. | (T) |
F032 | Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that currently use or have previously used chlorophenolic formulations (except potentially cross-contaminated wastes that have had the F032 waste code deleted in accordance with Section 721.135 and 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 pentachlorophenol. | (T) |
F034 | Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use creosote formulations. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote or pentachlorophenol. | (T) |
F035 | 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 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. | (T) |
F037 | Petroleum refinery primary oil/water/solids separation sludge—any sludge generated from the gravitational separation of oil/water/solids during the storage or treatment of process wastewaters and oily cooling wastewaters from petroleum refineries. Such sludges include, but are not limited to, those generated in: oil/water/solids separators; tanks and impoundments; ditches and other conveyances; sumps; and stormwater units receiving dry weather flow. Sludge generated in stormwater units that do not receive dry weather flow, sludge generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludge generated in aggressive biological treatment units as defined in subsection (b)(2) of this Section (including sludge 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. This listing does include residuals generated from processing or recycling oil-bearing hazardous secondary materials excluded under Section 721.104(a)(12)(A) if those residuals are to be disposed of. | (T) |
F038 | Petroleum refinery secondary (emulsified) oil/water/solids separation sludge—any 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 the following types of units: induced air floatation (IAF) units, tanks and impoundments, and all sludges generated in dissolved air flotation (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 subsection (b)(2) of this Section (including sludges and floats generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units), F037, K048, and K051 wastes are not included in this listing. | (T) |
F039 | Multi-source leachate resulting from the disposal of more than one restricted waste classified as hazardous under this Subpart D. For purposes of this hazardous waste listing, “leachate” means liquids that have percolated through land-disposed wastes. (This multi-source leachate listing does not apply to leachate resulting from the disposal of more than one of the following USEPA hazardous wastes where the disposal of no other hazardous waste is involved: F020, F021, F022, F026, F027, and F028. Leachate from disposal of any combination of these hazardous wastes is considered single-source leachate, and that leachate retains the USEPA hazardous waste numbers of the wastes from which the leachate derived, and the leachate must meet the treatment standards for the underlying waste codes.)
BOARD NOTE: Derived from the listing for F039 at 40 CFR 261.31(a) (2010) and the discussion at 55 Fed. Reg. 22520, 22619-22623 (June 1, 1990). |
(T) |
USEPA Hazardous Waste No. | Industry and Hazardous Waste | Hazard Code |
K001 | Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote or pentachlorophenol. | (T) |
K002 | Wastewater treatment sludge from the production of chrome yellow and orange pigments. | (T) |
K003 | Wastewater treatment sludge from the production of molybdate orange pigments. | (T) |
K004 | Wastewater treatment sludge from the production of zinc yellow pigments. | (T) |
K005 | Wastewater treatment sludge from the production of chrome green pigments. | (T) |
K006 | Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous and hydrated). | (T) |
K007 | Wastewater treatment sludge from the production of iron blue pigments. | (T) |
K008 | Oven residue from the production of chrome oxide green pigments. | (T) |
K009 | Distillation bottoms from the production of acetaldehyde from ethylene. | (T) |
K010 | Distillation side cuts from the production of acetaldehyde from ethylene. | (T) |
K011 | Bottom stream from the wastewater stripper in the production of acrylonitrile. | (R, T) |
K013 | Bottom stream from the acetonitrile column in the production of acrylonitrile. | (T) |
K014 | Bottoms from the acetonitrile purification column in the production of acrylonitrile. | (T) |
K015 | Still bottoms from the distillation of benzyl chloride. | (T) |
K016 | Heavy ends or distillation residues from the production of carbon tetrachloride. | (T) |
K017 | Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin. | (T) |
K018 | Heavy ends from the fractionation column in ethyl chloride production. | (T) |
K019 | Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production. | (T) |
K020 | Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production. | (T) |
K021 | Aqueous spent antimony catalyst waste from fluoromethanes production. | (T) |
K022 | Distillation bottom tars from the production of phenol/acetone from cumene. | (T) |
K023 | Distillation light ends from the production of phthalic anhydride from naphthalene. | (T) |
K024 | Distillation bottoms from the production of phthalic anhydride from naphthalene. | (T) |
K093 | Distillation light ends from the production of phthalic anhydride from ortho-xylene. | (T) |
K094 | Distillation bottoms from the production of phthalic anhydride from ortho-xylene. | (T) |
K025 | Distillation bottoms from the production of nitrobenzene by the nitration of benzene. | (T) |
K026 | Stripping still tails from the production of methyl ethyl pyridines. | (T) |
K027 | Centrifuge and distillation residues from toluene diisocyanate production. | (R, T) |
K028 | Spent catalyst from the hydrochlorinator reactor in the production of 1,1,1-trichloroethane. | (T) |
K029 | Waste from the product stream stripper in the production of 1,1,1-trichloroethane. | (T) |
K095 | Distillation bottoms from the production of 1,1,1-trichloroethane. | (T) |
K096 | Heavy ends from the heavy ends column from the production of 1,1,1-trichloroethane. | (T) |
K030 | Column bottoms or heavy ends from the combined production of trichloroethylene and perchloroethylene. | (T) |
K083 | Distillation bottoms from aniline production. | (T) |
K103 | Process residues from aniline extraction from the production of aniline. | (T) |
K104 | Combined wastewater streams generated from nitrobenzene/aniline production. | (T) |
K085 | Distillation or fractionation column bottoms from the production of chlorobenzenes. | (T) |
K105 | Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes. | (T) |
K107 | Column bottoms from product separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. | (C, T) |
K108 | Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. | (I, T) |
K109 | Spent filter cartridges from the product purification from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. | (T) |
K110 | Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. | (T) |
K111 | Product wastewaters from the production of dinitrotoluene via nitration of toluene. | (C, T) |
K112 | Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene. | (T) |
K113 | Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. | (T) |
K114 | Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. | (T) |
K115 | Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. | (T) |
K116 | Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine. | (T) |
K117 | Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene. | (T) |
K118 | Spent adsorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene. | (T) |
K136 | Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene. | (T) |
K156 | Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.) | (T) |
K157 | Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.) | (T) |
K158 | Baghouse dusts and filter/separation solids from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.) | (T) |
K159 | Organics from the treatment of thiocarbamate wastes. | (T) |
K161 | Purification solids (including filtration, evaporation, and centrifugation solids), bag house dust, and floor sweepings from the production of dithiocarbamate acids and their salts. (This listing does not include K125 or K126.) | (R, T) |
K174 | Wastewater treatment sludges from the production of ethylene dichloride or vinyl chloride monomer (including sludges that result from commingled ethylene dichloride or vinyl chloride monomer wastewater and other wastewater), unless the sludges meet the following conditions: (1) the sludges are disposed of in a RCRA Subtitle C (42 USC 6921-6939e) or non-hazardous landfill licensed or permitted by a state or the federal government; (2) the sludges are not otherwise placed on the land prior to final disposal; and (3) the generator maintains documentation demonstrating that the waste was either disposed of in an on-site landfill or consigned to a transporter or disposal facility that provided a written commitment to dispose of the waste in an off-site landfill. Upon a showing by the government that a respondent in any enforcement action brought to enforce the requirements of Subtitle C of this Part managed wastewater treatment sludges from the production of vinyl chloride monomer or ethylene dichloride, the respondent must demonstrate that it meets the conditions of the exclusion that are set forth above. In doing so, the respondent must provide appropriate documentation that the terms of the exclusion were met (e.g., contracts between the generator and the landfill owner or operator, invoices documenting delivery of waste to landfill, etc.). | (T) |
K175 | Wastewater treatment sludges from the production of vinyl chloride monomer using mercuric chloride catalyst in an acetylene-based process. | (T) |
K071 | Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used. | (T) |
K073 | Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production. | (T) |
K106 | Wastewater treatment sludge from the mercury cell process in chlorine production. | (T) |
K176 | Baghouse filters from the production of antimony oxide, including filters from the production of intermediates (e.g., antimony metal or crude antimony oxide). | (E) |
K177 | Slag from the production of antimony oxide that is speculatively accumulated or disposed of, including slag from the production of intermediates (e.g., antimony metal or crude antimony oxide). | (T) |
K178 | Residues from manufacturing and manufacturing-site storage of ferric chloride from acids formed during the production of titanium dioxide using the chloride-ilmenite process. | (T) |
K181 | Nonwastewaters from the production of dyes or pigments (including nonwastewaters commingled at the point of generation with nonwastewaters from other processes) that, at the point of generation, contain mass loadings of any of the constituents identified in subsection (c) of this Section that are equal to or greater than the corresponding subsection (c) levels, as determined on a calendar year basis. These wastes will not be hazardous if the nonwastewaters are managed in one of the following ways:
1) They are disposed of in a municipal solid waste landfill unit that is subject to the design criteria in 35 Ill. Adm. Code 811.303 through 811.309 and 811.315 through 811.317 and Subpart E of 35 Ill. Adm. Code 811 or 35 Ill. Adm. Code 814.302 and 814.402; 2) They are disposed of in a hazardous waste landfill unit that is subject to either 35 Ill. Adm. Code 724.401 or 725.401; 3) They are disposed of in other municipal solid waste landfill units that meet the design criteria in 35 Ill. Adm. Code 811.303 through 811.309 and 811.315 through 811.317 and Subpart E of 35 Ill. Adm. Code 811 or 35 Ill. Adm. Code 814.302 and 814.402, 35 Ill. Adm. Code 724.401, or 35 Ill. Adm. Code 725.401; or 4) They are treated in a combustion unit that is permitted under 415 ILCS 5/39(d), or an onsite combustion unit that is permitted under 415 ILCS 5/39.5. For the purposes of this listing, dyes or pigments production is defined in subsection (b)(1) of this Section. Subsection (d) of this Section describes the process for demonstrating that a facility’s nonwastewaters are not K181 waste. This listing does not apply to wastes that are otherwise identified as hazardous under Sections 721.121 through 721.124 and 721.131 through 721.133 at the point of generation. Also, the listing does not apply to wastes generated before any annual mass loading limit is met, as set forth in subsection (c) of this Section. |
(T) |
K031 | By-product salts generated in the production of MSMA and cacodylic acid. | (T) |
K032 | Wastewater treatment sludge from the production of chlordane. | (T) |
K033 | Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane. | (T) |
K034 | Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane. | (T) |
K097 | Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane. | (T) |
K035 | Wastewater treatment sludges generated in the production of creosote. | (T) |
K036 | Still bottoms from toluene reclamation distillation in the production of disulfoton. | (T) |
K037 | Wastewater treatment sludges from the production of disulfoton. | (T) |
K038 | Wastewater from the washing and stripping of phorate production. | (T) |
K039 | Filter cake from the filtration of diethylphosphorodithioic acid in the production of phorate. | (T) |
K040 | Wastewater treatment sludge from the production of phorate. | (T) |
K041 | Wastewater treatment sludge from the production of toxaphene. | (T) |
K098 | Untreated process wastewater from the production of toxaphene. | (T) |
K042 | Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5-T. | (T) |
K043 | 2,6-Dichlorophenol waste from the production of 2,4-D. | (T) |
K099 | Untreated wastewater from the production of 2,4-D. | (T) |
K123 | Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salts. | (T) |
K124 | Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts. | (C, T) |
K125 | Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts. | (T) |
K126 | Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts. | (T) |
K131 | Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide. | (C, T) |
K132 | Spent absorbent and wastewater separator solids from the production of methyl bromide. | (T) |
K044 | Wastewater treatment sludges from the manufacturing and processing of explosives. | (R) |
K045 | Spent carbon from the treatment of wastewater containing explosives. | (R) |
K046 | Wastewater treatment sludges from the manufacturing, formulation and loading of lead-based initiating compounds. | (T) |
K047 | Pink/red water from TNT operations. | (R) |
K048 | Dissolved air flotation (DAF) float from the petroleum refining industry. | (T) |
K049 | Slop oil emulsion solids from the petroleum refining industry. | (T) |
K050 | Heat exchanger bundle cleaning sludge from the petroleum refining industry. | (T) |
K051 | API separator sludge from the petroleum refining industry. | (T) |
K052 | Tank bottoms (leaded) from the petroleum refining industry. | (T) |
K169 | Crude oil storage tank sediment from petroleum refining operations. | (T) |
K170 | Clarified slurry oil tank sediment or in-line filter/separation solids from petroleum refining operations. | (T) |
K171 | Spent hydrotreating catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media). | (I, T) |
K172 | Spent hydrorefining catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media). | (I, T) |
K061 | Emission control dust/sludge from the primary production of steel in electric furnaces. | (T) |
K062 | Spent pickle liquor generated by steel finishing operations of facilities within the iron and steel industry (SIC Codes 331 and 332) (as defined in 35 Ill. Adm. Code 720.110). | (C, T) |
K088 | Spent potliners from primary aluminum reduction. | (T) |
K069 | Emission control dust/sludge from secondary lead smelting. | (T) |
K100 | Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting. | (T) |
K084 | Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds. | (T) |
K101 | Distillation tar residues from the distillation of aniline-based compounds in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds. | (T) |
K102 | Residue from use of activated carbon for decolorization in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds. | (T) |
K086 | Solvent washes and sludges, caustic washes and sludges, or water washes and sludges from cleaning tubs and equipment used in the formulation of ink from pigments, dryers, soaps and stabilizers containing chromium and lead. | (T) |
K060 | Ammonia still lime sludge from coking operations. | (T) |
K087 | Decanter tank tar sludge from coking operations. | (T) |
K141 | Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the production of coke from coal or the recovery of coke by-products produced from coal. This listing does not include K087 (decanter tank tar sludges from coking operations). | (T) |
K142 | Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal. | (T) |
K143 | Process residues from the recovery of light oil, including, but not limited to, those generated in stills, decanters, and wash oil recovery units from the recovery of coke by-products produced from coal. | (T) |
K144 | Wastewater sump residues from light oil refining, including, but not limited to, intercepting or contamination sump sludges from the recovery of coke by-products produced from coal. | (T) |
K145 | Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal. | (T) |
K147 | Tar storage tank residues from coal tar refining. | (T) |
K148 | Residues from coal tar distillation, including, but not limited to, still bottoms. | (T) |
K149 | Distillation bottoms from the production of a - (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. (This waste does not include still bottoms from the distillation of benzyl chloride.) | (T) |
K150 | Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydrochloric acid recovery processes associated with the production of a - (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. | (T) |
K151 | Wastewater treatment sludges, excluding neutralization and biological sludges, generated during the treatment of wastewaters from the production of a - (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. | (T) |
Constituent | Chemical Abstracts No. | Mass Levels (kg/yr) |
Aniline | 62-53-3 | 9,300 |
o-Anisidine | 90-04-0 | 110 |
4-Chloroaniline | 106-47-8 | 4,800 |
p-Cresidine | 120-71-8 | 660 |
2,4-Dimethylaniline | 95-68-1 | 100 |
1,2-Phenylenediamine | 95-54-5 | 710 |
1,3-Phenylenediamine | 108-45-2 | 1,200 |
Section 721.133 Discarded Commercial Chemical Products, Off-Specification Species, Container Residues, and Spill Residues Thereof
The following materials or items are hazardous wastes if and when they are discarded or intended to be discarded, as described in Section 721.102(a)(2)(A); when they are mixed with waste oil or used oil or other material and applied to the land for dust suppression or road treatment; when they are otherwise applied to the land in lieu of their original intended use or when they are contained in products that are applied to land in lieu of their original intended use; or when, in lieu of their original intended use, they are produced for use as (or as a component of) a fuel, distributed for use as a fuel, or burned as a fuel.
a) Any commercial chemical product or manufacturing chemical intermediate having the generic name listed in subsection (e) or (f).
b) Any off-specification commercial chemical product or manufacturing chemical intermediate that, if it met specifications, would have the generic name listed in subsection (e) or (f).
c) Any residue remaining in a container or inner liner removed from a container that has held any commercial chemical product or manufacturing chemical intermediate having the generic name listed in subsection (e) or (f), unless the container is empty, as defined in Section 721.107(b)(3) or 35 Ill. Adm. Code 726.607.
BOARD NOTE: Unless the residue is being beneficially used or reused; legitimately recycled or reclaimed; or accumulated, stored, transported, or treated prior to such use, reuse, recycling, or reclamation, the Board considers the residue to be intended for discard, and thus a hazardous waste. An example of a legitimate reuse of the residue would be if the residue remains in the container and the container is used to hold the same commercial chemical product or manufacturing chemical intermediate it previously held. An example of the discard of the residue would be if the drum is sent to a drum reconditioner that reconditions the drum but discards the residue.
d) Any residue or contaminated soil, water, or other debris resulting from the cleanup of a spill into or on any land or water of any commercial chemical product or manufacturing chemical intermediate having the generic name listed in subsection (e) or (f) or any residue or contaminated soil, water, or other debris resulting from the cleanup of a spill into or on any land or water of any off-specification chemical product or manufacturing chemical intermediate that, if it met specifications, would have the generic name listed in subsection (e) or (f).
BOARD NOTE: The phrase “commercial chemical product or manufacturing chemical intermediate having the generic name” refers to a chemical substance that is manufactured or formulated for commercial or manufacturing use that consists of the commercially pure grade of the chemical, any technical grades of the chemical that are produced or marketed, and all formulations in which the chemical is the sole active ingredient. It does not refer to a material, such as a manufacturing process waste, that contains any of the substances listed in subsection (e) or (f). If a manufacturing process waste is deemed to be a hazardous waste because it contains a substance listed in subsection (e) or (f), such waste will be listed in either Sections 721.131 or 721.132 or will be identified as a hazardous waste by the characteristics set forth in Subpart C.
e) The commercial chemical products, manufacturing chemical intermediates, or off-specification commercial chemical products or manufacturing chemical intermediates referred to in subsections (a) through (d) are identified as acute hazardous waste (H). These wastes and their corresponding USEPA hazardous waste numbers are the following:
BOARD NOTE: For the convenience of the regulated community, the primary hazardous properties of these materials have been indicated by the letters T (Toxicity), and R (Reactivity). The absence of a letter indicates that the compound is only listed for acute toxicity. Wastes are first listed in alphabetical order by substance and then listed again in numerical order by USEPA hazardous waste number.
Alphabetical Listing
USEPA Hazardous Waste No. | Chemical Abstracts No. (CAS No.) | Substance | Hazard Code |
P023 | 107-20-0 | Acetaldehyde, chloro- | |
P002 | 591-08-2 | Acetamide, N-(aminothioxomethyl) | |
P057 | 640-19-7 | Acetamide, 2-fluoro- | |
P058 | 62-74-8 | Acetic acid, fluoro-, sodium salt | |
P002 | 591-08-2 | 1-Acetyl-2-thiourea | |
P003 | 107-02-8 | Acrolein | |
P070 | 116-06-3 | Aldicarb | |
P203 | 1646-88-4 | Aldicarb sulfone | |
P004 | 309-00-2 | Aldrin | |
P005 | 107-18-6 | Allyl alcohol | |
P006 | 20859-73-8 | Aluminum phosphide | (R, T) |
P007 | 2763-96-4 | 5-(Aminomethyl)-3-isoxazolol | |
P008 | 504-24-5 | 4-Aminopyridine | |
P009 | 131-74-8 | Ammonium picrate | (R) |
P119 | 7803-55-6 | Ammonium vanadate | |
P099 | 506-61-6 | Argentate(1-), bis(cyano-C)-, potassium | |
P010 | 7778-39-4 | Arsenic acid H3AsO4 | |
P012 | 1327-53-3 | Arsenic oxide As2O3 | |
P011 | 1303-28-2 | Arsenic oxide As2O5 | |
P011 | 1303-28-2 | Arsenic pentoxide | |
P012 | 1327-53-3 | Arsenic trioxide | |
P038 | 692-42-2 | Arsine, diethyl- | |
P036 | 696-28-6 | Arsonous dichloride, phenyl- | |
P054 | 151-56-4 | Aziridine | |
P067 | 75-55-8 | Aziridine, 2-methyl | |
P013 | 542-62-1 | Barium cyanide | |
P024 | 106-47-8 | Benzenamine, 4-chloro- | |
P077 | 100-01-6 | Benzenamine, 4-nitro- | |
P028 | 100-44-7 | Benzene, (chloromethyl)- | |
P042 | 51-43-4 | 1,2-Benzenediol, 4-(1-hydroxy-2-(methylamino)ethyl)-, (R)- | |
P046 | 122-09-8 | Benzeneethanamine, a , a -dimethyl- | |
P014 | 108-98-5 | Benzenethiol | |
P127 | 1563-66-2 | 7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-, methylcarbamate | |
P188 | 57-64-7 | Benzoic acid, 2-hydroxy-, compound with (3aS-cis)-1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethylpyrrolo(2,3-b)indol-5-yl methylcarbamate ester (1:1) | |
P001 | 81-81-2* | 2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, and salts, when present at concentrations greater than 0.3 percent | |
P028 | 100-44-7 | Benzyl chloride | |
P015 | 7440-41-7 | Beryllium powder | |
P017 | 598-31-2 | Bromoacetone | |
P018 | 357-57-3 | Brucine | |
P045 | 39196-18-6 | 2-Butanone, 3,3-dimethyl-1-(methylthio)-, O-((methylamino)carbonyl) oxime | |
P021 | 592-01-8 | Calcium cyanide | |
P021 | 592-01-8 | Calcium cyanide Ca(CN)2 | |
P189 | 55285-14-8 | Carbamic acid, ((dibutylamino)-thio)methyl-, 2,3-dihydro-2,2-dimethyl-7-benzofuranyl ester | |
P191 | 644-64-4 | Carbamic acid, dimethyl-, 1-((dimethyl-amino)carbonyl)-5-methyl-1H-pyrazol-3-yl ester | |
P192 | 119-38-0 | Carbamic acid, dimethyl-, 3-methyl-1-(1-methylethyl)-1H-pyrazol-5-yl ester | |
P190 | 1129-41-5 | Carbamic acid, methyl-, 3-methylphenyl ester | |
P127 | 1563-66-2 | Carbofuran | |
P022 | 75-15-0 | Carbon disulfide | |
P095 | 75-44-5 | Carbonic dichloride | |
P189 | 55285-14-8 | Carbosulfan | |
P023 | 107-20-0 | Chloroacetaldehyde | |
P024 | 106-47-8 | p-Chloroaniline | |
P026 | 5344-82-1 | 1-(o-Chlorophenyl)thiourea | |
P027 | 542-76-7 | 3-Chloropropionitrile | |
P029 | 544-92-3 | Copper cyanide | |
P029 | 544-92-3 | Copper cyanide CuCN | |
P202 | 64-00-6 | m-Cumenyl methylcarbamate | |
P030 | Cyanides (soluble cyanide salts), not otherwise specified | ||
P031 | 460-19-5 | Cyanogen | |
P033 | 506-77-4 | Cyanogen chloride | |
P033 | 506-77-4 | Cyanogen chloride CNCl | |
P034 | 131-89-5 | 2-Cyclohexyl-4,6-dinitrophenol | |
P016 | 542-88-1 | Dichloromethyl ether | |
P036 | 696-28-6 | Dichlorophenylarsine | |
P037 | 60-57-1 | Dieldrin | |
P038 | 692-42-2 | Diethylarsine | |
P041 | 311-45-5 | Diethyl-p-nitrophenyl phosphate | |
P040 | 297-97-2 | O,O-Diethyl O-pyrazinyl phosphorothioate | |
P043 | 55-91-4 | Diisopropylfluorophosphate (DFP) | |
P191 | 644-64-4 | Dimetilan | |
P004 | 309-00-2 | 1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1 a ,4 a ,4a b ,5 a ,8 a ,8a b )- | |
P060 | 465-73-6 | 1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1 a ,4 a ,4a b ,5 b ,8 b ,8a b )- | |
P037 | 60-57-1 | 2,7:3,6-Dimethanonaphth(2,3-b)oxirene, 3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-, (1a a ,2 b ,2a a ,3 b ,6 b ,6a a ,7 b ,7a a )- | |
P051 | 72-20-8* | 2,7:3,6-Dimethanonaphth(2,3-b)oxirene, 3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-, (1a a ,2 b ,2a b ,3 a ,6 a ,6a b ,7 b ,7a a )-, and metabolites | |
P044 | 60-51-5 | Dimethoate | |
P046 | 122-09-8 | a , a -Dimethylphenethylamine | |
P047 | 534-52-1* | 4,6-Dinitro-o-cresol and salts | |
P048 | 51-28-5 | 2,4-Dinitrophenol | |
P020 | 88-85-7 | Dinoseb | |
P085 | 152-16-9 | Diphosphoramide, octamethyl- | |
P111 | 107-49-3 | Diphosphoric acid, tetraethyl ester | |
P039 | 298-04-4 | Disulfoton | |
P049 | 541-53-7 | Dithiobiuret | |
P185 | 26419-73-8 | 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O-((methylamino)- carbonyl)oxime | |
P050 | 115-29-7 | Endosulfan | |
P088 | 145-73-3 | Endothall | |
P051 | 72-20-8 | Endrin | |
P051 | 72-20-8 | Endrin, and metabolites | |
P042 | 51-43-4 | Epinephrine | |
P031 | 460-19-5 | Ethanedinitrile | |
P194 | 23135-22-0 | Ethanimidothioic acid, 2-(dimethylamino)-N-(((methylamino)carbonyl)oxy)-2-oxo-, methyl ester | |
P066 | 16752-77-5 | Ethanimidothioic acid, N-(((methylamino)carbonyl)oxy)-, methyl ester | |
P101 | 107-12-0 | Ethyl cyanide | |
P054 | 151-56-4 | Ethyleneimine | |
P097 | 52-85-7 | Famphur | |
P056 | 7782-41-4 | Fluorine | |
P057 | 640-19-7 | Fluoroacetamide | |
P058 | 62-74-8 | Fluoroacetic acid, sodium salt | |
P198 | 23422-53-9 | Formetanate hydrochloride | |
P197 | 17702-57-7 | Formparanate | |
P065 | 628-86-4 | Fulminic acid, mercury (2+) salt | (R, T) |
P059 | 76-44-8 | Heptachlor | |
P062 | 757-58-4 | Hexaethyl tetraphosphate | |
P116 | 79-19-6 | Hydrazinecarbothioamide | |
P068 | 60-34-4 | Hydrazine, methyl- | |
P063 | 74-90-8 | Hydrocyanic acid | |
P063 | 74-90-8 | Hydrogen cyanide | |
P096 | 7803-51-2 | Hydrogen phosphide | |
P060 | 465-73-6 | Isodrin | |
P192 | 119-38-0 | Isolan | |
P202 | 64-00-6 | 3-Isopropylphenyl-N-methylcarbamate | |
P007 | 2763-96-4 | 3(2H)-Isoxazolone, 5-(aminomethyl)- | |
P196 | 15339-36-3 | Manganese, bis(dimethylcarbamodithioato-S,S’)- | |
P196 | 15339-36-3 | Manganese dimethyldithiocarbamate | |
P092 | 62-38-4 | Mercury, (acetato-O)phenyl- | |
P065 | 628-86-4 | Mercury fulminate | (R, T) |
P082 | 62-75-9 | Methanamine, N-methyl-N-nitroso- | |
P064 | 624-83-9 | Methane, isocyanato- | |
P016 | 542-88-1 | Methane, oxybis(chloro- | |
P112 | 509-14-8 | Methane, tetranitro- | (R) |
P118 | 75-70-7 | Methanethiol, trichloro- | |
P198 | 23422-53-9 | Methanimidamide, N,N-dimethyl-N’-(3-(((methylamino)-carbonyl)oxy)phenyl)-, monohydrochloride | |
P197 | 17702-57-7 | Methanimidamide, N,N-dimethyl-N’-(2-methyl-4-(((methylamino)carbonyl)oxy)phenyl)- | |
P199 | 2032-65-7 | Methiocarb | |
P050 | 115-29-7 | 6,9-Methano-2,4,3-benzodioxathiepen, 6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide | |
P059 | 76-44-8 | 4,7-Methano-1H-indene, 1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro- | |
P066 | 16752-77-5 | Methomyl | |
P068 | 60-34-4 | Methyl hydrazine | |
P064 | 624-83-9 | Methyl isocyanate | |
P069 | 75-86-5 | 2-Methyllactonitrile | |
P071 | 298-00-0 | Methyl parathion | |
P190 | 1129-41-5 | Metolcarb | |
P128 | 315-18-4 | Mexacarbate | |
P072 | 86-88-4 | a -Naphthylthiourea | |
P073 | 13463-39-3 | Nickel carbonyl | |
P073 | 13463-39-3 | Nickel carbonyl Ni(CO)4, (T-4)- | |
P074 | 557-19-7 | Nickel cyanide | |
P074 | 557-19-7 | Nickel cyanide Ni(CN)2 | |
P075 | 54-11-5* | Nicotine, and salts (excluding patches, gums and lozenges that are FDA-approved over-the-counter nicotine replacement therapies) | |
P076 | 10102-43-9 | Nitric oxide | |
P077 | 100-01-6 | p-Nitroaniline | |
P078 | 10102-44-0 | Nitrogen dioxide | |
P076 | 10102-43-9 | Nitrogen oxide NO | |
P078 | 10102-44-0 | Nitrogen oxide NO2 | |
P081 | 55-63-0 | Nitroglycerine | (R) |
P082 | 62-75-9 | N-Nitrosodimethylamine | |
P084 | 4549-40-0 | N-Nitrosomethylvinylamine | |
P085 | 152-16-9 | Octamethylpyrophosphoramide | |
P087 | 20816-12-0 | Osmium oxide OsO4, (T-4)- | |
P087 | 20816-12-0 | Osmium tetroxide | |
P088 | 145-73-3 | 7-Oxabicyclo(2.2.1)heptane-2,3-dicarboxylic acid | |
P194 | 23135-22-0 | Oxamyl | |
P089 | 56-38-2 | Parathion | |
P034 | 131-89-5 | Phenol, 2-cyclohexyl-4,6-dinitro- | |
P128 | 315-18-4 | Phenol, 4-(dimethylamino)-3,5-dimethyl-, methylcarbamate (ester) | |
P199 | 2032-65-7 | Phenol, (3,5-dimethyl-4-(methylthio)-, methylcarbamate | |
P048 | 51-28-5 | Phenol, 2,4-dinitro- | |
P047 | 534-52-1* | Phenol, 2-methyl-4,6-dinitro-, and salts | |
P202 | 64-00-6 | Phenol, 3-(1-methylethyl)-, methyl carbamate | |
P201 | 2631-37-0 | Phenol, 3-methyl-5-(1-methylethyl)-, methyl carbamate | |
P020 | 88-85-7 | Phenol, 2-(1-methylpropyl)-4,6-dinitro- | |
P009 | 131-74-8 | Phenol, 2,4,6-trinitro-, ammonium salt | (R) |
P092 | 62-38-4 | Phenylmercury acetate | |
P093 | 103-85-5 | Phenylthiourea | |
P094 | 298-02-2 | Phorate | |
P095 | 75-44-5 | Phosgene | |
P096 | 7803-51-2 | Phosphine | |
P041 | 311-45-5 | Phosphoric acid, diethyl 4-nitrophenyl ester | |
P039 | 298-04-4 | Phosphorodithioic acid, O,O-diethyl S-(2-(ethylthio)ethyl) ester | |
P094 | 298-02-2 | Phosphorodithioic acid, O,O-diethyl S-((ethylthio)methyl) ester | |
P044 | 60-51-5 | Phosphorodithioic acid, O,O-dimethyl S-(2-(methylamino)-2-oxoethyl)ester | |
P043 | 55-91-4 | Phosphorofluoridic acid, bis(1-methylethyl)ester | |
P089 | 56-38-2 | Phosphorothioic acid, O,O-diethyl O-(4-nitrophenyl) ester | |
P040 | 297-97-2 | Phosphorothioic acid, O,O-diethyl O-pyrazinyl ester | |
P097 | 52-85-7 | Phosphorothioic acid, O-(4-((dimethylamino)sulfonyl)phenyl) O,O-dimethyl ester | |
P071 | 298-00-0 | Phosphorothioic acid, O,O-dimethyl O-(4-nitrophenyl) ester | |
P204 | 57-47-6 | Physostigmine | |
P188 | 57-64-7 | Physostigmine salicylate | |
P110 | 78-00-2 | Plumbane, tetraethyl- | |
P098 | 151-50-8 | Potassium cyanide | |
P098 | 151-50-8 | Potassium cyanide KCN | |
P099 | 506-61-6 | Potassium silver cyanide | |
P201 | 2631-37-0 | Promecarb | |
P203 | 1646-88-4 | Propanal, 2-methyl-2-(methyl-sulfonyl)-, O-((methylamino)carbonyl) oxime | |
P070 | 116-06-3 | Propanal, 2-methyl-2-(methylthio)-, O-((methylamino)carbonyl)oxime | |
P101 | 107-12-0 | Propanenitrile | |
P027 | 542-76-7 | Propanenitrile, 3-chloro- | |
P069 | 75-86-5 | Propanenitrile, 2-hydroxy-2-methyl- | |
P081 | 55-63-0 | 1,2,3-Propanetriol, trinitrate- | (R) |
P017 | 598-31-2 | 2-Propanone, 1-bromo- | |
P102 | 107-19-7 | Propargyl alcohol | |
P003 | 107-02-8 | 2-Propenal | |
P005 | 107-18-6 | 2-Propen-1-ol | |
P067 | 75-55-8 | 1,2-Propylenimine | |
P102 | 107-19-7 | 2-Propyn-1-ol | |
P008 | 504-24-5 | 4-Pyridinamine | |
P075 | 54-11-5* | Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)- and salts (excluding patches, gums and lozenges that are FDA-approved over-the-counter nicotine replacement therapies) | |
P204 | 57-47-6 | Pyrrolo(2,3-b)indol-5-ol, 1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethyl-, methylcarbamate (ester), (3aS-cis)- | |
P114 | 12039-52-0 | Selenious acid, dithallium (1+) salt | |
P103 | 630-10-4 | Selenourea | |
P104 | 506-64-9 | Silver cyanide | |
P104 | 506-64-9 | Silver cyanide AgCN | |
P105 | 26628-22-8 | Sodium azide | |
P106 | 143-33-9 | Sodium cyanide | |
P106 | 143-33-9 | Sodium cyanide NaCN | |
P108 | 57-24-9* | Strychnidin-10-one, and salts | |
P018 | 357-57-3 | Strychnidin-10-one, 2,3-dimethoxy- | |
P108 | 57-24-9* | Strychnine and salts | |
P115 | 7446-18-6 | Sulfuric acid, dithallium (1+) salt | |
P109 | 3689-24-5 | Tetraethyldithiopyrophosphate | |
P110 | 78-00-2 | Tetraethyl lead | |
P111 | 107-49-3 | Tetraethylpyrophosphate | |
P112 | 509-14-8 | Tetranitromethane | (R) |
P062 | 757-58-4 | Tetraphosphoric acid, hexaethyl ester | |
P113 | 1314-32-5 | Thallic oxide | |
P113 | 1314-32-5 | Thallium oxide Tl2O3 | |
P114 | 12039-52-0 | Thallium (I) selenite | |
P115 | 7446-18-6 | Thallium (I) sulfate | |
P109 | 3689-24-5 | Thiodiphosphoric acid, tetraethyl ester | |
P045 | 39196-18-4 | Thiofanox | |
P049 | 541-53-7 | Thioimidodicarbonic diamide ((H2N)C(S))2NH | |
P014 | 108-98-5 | Thiophenol | |
P116 | 79-19-6 | Thiosemicarbazide | |
P026 | 5344-82-1 | Thiourea, (2-chlorophenyl)- | |
P072 | 86-88-4 | Thiourea, 1-naphthalenyl- | |
P093 | 103-85-5 | Thiourea, phenyl- | |
P123 | 8001-35-2 | Toxaphene | |
P185 | 26419-73-8 | Tirpate | |
P118 | 75-70-7 | Trichloromethanethiol | |
P119 | 7803-55-6 | Vanadic acid, ammonium salt | |
P120 | 1314-62-1 | Vanadium oxide V2O5 | |
P120 | 1314-62-1 | Vanadium pentoxide | |
P084 | 4549-40-0 | Vinylamine, N-methyl-N-nitroso- | |
P001 | 81-81-2* | Warfarin, and salts, when present at concentrations greater than 0.3 percent | |
P121 | 557-21-1 | Zinc cyanide | |
P121 | 557-21-1 | Zinc cyanide Zn(CN)2 | |
P205 | 137-30-4 | Zinc, bis(dimethylcarbamodithioato-S,S’)- | |
P122 | 1314-84-7 | Zinc phosphide Zn3P2, when present at concentrations greater than 10 percent | (R, T) |
P205 | 137-30-4 | Ziram |
USEPA Hazardous Waste No. | Chemical Abstracts No. (CAS No.) | Substance | Hazard Code |
P001 | 81-81-2* | 2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, and salts, when present at concentrations greater than 0.3 percent | |
P001 | 81-81-2* | Warfarin, and salts, when present at concentrations greater than 0.3 percent | |
P002 | 591-08-2 | Acetamide, N-(aminothioxomethyl) | |
P002 | 591-08-2 | 1-Acetyl-2-thiourea | |
P003 | 107-02-8 | Acrolein | |
P003 | 107-02-8 | 2-Propenal | |
P004 | 309-00-2 | Aldrin | |
P004 | 309-00-2 | 1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1 a ,4 a ,4a b ,5 a ,8 a ,8a b )- | |
P005 | 107-18-6 | Allyl alcohol | |
P005 | 107-18-6 | 2-Propen-1-ol | |
P006 | 20859-73-8 | Aluminum phosphide | (R, T) |
P007 | 2763-96-4 | 5-(Aminomethyl)-3-isoxazolol | |
P007 | 2763-96-4 | 3(2H)-Isoxazolone, 5-(aminomethyl)- | |
P008 | 504-24-5 | 4-Aminopyridine | |
P008 | 504-24-5 | 4-Pyridinamine | |
P009 | 131-74-8 | Ammonium picrate | (R) |
P009 | 131-74-8 | Phenol, 2,4,6-trinitro-, ammonium salt | (R) |
P010 | 7778-39-4 | Arsenic acid H3AsO4 | |
P011 | 1303-28-2 | Arsenic oxide As2O5 | |
P011 | 1303-28-2 | Arsenic pentoxide | |
P012 | 1327-53-3 | Arsenic oxide As2O3 | |
P012 | 1327-53-3 | Arsenic trioxide | |
P013 | 542-62-1 | Barium cyanide | |
P014 | 108-98-5 | Benzenethiol | |
P014 | 108-98-5 | Thiophenol | |
P015 | 7440-41-7 | Beryllium powder | |
P016 | 542-88-1 | Dichloromethyl ether | |
P016 | 542-88-1 | Methane, oxybis(chloro- | |
P017 | 598-31-2 | Bromoacetone | |
P017 | 598-31-2 | 2-Propanone, 1-bromo- | |
P018 | 357-57-3 | Brucine | |
P018 | 357-57-3 | Strychnidin-10-one, 2,3-dimethoxy- | |
P020 | 88-85-7 | Dinoseb | |
P020 | 88-85-7 | Phenol, 2-(1-methylpropyl)-4,6-dinitro- | |
P021 | 592-01-8 | Calcium cyanide | |
P021 | 592-01-8 | Calcium cyanide Ca(CN)2 | |
P022 | 75-15-0 | Carbon disulfide | |
P023 | 107-20-0 | Acetaldehyde, chloro- | |
P023 | 107-20-0 | Chloroacetaldehyde | |
P024 | 106-47-8 | Benzenamine, 4-chloro- | |
P024 | 106-47-8 | p-Chloroaniline | |
P026 | 5344-82-1 | 1-(o-Chlorophenyl)thiourea | |
P026 | 5344-82-1 | Thiourea, (2-chlorophenyl)- | |
P027 | 542-76-7 | 3-Chloropropionitrile | |
P027 | 542-76-7 | Propanenitrile, 3-chloro- | |
P028 | 100-44-7 | Benzene, (chloromethyl)- | |
P028 | 100-44-7 | Benzyl chloride | |
P029 | 544-92-3 | Copper cyanide | |
P029 | 544-92-3 | Copper cyanide CuCN | |
P030 | Cyanides (soluble cyanide salts), not otherwise specified | ||
P031 | 460-19-5 | Cyanogen | |
P031 | 460-19-5 | Ethanedinitrile | |
P033 | 506-77-4 | Cyanogen chloride | |
P033 | 506-77-4 | Cyanogen chloride CNCl | |
P034 | 131-89-5 | 2-Cyclohexyl-4,6-dinitrophenol | |
P034 | 131-89-5 | Phenol, 2-cyclohexyl-4,6-dinitro- | |
P036 | 696-28-6 | Arsonous dichloride, phenyl- | |
P036 | 696-28-6 | Dichlorophenylarsine | |
P037 | 60-57-1 | Dieldrin | |
P037 | 60-57-1 | 2,7:3,6-Dimethanonaphth(2,3-b)oxirene, 3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-, (1a a ,2 b ,2a a ,3 b ,6 b ,6a a ,7 b ,7a a )- | |
P038 | 692-42-2 | Arsine, diethyl- | |
P038 | 692-42-2 | Diethylarsine | |
P039 | 298-04-4 | Disulfoton | |
P039 | 298-04-4 | Phosphorodithioic acid, O,O-diethyl S-(2-(ethylthio)ethyl) ester | |
P040 | 297-97-2 | O,O-Diethyl O-pyrazinyl phosphorothioate | |
P040 | 297-97-2 | Phosphorothioic acid, O,O-diethyl O-pyrazinyl ester | |
P041 | 311-45-5 | Diethyl-p-nitrophenyl phosphate | |
P041 | 311-45-5 | Phosphoric acid, diethyl 4-nitrophenyl ester | |
P042 | 51-43-4 | 1,2-Benzenediol, 4-(1-hydroxy-2-(methylamino)ethyl)-, (R)- | |
P042 | 51-43-4 | Epinephrine | |
P043 | 55-91-4 | Diisopropylfluorophosphate (DFP) | |
P043 | 55-91-4 | Phosphorofluoridic acid, bis(1-methylethyl)ester | |
P044 | 60-51-5 | Dimethoate | |
P044 | 60-51-5 | Phosphorodithioic acid, O,O-dimethyl S-(2-(methylamino)-2-oxoethyl)ester | |
P045 | 39196-18-6 | 2-Butanone, 3,3-dimethyl-1-(methylthio)-, O-((methylamino)carbonyl) oxime | |
P045 | 39196-18-4 | Thiofanox | |
P046 | 122-09-8 | Benzeneethanamine, a , a -dimethyl- | |
P046 | 122-09-8 | a , a -Dimethylphenethylamine | |
P047 | 534-52-1* | 4,6-Dinitro-o-cresol and salts | |
P047 | 534-52-1* | Phenol, 2-methyl-4,6-dinitro-, and salts | |
P048 | 51-28-5 | 2,4-Dinitrophenol | |
P048 | 51-28-5 | Phenol, 2,4-dinitro- | |
P049 | 541-53-7 | Dithiobiuret | |
P049 | 541-53-7 | Thioimidodicarbonic diamide ((H2N)C(S))2NH | |
P050 | 115-29-7 | Endosulfan | |
P050 | 115-29-7 | 6,9-Methano-2,4,3-benzodioxathiepen, 6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide | |
P051 | 72-20-8* | 2,7:3,6-Dimethanonaphth(2,3-b)oxirene, 3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-, (1a a ,2 b ,2a b ,3 a ,6 a ,6a b ,7 b ,7a a )-, and metabolites | |
P051 | 72-20-8 | Endrin | |
P051 | 72-20-8 | Endrin, and metabolites | |
P054 | 151-56-4 | Aziridine | |
P054 | 151-56-4 | Ethyleneimine | |
P056 | 7782-41-4 | Fluorine | |
P057 | 640-19-7 | Acetamide, 2-fluoro- | |
P057 | 640-19-7 | Fluoroacetamide | |
P058 | 62-74-8 | Acetic acid, fluoro-, sodium salt | |
P058 | 62-74-8 | Fluoroacetic acid, sodium salt | |
P059 | 76-44-8 | Heptachlor | |
P059 | 76-44-8 | 4,7-Methano-1H-indene, 1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro- | |
P060 | 465-73-6 | 1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1 a ,4 a ,4a b ,5 b ,8 b ,8a b )- | |
P060 | 465-73-6 | Isodrin | |
P062 | 757-58-4 | Hexaethyl tetraphosphate | |
P062 | 757-58-4 | Tetraphosphoric acid, hexaethyl ester | |
P063 | 74-90-8 | Hydrocyanic acid | |
P063 | 74-90-8 | Hydrogen cyanide | |
P064 | 624-83-9 | Methane, isocyanato- | |
P064 | 624-83-9 | Methyl isocyanate | |
P065 | 628-86-4 | Fulminic acid, mercury (2+) salt | (R, T) |
P065 | 628-86-4 | Mercury fulminate | (R, T) |
P066 | 16752-77-5 | Ethanimidothioic acid, N-(((methylamino)carbonyl)oxy)-, methyl ester | |
P066 | 16752-77-5 | Methomyl | |
P067 | 75-55-8 | Aziridine, 2-methyl | |
P067 | 75-55-8 | 1,2-Propylenimine | |
P068 | 60-34-4 | Hydrazine, methyl- | |
P068 | 60-34-4 | Methyl hydrazine | |
P069 | 75-86-5 | 2-Methyllactonitrile | |
P069 | 75-86-5 | Propanenitrile, 2-hydroxy-2-methyl- | |
P070 | 116-06-3 | Aldicarb | |
P070 | 116-06-3 | Propanal, 2-methyl-2-(methylthio)-, O-((methylamino)carbonyl)oxime | |
P071 | 298-00-0 | Methyl parathion | |
P071 | 298-00-0 | Phosphorothioic acid, O,O-dimethyl O-(4-nitrophenyl) ester | |
P072 | 86-88-4 | a -Naphthylthiourea | |
P072 | 86-88-4 | Thiourea, 1-naphthalenyl- | |
P073 | 13463-39-3 | Nickel carbonyl | |
P073 | 13463-39-3 | Nickel carbonyl Ni(CO)4, (T-4)- | |
P074 | 557-19-7 | Nickel cyanide | |
P074 | 557-19-7 | Nickel cyanide Ni(CN)2 | |
P075 | 54-11-5* | Nicotine, and salts (excluding patches, gums and lozenges that are FDA-approved over-the-counter nicotine replacement therapies) | |
P075 | 54-11-5* | Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)- and salts (excluding patches, gums and lozenges that are FDA-approved over-the-counter nicotine replacement therapies) | |
P076 | 10102-43-9 | Nitric oxide | |
P076 | 10102-43-9 | Nitrogen oxide NO | |
P077 | 100-01-6 | Benzenamine, 4-nitro- | |
P077 | 100-01-6 | p-Nitroaniline | |
P078 | 10102-44-0 | Nitrogen dioxide | |
P078 | 10102-44-0 | Nitrogen oxide NO2 | |
P081 | 55-63-0 | Nitroglycerine | (R) |
P081 | 55-63-0 | 1,2,3-Propanetriol, trinitrate- | (R) |
P082 | 62-75-9 | Methanamine, N-methyl-N-nitroso- | |
P082 | 62-75-9 | N-Nitrosodimethylamine | |
P084 | 4549-40-0 | N-Nitrosomethylvinylamine | |
P084 | 4549-40-0 | Vinylamine, N-methyl-N-nitroso- | |
P085 | 152-16-9 | Diphosphoramide, octamethyl- | |
P085 | 152-16-9 | Octamethylpyrophosphoramide | |
P087 | 20816-12-0 | Osmium oxide OsO4, (T-4)- | |
P087 | 20816-12-0 | Osmium tetroxide | |
P088 | 145-73-3 | Endothall | |
P088 | 145-73-3 | 7-Oxabicyclo(2.2.1)heptane-2,3-dicarboxylic acid | |
P089 | 56-38-2 | Parathion | |
P089 | 56-38-2 | Phosphorothioic acid, O,O-diethyl O-(4-nitrophenyl) ester | |
P092 | 62-38-4 | Mercury, (acetato-O)phenyl- | |
P092 | 62-38-4 | Phenylmercury acetate | |
P093 | 103-85-5 | Phenylthiourea | |
P093 | 103-85-5 | Thiourea, phenyl- | |
P094 | 298-02-2 | Phorate | |
P094 | 298-02-2 | Phosphorodithioic acid, O,O-diethyl S-((ethylthio)methyl) ester | |
P095 | 75-44-5 | Carbonic dichloride | |
P095 | 75-44-5 | Phosgene | |
P096 | 7803-51-2 | Hydrogen phosphide | |
P096 | 7803-51-2 | Phosphine | |
P097 | 52-85-7 | Famphur | |
P097 | 52-85-7 | Phosphorothioic acid, O-(4-((dimethylamino)sulfonyl)phenyl) O,O-dimethyl ester | |
P098 | 151-50-8 | Potassium cyanide | |
P098 | 151-50-8 | Potassium cyanide KCN | |
P099 | 506-61-6 | Argentate(1-), bis(cyano-C)-, potassium | |
P099 | 506-61-6 | Potassium silver cyanide | |
P101 | 107-12-0 | Ethyl cyanide | |
P101 | 107-12-0 | Propanenitrile | |
P102 | 107-19-7 | Propargyl alcohol | |
P102 | 107-19-7 | 2-Propyn-1-ol | |
P103 | 630-10-4 | Selenourea | |
P104 | 506-64-9 | Silver cyanide | |
P104 | 506-64-9 | Silver cyanide AgCN | |
P105 | 26628-22-8 | Sodium azide | |
P106 | 143-33-9 | Sodium cyanide | |
P106 | 143-33-9 | Sodium cyanide NaCN | |
P108 | 57-24-9* | Strychnidin-10-one, and salts | |
P108 | 57-24-9* | Strychnine and salts | |
P109 | 3689-24-5 | Tetraethyldithiopyrophosphate | |
P109 | 3689-24-5 | Thiodiphosphoric acid, tetraethyl ester | |
P110 | 78-00-2 | Plumbane, tetraethyl- | |
P110 | 78-00-2 | Tetraethyl lead | |
P111 | 107-49-3 | Diphosphoric acid, tetraethyl ester | |
P111 | 107-49-3 | Tetraethylpyrophosphate | |
P112 | 509-14-8 | Methane, tetranitro- | (R) |
P112 | 509-14-8 | Tetranitromethane | (R) |
P113 | 1314-32-5 | Thallic oxide | |
P113 | 1314-32-5 | Thallium oxide Tl2O3 | |
P114 | 12039-52-0 | Selenious acid, dithallium (1+) salt | |
P114 | 12039-52-0 | Thallium (I) selenite | |
P115 | 7446-18-6 | Sulfuric acid, dithallium (1+) salt | |
P115 | 7446-18-6 | Thallium (I) sulfate | |
P116 | 79-19-6 | Hydrazinecarbothioamide | |
P116 | 79-19-6 | Thiosemicarbazide | |
P118 | 75-70-7 | Methanethiol, trichloro- | |
P118 | 75-70-7 | Trichloromethanethiol | |
P119 | 7803-55-6 | Ammonium vanadate | |
P119 | 7803-55-6 | Vanadic acid, ammonium salt | |
P120 | 1314-62-1 | Vanadium oxide V2O5 | |
P120 | 1314-62-1 | Vanadium pentoxide | |
P121 | 557-21-1 | Zinc cyanide | |
P121 | 557-21-1 | Zinc cyanide Zn(CN)2 | |
P122 | 1314-84-7 | Zinc phosphide Zn3P2, when present at concentrations greater than 10 percent | (R, T) |
P123 | 8001-35-2 | Toxaphene | |
P127 | 1563-66-2 | 7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-, methylcarbamate | |
P127 | 1563-66-2 | Carbofuran | |
P128 | 315-18-4 | Phenol, 4-(dimethylamino)-3,5-dimethyl-, methylcarbamate (ester) | |
P128 | 315-18-4 | Mexacarbate | |
P185 | 26419-73-8 | 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O-((methylamino)- carbonyl)oxime | |
P185 | 26419-73-8 | Tirpate | |
P188 | 57-64-7 | Benzoic acid, 2-hydroxy-, compound with (3aS-cis)-1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethylpyrrolo(2,3-b)indol-5-yl methylcarbamate ester (1:1) | |
P188 | 57-64-7 | Physostigmine salicylate | |
P189 | 55285-14-8 | Carbamic acid, ((dibutylamino)-thio)methyl-, 2,3-dihydro-2,2-dimethyl-7-benzofuranyl ester | |
P189 | 55285-14-8 | Carbosulfan | |
P190 | 1129-41-5 | Carbamic acid, methyl-, 3-methylphenyl ester | |
P190 | 1129-41-5 | Metolcarb | |
P191 | 644-64-4 | Carbamic acid, dimethyl-, 1-((dimethyl-amino)carbonyl)-5-methyl-1H-pyrazol-3-yl ester | |
P191 | 644-64-4 | Dimetilan | |
P192 | 119-38-0 | Carbamic acid, dimethyl-, 3-methyl-1-(1-methylethyl)-1H-pyrazol-5-yl ester | |
P192 | 119-38-0 | Isolan | |
P194 | 23135-22-0 | Ethanimidothioic acid, 2-(dimethylamino)-N-(((methylamino)carbonyl)oxy)-2-oxo-, methyl ester | |
P194 | 23135-22-0 | Oxamyl | |
P196 | 15339-36-3 | Manganese, bis(dimethylcarbamodithioato-S,S’)- | |
P196 | 15339-36-3 | Manganese dimethyldithiocarbamate | |
P197 | 17702-57-7 | Formparanate | |
P197 | 17702-57-7 | Methanimidamide, N,N-dimethyl-N’-(2-methyl-4-(((methylamino)carbonyl)oxy)phenyl)- | |
P198 | 23422-53-9 | Formetanate hydrochloride | |
P198 | 23422-53-9 | Methanimidamide, N,N-dimethyl-N’-(3-(((methylamino)-carbonyl)oxy)phenyl)-, monohydrochloride | |
P199 | 2032-65-7 | Methiocarb | |
P199 | 2032-65-7 | Phenol, (3,5-dimethyl-4-(methylthio)-, methylcarbamate | |
P201 | 2631-37-0 | Phenol, 3-methyl-5-(1-methylethyl)-, methyl carbamate | |
P201 | 2631-37-0 | Promecarb | |
P202 | 64-00-6 | m-Cumenyl methylcarbamate | |
P202 | 64-00-6 | 3-Isopropylphenyl-N-methylcarbamate | |
P202 | 64-00-6 | Phenol, 3-(1-methylethyl)-, methyl carbamate | |
P203 | 1646-88-4 | Aldicarb sulfone | |
P203 | 1646-88-4 | Propanal, 2-methyl-2-(methyl-sulfonyl)-, O-((methylamino)carbonyl) oxime | |
P204 | 57-47-6 | Physostigmine | |
P204 | 57-47-6 | Pyrrolo(2,3-b)indol-5-ol, 1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethyl-, methylcarbamate (ester), (3aS-cis)- | |
P205 | 137-30-4 | Zinc, bis(dimethylcarbamodithioato-S,S’)- | |
P205 | 137-30-4 | Ziram |
f) The commercial chemical products, manufacturing chemical intermediates, or off-specification commercial chemical products referred to in subsections (a) through (d), are identified as toxic wastes (T) unless otherwise designated. These wastes and their corresponding USEPA hazardous waste numbers are the following:
BOARD NOTE: For the convenience of the regulated community, the primary hazardous properties of these materials have been indicated by the letters T (Toxicity), R (Reactivity), I (Ignitability), and C (Corrosivity). The absence of a letter indicates that the compound is only listed for toxicity. Wastes are first listed in alphabetical order by substance and then listed again in numerical order by USEPA hazardous waste number.
USEPA Hazardous Waste No. | Chemical Abstracts No. (CAS No.) | Substance | Hazard Code |
U394 | 30558-43-1 | A2213 | |
U001 | 75-07-0 | Acetaldehyde | (I) |
U034 | 75-87-6 | Acetaldehyde, trichloro- | |
U187 | 62-44-2 | Acetamide, N-(4-ethoxyphenyl)- | |
U005 | 53-96-3 | Acetamide, N-9H-fluoren-2-yl- | |
U240 | P 94-75-7 | Acetic acid, (2,4-dichlorophenoxy)-, salts and esters | |
U112 | 141-78-6 | Acetic acid, ethyl ester | (I) |
U144 | 301-04-2 | Acetic acid, lead (2+) salt | |
U214 | 563-68-8 | Acetic acid, thallium (1+) salt | |
See F027 | 93-76-5 | Acetic acid, (2,4,5-trichlorophenoxy)- | |
U002 | 67-64-1 | Acetone | (I) |
U003 | 75-05-8 | Acetonitrile | (I, T) |
U004 | 98-86-2 | Acetophenone | |
U005 | 53-96-3 | 2-Acetylaminofluorene | |
U006 | 75-36-5 | Acetyl chloride | (C, R, T) |
U007 | 79-06-1 | Acrylamide | |
U008 | 79-10-7 | Acrylic acid | (I) |
U009 | 107-13-1 | Acrylonitrile | |
U011 | 61-82-5 | Amitrole | |
U012 | 62-53-3 | Aniline | (I, T) |
U136 | 75-60-5 | Arsinic acid, dimethyl- | |
U014 | 492-80-8 | Auramine | |
U015 | 115-02-6 | Azaserine | |
U010 | 50-07-7 | Azirino(2',3':3,4)pyrrolo(1,2-a)indole-4,7-dione, 6-amino-8-(((aminocarbonyl)oxy)methyl)-1,1a,2,8,8a,8b-hexahydro-8a-methoxy-5-methyl-, (1a-S-(1a a ,8 b ,8a a ,8b a ))- | |
U280 | 101-27-9 | Barban | |
U278 | 22781-23-3 | Bendiocarb | |
U364 | 22961-82-6 | Bendiocarb phenol | |
U271 | 17804-35-2 | Benomyl | |
U157 | 56-49-5 | Benz(j)aceanthrylene, 1,2-dihydro-3-methyl- | |
U016 | 225-51-4 | Benz(c)acridine | |
U017 | 98-87-3 | Benzal chloride | |
U192 | 23950-58-5 | Benzamide, 3,5-dichloro-N-(1,1-dimethyl-2-propynyl)- | |
U018 | 56-55-3 | Benz(a)anthracene | |
U094 | 57-97-6 | Benz(a)anthracene, 7,12-dimethyl- | |
U012 | 62-53-3 | Benzenamine | (I, T) |
U014 | 492-80-8 | Benzenamine, 4,4'-carbonimidoylbis(N,N-dimethyl- | |
U049 | 3165-93-3 | Benzenamine, 4-chloro-2-methyl-, hydrochloride | |
U093 | 60-11-7 | Benzenamine, N,N-dimethyl-4-(phenylazo)- | |
U328 | 95-53-4 | Benzenamine, 2-methyl- | |
U353 | 106-49-0 | Benzenamine, 4-methyl- | |
U158 | 101-14-4 | Benzenamine, 4,4'-methylenebis(2-chloro- | |
U222 | 636-21-5 | Benzenamine, 2-methyl-, hydrochloride | |
U181 | 99-55-8 | Benzenamine, 2-methyl-5-nitro- | |
U019 | 71-43-2 | Benzene | (I, T) |
U038 | 510-15-6 | Benzeneacetic acid, 4-chloro- a -(4-chlorophenyl)- a -hydroxy-, ethyl ester | |
U030 | 101-55-3 | Benzene, 1-bromo-4-phenoxy- | |
U035 | 305-03-3 | Benzenebutanoic acid, 4-(bis(2-chloroethyl)amino)- | |
U037 | 108-90-7 | Benzene, chloro- | |
U221 | 25376-45-8 | Benzenediamine, ar-methyl- | |
U028 | 117-81-7 | 1,2-Benzenedicarboxylic acid, bis(2-ethylhexyl) ester | |
U069 | 84-74-2 | 1,2-Benzenedicarboxylic acid, dibutyl ester | |
U088 | 84-66-2 | 1,2-Benzenedicarboxylic acid, diethyl ester | |
U102 | 131-11-3 | 1,2-Benzenedicarboxylic acid, dimethyl ester | |
U107 | 117-84-0 | 1,2-Benzenedicarboxylic acid, dioctyl ester | |
U070 | 95-50-1 | Benzene, 1,2-dichloro- | |
U071 | 541-73-1 | Benzene, 1,3-dichloro- | |
U072 | 106-46-7 | Benzene, 1,4-dichloro- | |
U060 | 72-54-8 | Benzene, 1,1'-(2,2-dichloroethylidene)bis(4-chloro- | |
U017 | 98-87-3 | Benzene, (dichloromethyl)- | |
U223 | 26471-62-5 | Benzene, 1,3-diisocyanatomethyl- | (R, T) |
U239 | 1330-20-7 | Benzene, dimethyl- | (I) |
U201 | 108-46-3 | 1,3-Benzenediol | |
U127 | 118-74-1 | Benzene, hexachloro- | |
U056 | 110-82-7 | Benzene, hexahydro- | (I) |
U220 | 108-88-3 | Benzene, methyl- | |
U105 | 121-14-2 | Benzene, 1-methyl-2,4-dinitro- | |
U106 | 606-20-2 | Benzene, 2-methyl-1,3-dinitro- | |
U055 | 98-82-8 | Benzene, (1-methylethyl)- | (I) |
U169 | 98-95-3 | Benzene, nitro- | (I, T) |
U183 | 608-93-5 | Benzene, pentachloro- | |
U185 | 82-68-8 | Benzene, pentachloronitro- | |
U020 | 98-09-9 | Benzenesulfonic acid chloride | (C, R) |
U020 | 98-09-9 | Benzenesulfonyl chloride | (C, R) |
U207 | 95-94-3 | Benzene, 1,2,4,5-tetrachloro- | |
U061 | 50-29-3 | Benzene, 1,1'-(2,2,2-trichloroethylidene)bis(4-chloro- | |
U247 | 72-43-5 | Benzene, 1,1'-(2,2,2-trichloroethylidene)bis(4-methoxy- | |
U023 | 98-07-7 | Benzene, (trichloromethyl)- | (C, R, T) |
U234 | 99-35-4 | Benzene, 1,3,5-trinitro- | (R, T) |
U021 | 92-87-5 | Benzidene | |
U203 | 94-59-7 | 1,3-Benzodioxole, 5-(2-propenyl)- | |
U141 | 120-58-1 | 1,3-Benzodioxole, 5-(1-propenyl)- | |
U090 | 94-58-6 | 1,3-Benzodioxole, 5-propyl- | |
U278 | 22781-23-3 | 1,3-Benzodioxol-4-ol, 2,2-dimethyl-, methyl carbamate | |
U364 | 22961-82-6 | 1,3-Benzodioxol-4-ol, 2,2-dimethyl- | |
U367 | 1563-38-8 | 7-Benzofuranol, 2,3-dihydro-2,2-dimethyl- | |
U064 | 189-55-9 | Benzo(rst)pentaphene | |
U248 | 81-81-2 | 2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, and salts, when present at concentrations of 0.3 percent or less | |
U022 | 50-32-8 | Benzo(a)pyrene | |
U197 | 106-51-4 | p-Benzoquinone | |
U023 | 98-07-7 | Benzotrichloride | (C, R, T) |
U085 | 1464-53-5 | 2,2'-Bioxirane | (I, T) |
U021 | 92-87-5 | (1,1'-Biphenyl)-4,4'-diamine | |
U073 | 91-94-1 | (1,1'-Biphenyl)-4,4'-diamine, 3,3'-dichloro- | |
U091 | 119-90-4 | (1,1'-Biphenyl)-4,4'-diamine, 3,3'-dimethoxy- | |
U095 | 119-93-7 | (1,1'-Biphenyl)-4,4'-diamine, 3,3'-dimethyl- | |
U225 | 75-25-2 | Bromoform | |
U030 | 101-55-3 | 4-Bromophenyl phenyl ether | |
U128 | 87-68-3 | 1,3-Butadiene, 1,1,2,3,4,4-hexachloro- | |
U172 | 924-16-3 | 1-Butanamine, N-butyl-N-nitroso- | |
U031 | 71-36-3 | 1-Butanol | (I) |
U159 | 78-93-3 | 2-Butanone | (I, T) |
U160 | 1338-23-4 | 2-Butanone, peroxide | (R, T) |
U053 | 4170-30-3 | 2-Butenal | |
U074 | 764-41-0 | 2-Butene, 1,4-dichloro- | (I, T) |
U143 | 303-34-4 | 2-Butenoic acid, 2-methyl-, 7-((2,3-dihydroxy-2-(1-methoxyethyl)-3-methyl-1-oxobutoxy)methyl)-2,3,5,7a-tetrahydro-1H-pyrrolizin-1-yl ester, (1S-(1 a (Z), 7(2S*,3R*), 7a a ))- | |
U031 | 71-36-3 | n-Butyl alcohol | (I) |
U136 | 75-60-5 | Cacodylic acid | |
U032 | 13765-19-0 | Calcium chromate | |
U372 | 10605-21-7 | Carbamic acid, 1H-benzimidazol-2-yl, methyl ester | |
U271 | 17804-35-2 | Carbamic acid, (1-((butylamino)carbonyl)-1H-benzimidazol-2-yl)-, methyl ester | |
U280 | 101-27-9 | Carbamic acid, (3-chlorophenyl)-, 4-chloro-2-butynyl ester | |
U238 | 51-79-6 | Carbamic acid, ethyl ester | |
U178 | 615-53-2 | Carbamic acid, methylnitroso-, ethyl ester | |
U373 | 122-42-9 | Carbamic acid, phenyl-, 1-methylethyl ester | |
U409 | 23564-05-8 | Carbamic acid, (1,2-phenylenebis(iminocarbonothioyl))bis-, dimethyl ester | |
U097 | 79-44-7 | Carbamic chloride, dimethyl- | |
U114 | P 111-54-6 | Carbamodithioic acid, 1,2-ethanediylbis-, salts and esters | |
U062 | 2303-16-4 | Carbamothioic acid, bis(1-methylethyl)-, S-(2,3-dichloro-2-propenyl) ester | |
U389 | 2303-17-5 | Carbamothioic acid, bis(1-methylethyl)-, S-(2,3,3-trichloro-2-propenyl) ester | |
U387 | 52888-80-9 | Carbamothioic acid, dipropyl-, S-(phenylmethyl) ester | |
U279 | 63-25-2 | Carbaryl | |
U372 | 10605-21-7 | Carbendazim | |
U367 | 1563-38-8 | Carbofuran phenol | |
U215 | 6533-73-9 | Carbonic acid, dithallium (1+) salt | |
U033 | 353-50-4 | Carbonic difluoride | (R, T) |
U156 | 79-22-1 | Carbonochloridic acid, methyl ester | (I, T) |
U033 | 353-50-4 | Carbon oxyfluoride | (R, T) |
U211 | 56-23-5 | Carbon tetrachloride | |
U034 | 75-87-6 | Chloral | |
U035 | 305-03-3 | Chlorambucil | |
U036 | 57-74-9 | Chlordane, a and g isomers | |
U026 | 494-03-1 | Chlornaphazin | |
U037 | 108-90-7 | Chlorobenzene | |
U038 | 510-15-6 | Chlorobenzilate | |
U039 | 59-50-7 | p-Chloro-m-cresol | |
U042 | 110-75-8 | 2-Chloroethyl vinyl ether | |
U044 | 67-66-3 | Chloroform | |
U046 | 107-30-2 | Chloromethyl methyl ether | |
U047 | 91-58-7 | b -Chloronaphthalene | |
U048 | 95-57-8 | o-Chlorophenol | |
U049 | 3165-93-3 | 4-Chloro-o-toluidine, hydrochloride | |
U032 | 13765-19-0 | Chromic acid H2CrO4, calcium salt | |
U050 | 218-01-9 | Chrysene | |
U051 | Creosote | ||
U052 | 1319-77-3 | Cresol (Cresylic acid) | |
U053 | 4170-30-3 | Crotonaldehyde | |
U055 | 98-82-8 | Cumene | (I) |
U246 | 506-68-3 | Cyanogen bromide CNBr | |
U197 | 106-51-4 | 2,5-Cyclohexadiene-1,4-dione | |
U056 | 110-82-7 | Cyclohexane | (I) |
U129 | 58-89-9 | Cyclohexane, 1,2,3,4,5,6-hexachloro-, (1 a ,2 a ,3 b ,4 a ,5 a ,6 b )- | |
U057 | 108-94-1 | Cyclohexanone | (I) |
U130 | 77-47-4 | 1,3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro- | |
U058 | 50-18-0 | Cyclophosphamide | |
U240 | P 94-75-7 | 2,4-D, salts and esters | |
U059 | 20830-81-3 | Daunomycin | |
U060 | 72-54-8 | DDD | |
U061 | 50-29-3 | DDT | |
U062 | 2303-16-4 | Diallate | |
U063 | 53-70-3 | Dibenz(a,h)anthracene | |
U064 | 189-55-9 | Dibenzo(a,i)pyrene | |
U066 | 96-12-8 | 1,2-Dibromo-3-chloropropane | |
U069 | 84-74-2 | Dibutyl phthalate | |
U070 | 95-50-1 | o-Dichlorobenzene | |
U071 | 541-73-1 | m-Dichlorobenzene | |
U072 | 106-46-7 | p-Dichlorobenzene | |
U073 | 91-94-1 | 3,3'-Dichlorobenzidine | |
U074 | 764-41-0 | 1,4-Dichloro-2-butene | (I, T) |
U075 | 75-71-8 | Dichlorodifluoromethane | |
U078 | 75-35-4 | 1,1-Dichloroethylene | |
U079 | 156-60-5 | 1,2-Dichloroethylene | |
U025 | 111-44-4 | Dichloroethyl ether | |
U027 | 108-60-1 | Dichloroisopropyl ether | |
U024 | 111-91-1 | Dichloromethoxy ethane | |
U081 | 120-83-2 | 2,4-Dichlorophenol | |
U082 | 87-65-0 | 2,6-Dichlorophenol | |
U084 | 542-75-6 | 1,3-Dichloropropene | |
U085 | 1464-53-5 | 1,2:3,4-Diepoxybutane | (I, T) |
U395 | 5952-26-1 | Diethylene glycol, dicarbamate | |
U108 | 123-91-1 | 1,4-Diethyleneoxide | |
U028 | 117-81-7 | Diethylhexyl phthalate | |
U086 | 1615-80-1 | N,N'-Diethylhydrazine | |
U087 | 3288-58-2 | O,O-Diethyl S-methyl dithiophosphate | |
U088 | 84-66-2 | Diethyl phthalate | |
U089 | 56-53-1 | Diethylstilbestrol | |
U090 | 94-58-6 | Dihydrosafrole | |
U091 | 119-90-4 | 3,3'-Dimethoxybenzidine | |
U092 | 124-40-3 | Dimethylamine | (I) |
U093 | 60-11-7 | p-Dimethylaminoazobenzene | |
U094 | 57-97-6 | 7,12-Dimethylbenz(a)anthracene | |
U095 | 119-93-7 | 3,3'-Dimethylbenzidine | |
U096 | 80-15-9 | a , a -Dimethylbenzylhydroperoxide | (R) |
U097 | 79-44-7 | Dimethylcarbamoyl chloride | |
U098 | 57-14-7 | 1,1-Dimethylhydrazine | |
U099 | 540-73-8 | 1,2-Dimethylhydrazine | |
U101 | 105-67-9 | 2,4-Dimethylphenol | |
U102 | 131-11-3 | Dimethyl phthalate | |
U103 | 77-78-1 | Dimethyl sulfate | |
U105 | 121-14-2 | 2,4-Dinitrotoluene | |
U106 | 606-20-2 | 2,6-Dinitrotoluene | |
U107 | 117-84-0 | Di-n-octyl phthalate | |
U108 | 123-91-1 | 1,4-Dioxane | |
U109 | 122-66-7 | 1,2-Diphenylhydrazine | |
U110 | 142-84-7 | Dipropylamine | (I) |
U111 | 621-64-7 | Di-n-propylnitrosamine | |
U041 | 106-89-8 | Epichlorohydrin | |
U001 | 75-07-0 | Ethanal | (I) |
U404 | 121-44-8 | Ethanamine, N,N-diethyl- | |
U174 | 55-18-5 | Ethanamine, N-ethyl-N-nitroso- | |
U155 | 91-80-5 | 1,2-Ethanediamine, N,N-dimethyl-N'-2-pyridinyl-N'-(2-thienylmethyl)- | |
U067 | 106-93-4 | Ethane, 1,2-dibromo- | |
U076 | 75-34-3 | Ethane, 1,1-dichloro- | |
U077 | 107-06-2 | Ethane, 1,2-dichloro- | |
U131 | 67-72-1 | Ethane, hexachloro- | |
U024 | 111-91-1 | Ethane, 1,1'-(methylenebis(oxy))bis(2-chloro- | |
U117 | 60-29-7 | Ethane, 1,1'-oxybis- | (I) |
U025 | 111-44-4 | Ethane, 1,1'-oxybis(2-chloro- | |
U184 | 76-01-7 | Ethane, pentachloro- | |
U208 | 630-20-6 | Ethane, 1,1,1,2-tetrachloro- | |
U209 | 79-34-5 | Ethane, 1,1,2,2-tetrachloro- | |
U218 | 62-55-5 | Ethanethioamide | |
U226 | 71-55-6 | Ethane, 1,1,1-trichloro- | |
U227 | 79-00-5 | Ethane, 1,1,2-trichloro- | |
U410 | 59669-26-0 | Ethanimidothioic acid, N,N'- (thiobis((methylimino)carbonyloxy))bis-, dimethyl ester | |
U394 | 30558-43-1 | Ethanimidothioic acid, 2-(dimethylamino)-N-hydroxy-2-oxo-, methyl ester | |
U359 | 110-80-5 | Ethanol, 2-ethoxy- | |
U173 | 1116-54-7 | Ethanol, 2,2'-(nitrosoimino)bis- | |
U395 | 5952-26-1 | Ethanol, 2,2'-oxybis-, dicarbamate | |
U004 | 98-86-2 | Ethanone, 1-phenyl- | |
U043 | 75-01-4 | Ethene, chloro- | |
U042 | 110-75-8 | Ethene, (2-chloroethoxy)- | |
U078 | 75-35-4 | Ethene, 1,1-dichloro- | |
U079 | 156-60-5 | Ethene, 1,2-dichloro-, (E)- | |
U210 | 127-18-4 | Ethene, tetrachloro- | |
U228 | 79-01-6 | Ethene, trichloro- | |
U112 | 141-78-6 | Ethyl acetate | (I) |
U113 | 140-88-5 | Ethyl acrylate | (I) |
U238 | 51-79-6 | Ethyl carbamate (urethane) | |
U117 | 60-29-7 | Ethyl ether | (I) |
U114 | P 111-54-6 | Ethylenebisdithiocarbamic acid, salts and esters | |
U067 | 106-93-4 | Ethylene dibromide | |
U077 | 107-06-2 | Ethylene dichloride | |
U359 | 110-80-5 | Ethylene glycol monoethyl ether | |
U115 | 75-21-8 | Ethylene oxide | (I, T) |
U116 | 96-45-7 | Ethylenethiourea | |
U076 | 75-34-3 | Ethylidene dichloride | |
U118 | 97-63-2 | Ethyl methacrylate | |
U119 | 62-50-0 | Ethyl methanesulfonate | |
U120 | 206-44-0 | Fluoranthene | |
U122 | 50-00-0 | Formaldehyde | |
U123 | 64-18-6 | Formic acid | (C, T) |
U124 | 110-00-9 | Furan | (I) |
U125 | 98-01-1 | 2-Furancarboxaldehyde | (I) |
U147 | 108-31-6 | 2,5-Furandione | |
U213 | 109-99-9 | Furan, tetrahydro- | (I) |
U125 | 98-01-1 | Furfural | (I) |
U124 | 110-00-9 | Furfuran | (I) |
U206 | 18883-66-4 | Glucopyranose, 2-deoxy-2-(3-methyl-3-nitrosoureido)-, D- | |
U206 | 18883-66-4 | D-Glucose, 2-deoxy-2-(((methylnitrosoamino)-carbonyl)amino)- | |
U126 | 765-34-4 | Glycidylaldehyde | |
U163 | 70-25-7 | Guanidine, N-methyl-N'-nitro-N-nitroso- | |
U127 | 118-74-1 | Hexachlorobenzene | |
U128 | 87-68-3 | Hexachlorobutadiene | |
U130 | 77-47-4 | Hexachlorocyclopentadiene | |
U131 | 67-72-1 | Hexachloroethane | |
U132 | 70-30-4 | Hexachlorophene | |
U243 | 1888-71-7 | Hexachloropropene | |
U133 | 302-01-2 | Hydrazine | (R, T) |
U086 | 1615-80-1 | Hydrazine, 1,2-diethyl- | |
U098 | 57-14-7 | Hydrazine, 1,1-dimethyl- | |
U099 | 540-73-8 | Hydrazine, 1,2-dimethyl- | |
U109 | 122-66-7 | Hydrazine, 1,2-diphenyl- | |
U134 | 7664-39-3 | Hydrofluoric acid | (C, T) |
U134 | 7664-39-3 | Hydrogen fluoride | (C, T) |
U135 | 7783-06-4 | Hydrogen sulfide | |
U135 | 7783-06-4 | Hydrogen sulfide H2S | |
U096 | 80-15-9 | Hydroperoxide, 1-methyl-1-phenylethyl- | (R) |
U116 | 96-45-7 | 2-Imidazolidinethione | |
U137 | 193-39-5 | Indeno(1,2,3-cd)pyrene | |
U190 | 85-44-9 | 1,3-Isobenzofurandione | |
U140 | 78-83-1 | Isobutyl alcohol | (I, T) |
U141 | 120-58-1 | Isosafrole | |
U142 | 143-50-0 | Kepone | |
U143 | 303-34-4 | Lasiocarpene | |
U144 | 301-04-2 | Lead acetate | |
U146 | 1335-32-6 | Lead, bis(acetato-O)tetrahydroxytri- | |
U145 | 7446-27-7 | Lead phosphate | |
U146 | 1335-32-6 | Lead subacetate | |
U129 | 58-89-9 | Lindane | |
U163 | 70-25-7 | MNNG | |
U147 | 108-31-6 | Maleic anhydride | |
U148 | 123-33-1 | Maleic hydrazide | |
U149 | 109-77-3 | Malononitrile | |
U150 | 148-82-3 | Melphalan | |
U151 | 7439-97-6 | Mercury | |
U152 | 126-98-7 | Methacrylonitrile | (I, T) |
U092 | 124-40-3 | Methanamine, N-methyl- | (I) |
U029 | 74-83-9 | Methane, bromo- | |
U045 | 74-87-3 | Methane, chloro- | (I, T) |
U046 | 107-30-2 | Methane, chloromethoxy- | |
U068 | 74-95-3 | Methane, dibromo- | |
U080 | 75-09-2 | Methane, dichloro- | |
U075 | 75-71-8 | Methane, dichlorodifluoro- | |
U138 | 74-88-4 | Methane, iodo- | |
U119 | 62-50-0 | Methanesulfonic acid, ethyl ester | |
U211 | 56-23-5 | Methane, tetrachloro- | |
U153 | 74-93-1 | Methanethiol | (I, T) |
U225 | 75-25-2 | Methane, tribromo- | |
U044 | 67-66-3 | Methane, trichloro- | |
U121 | 75-69-4 | Methane, trichlorofluoro- | |
U036 | 57-74-9 | 4,7-Methano-1H-indene, 1,2,4,5,6,7,8,8-octachloro-2,3,3a,4,7,7a-hexahydro- | |
U154 | 67-56-1 | Methanol | (I) |
U155 | 91-80-5 | Methapyrilene | |
U142 | 143-50-0 | 1,3,4-Metheno-2H-cyclobuta(cd)pentalen-2-one, 1,1a,3,3a,4,5,5,5a,5b,6-decachlorooctahydro- | |
U247 | 72-43-5 | Methoxychlor | |
U154 | 67-56-1 | Methyl alcohol | (I) |
U029 | 74-83-9 | Methyl bromide | |
U186 | 504-60-9 | 1-Methylbutadiene | (I) |
U045 | 74-87-3 | Methyl chloride | (I, T) |
U156 | 79-22-1 | Methyl chlorocarbonate | (I, T) |
U226 | 71-55-6 | Methylchloroform | |
U157 | 56-49-5 | 3-Methylcholanthrene | |
U158 | 101-14-4 | 4,4'-Methylenebis(2-chloroaniline) | |
U068 | 74-95-3 | Methylene bromide | |
U080 | 75-09-2 | Methylene chloride | |
U159 | 78-93-3 | Methyl ethyl ketone (MEK) | (I, T) |
U160 | 1338-23-4 | Methyl ethyl ketone peroxide | (R, T) |
U138 | 74-88-4 | Methyl iodide | |
U161 | 108-10-1 | Methyl isobutyl ketone | (I) |
U162 | 80-62-6 | Methyl methacrylate | (I, T) |
U161 | 108-10-1 | 4-Methyl-2-pentanone | (I) |
U164 | 56-04-2 | Methylthiouracil | |
U010 | 50-07-7 | Mitomycin C | |
U059 | 20830-81-3 | 5,12-Naphthacenedione, 8-acetyl-10-((3-amino-2,3,6-trideoxy- a -L-lyxo-hexapyranosyl)oxyl)-7,8,9,10-tetrahydro-6,8,11-trihydroxy-1-methoxy-, (8S-cis)- | |
U167 | 134-32-7 | 1-Naphthalenamine | |
U168 | 91-59-8 | 2-Naphthalenamine | |
U026 | 494-03-1 | Naphthaleneamine, N,N'-bis(2-chloroethyl)- | |
U165 | 91-20-3 | Naphthalene | |
U047 | 91-58-7 | Naphthalene, 2-chloro- | |
U166 | 130-15-4 | 1,4-Naphthalenedione | |
U236 | 72-57-1 | 2,7-Naphthalenedisulfonic acid, 3,3'-((3,3'-dimethyl-(1,1'-biphenyl)-4,4'-diyl)bis(azo)bis(5-amino-4-hydroxy)-, tetrasodium salt | |
U279 | 63-25-2 | 1-Naphthalenol, methylcarbamate | |
U166 | 130-15-4 | 1,4-Naphthoquinone | |
U167 | 134-32-7 | a -Naphthylamine | |
U168 | 91-59-8 | b -Naphthylamine | |
U217 | 10102-45-1 | Nitric acid, thallium (1+) salt | |
U169 | 98-95-3 | Nitrobenzene | (I, T) |
U170 | 100-02-7 | p-Nitrophenol | |
U171 | 79-46-9 | 2-Nitropropane | (I, T) |
U172 | 924-16-3 | N-Nitrosodi-n-butylamine | |
U173 | 1116-54-7 | N-Nitrosodiethanolamine | |
U174 | 55-18-5 | N-Nitrosodiethylamine | |
U176 | 759-73-9 | N-Nitroso-N-ethylurea | |
U177 | 684-93-5 | N-Nitroso-N-methylurea | |
U178 | 615-53-2 | N-Nitroso-N-methylurethane | |
U179 | 100-75-4 | N-Nitrosopiperidine | |
U180 | 930-55-2 | N-Nitrosopyrrolidine | |
U181 | 99-55-8 | 5-Nitro-o-toluidine | |
U193 | 1120-71-4 | 1,2-Oxathiolane, 2,2-dioxide | |
U058 | 50-18-0 | 2H-1,3,2-Oxazaphosphorin-2-amine, N,N-bis(2-chloroethyl)tetrahydro-, 2-oxide | |
U115 | 75-21-8 | Oxirane | (I, T) |
U126 | 765-34-4 | Oxiranecarboxyaldehyde | |
U041 | 106-89-8 | Oxirane, (chloromethyl)- | |
U182 | 123-63-7 | Paraldehyde | |
U183 | 608-93-5 | Pentachlorobenzene | |
U184 | 76-01-7 | Pentachloroethane | |
U185 | 82-68-8 | Pentachloronitrobenzene (PCNB) | |
See F027 | 87-86-5 | Pentachlorophenol | |
U161 | 108-10-1 | Pentanol, 4-methyl- | (I) |
U186 | 504-60-9 | 1,3-Pentadiene | (I) |
U187 | 62-44-2 | Phenacetin | |
U188 | 108-95-2 | Phenol | |
U048 | 95-57-8 | Phenol, 2-chloro- | |
U039 | 59-50-7 | Phenol, 4-chloro-3-methyl- | |
U081 | 120-83-2 | Phenol, 2,4-dichloro- | |
U082 | 87-65-0 | Phenol, 2,6-dichloro- | |
U089 | 56-53-1 | Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-, (E)- | |
U101 | 105-67-9 | Phenol, 2,4-dimethyl- | |
U052 | 1319-77-3 | Phenol, methyl- | |
U132 | 70-30-4 | Phenol, 2,2'-methylenebis(3,4,6-trichloro- | |
U411 | 114-26-1 | Phenol, 2-(1-methylethoxy)-, methylcarbamate | |
U170 | 100-02-7 | Phenol, 4-nitro- | |
See F027 | 87-86-5 | Phenol, pentachloro- | |
See F027 | 58-90-2 | Phenol, 2,3,4,6-tetrachloro- | |
See F027 | 95-95-4 | Phenol, 2,4,5-trichloro- | |
See F027 | 88-06-2 | Phenol, 2,4,6-trichloro- | |
U150 | 148-82-3 | L-Phenylalanine, 4-(bis(2-chloroethyl)amino)- | |
U145 | 7446-27-7 | Phosphoric acid, lead (2+) salt (2:3) | |
U087 | 3288-58-2 | Phosphorodithioic acid, O,O-diethyl S-methyl ester | |
U189 | 1314-80-3 | Phosphorus sulfide | (R) |
U190 | 85-44-9 | Phthalic anhydride | |
U191 | 109-06-8 | 2-Picoline | |
U179 | 100-75-4 | Piperidine, 1-nitroso- | |
U192 | 23950-58-5 | Pronamide | |
U194 | 107-10-8 | 1-Propanamine | (I, T) |
U111 | 621-64-7 | 1-Propanamine, N-nitroso-N-propyl- | |
U110 | 142-84-7 | 1-Propanamine, N-propyl- | (I) |
U066 | 96-12-8 | Propane, 1,2-dibromo-3-chloro- | |
U083 | 78-87-5 | Propane, 1,2-dichloro- | |
U149 | 109-77-3 | Propanedinitrile | |
U171 | 79-46-9 | Propane, 2-nitro- | (I, T) |
U027 | 108-60-1 | Propane, 2,2'-oxybis(2-chloro- | |
See F027 | 93-72-1 | Propanoic acid, 2-(2,4,5-trichlorophenoxy)- | |
U193 | 1120-71-4 | 1,3-Propane sultone | |
U235 | 126-72-7 | 1-Propanol, 2,3-dibromo-, phosphate (3:1) | |
U140 | 78-83-1 | 1-Propanol, 2-methyl- | (I, T) |
U002 | 67-64-1 | 2-Propanone | (I) |
U007 | 79-06-1 | 2-Propenamide | |
U084 | 542-75-6 | 1-Propene, 1,3-dichloro- | |
U243 | 1888-71-7 | 1-Propene, 1,1,2,3,3,3-hexachloro- | |
U009 | 107-13-1 | 2-Propenenitrile | |
U152 | 126-98-7 | 2-Propenenitrile, 2-methyl- | (I, T) |
U008 | 79-10-7 | 2-Propenoic acid | (I) |
U113 | 140-88-5 | 2-Propenoic acid, ethyl ester | (I) |
U118 | 97-63-2 | 2-Propenoic acid, 2-methyl-, ethyl ester | |
U162 | 80-62-6 | 2-Propenoic acid, 2-methyl-, methyl ester | (I, T) |
U373 | 122-42-9 | Propham | |
U411 | 114-26-1 | Propoxur | |
See F027 | 93-72-1 | Propionic acid, 2-(2,4,5-trichlorophenoxy)- | |
U194 | 107-10-8 | n-Propylamine | (I, T) |
U083 | 78-87-5 | Propylene dichloride | |
U387 | 52888-80-9 | Prosulfocarb | |
U148 | 123-33-1 | 3,6-Pyridazinedione, 1,2-dihydro- | |
U196 | 110-86-1 | Pyridine | |
U191 | 109-06-8 | Pyridine, 2-methyl- | |
U237 | 66-75-1 | 2,4-(1H,3H)-Pyrimidinedione, 5-(bis(2-chloroethyl)amino)- | |
U164 | 56-04-2 | 4(1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-thioxo- | |
U180 | 930-55-2 | Pyrrolidine, 1-nitroso- | |
U200 | 50-55-5 | Reserpine | |
U201 | 108-46-3 | Resorcinol | |
U203 | 94-59-7 | Safrole | |
U204 | 7783-00-8 | Selenious acid | |
U204 | 7783-00-8 | Selenium dioxide | |
U205 | 7488-56-4 | Selenium sulfide | (R, T) |
U205 | 7488-56-4 | Selenium sulfide SeS2 | (R, T) |
U015 | 115-02-6 | L-Serine, diazoacetate (ester) | |
See F027 | 93-72-1 | Silvex (2,4,5-TP) | |
U206 | 18883-66-4 | Streptozotocin | |
U103 | 77-78-1 | Sulfuric acid, dimethyl ester | |
U189 | 1314-80-3 | Sulfur phosphide | (R) |
See F027 | 93-76-5 | 2,4,5-T | |
U207 | 95-94-3 | 1,2,4,5-Tetrachlorobenzene | |
U208 | 630-20-6 | 1,1,1,2-Tetrachloroethane | |
U209 | 79-34-5 | 1,1,2,2-Tetrachloroethane | |
U210 | 127-18-4 | Tetrachloroethylene | |
See F027 | 58-90-2 | 2,3,4,6-Tetrachlorophenol | |
U213 | 109-99-9 | Tetrahydrofuran | (I) |
U214 | 563-68-8 | Thallium (I) acetate | |
U215 | 6533-73-9 | Thallium (I) carbonate | |
U216 | 7791-12-0 | Thallium (I) chloride | |
U216 | 7791-12-0 | Thallium chloride TlCl | |
U217 | 10102-45-1 | Thallium (I) nitrate | |
U218 | 62-55-5 | Thioacetamide | |
U410 | 59669-26-0 | Thiodicarb | |
U153 | 74-93-1 | Thiomethanol | (I, T) |
U244 | 137-26-8 | Thioperoxydicarbonic diamide ((H2N)C(S))2S2, tetramethyl- | |
U409 | 23564-05-8 | Thiophanate-methyl | |
U219 | 62-56-6 | Thiourea | |
U244 | 137-26-8 | Thiram | |
U220 | 108-88-3 | Toluene | |
U221 | 25376-45-8 | Toluenediamine | |
U223 | 26471-62-5 | Toluene diisocyanate | (R, T) |
U328 | 95-53-4 | o-Toluidine | |
U353 | 106-49-0 | p-Toluidine | |
U222 | 636-21-5 | o-Toluidine hydrochloride | |
U389 | 2303-17-5 | Triallate | |
U011 | 61-82-5 | 1H-1,2,4-Triazol-3-amine | |
U227 | 79-00-5 | Ethane, 1,1,2-trichloro- | |
U227 | 79-00-5 | 1,1,2-Trichloroethane | |
U228 | 79-01-6 | Trichloroethylene | |
U121 | 75-69-4 | Trichloromonofluoromethane | |
See F027 | 95-95-4 | 2,4,5-Trichlorophenol | |
See F027 | 88-06-2 | 2,4,6-Trichlorophenol | |
U404 | 121-44-8 | Triethylamine | |
U234 | 99-35-4 | 1,3,5-Trinitrobenzene | (R, T) |
U182 | 123-63-7 | 1,3,5-Trioxane, 2,4,6-trimethyl- | |
U235 | 126-72-7 | Tris(2,3-dibromopropyl) phosphate | |
U236 | 72-57-1 | Trypan blue | |
U237 | 66-75-1 | Uracil mustard | |
U176 | 759-73-9 | Urea, N-ethyl-N-nitroso- | |
U177 | 684-93-5 | Urea, N-methyl-N-nitroso- | |
U043 | 75-01-4 | Vinyl chloride | |
U248 | 81-81-2 | Warfarin, and salts, when present at concentrations of 0.3 percent or less | |
U239 | 1330-20-7 | Xylene | (I) |
U200 | 50-55-5 | Yohimban-16-carboxylic acid, 11,17-dimethoxy-18-((3,4,5-trimethoxybenzoyl)oxy)-, methyl ester, (3 b ,16 b ,17 a ,18 b ,20 a )- | |
U249 | 1314-84-7 | Zinc phosphide Zn3P2, when present at concentrations of 10 percent or less |
USEPA Hazardous Waste No. | Chemical Abstracts No. (CAS No.) | Substance | Hazard Code |
U001 | 75-07-0 | Acetaldehyde | (I) |
U001 | 75-07-0 | Ethanal | (I) |
U002 | 67-64-1 | Acetone | (I) |
U002 | 67-64-1 | 2-Propanone | (I) |
U003 | 75-05-8 | Acetonitrile | (I, T) |
U004 | 98-86-2 | Acetophenone | |
U004 | 98-86-2 | Ethanone, 1-phenyl- | |
U005 | 53-96-3 | Acetamide, N-9H-fluoren-2-yl- | |
U005 | 53-96-3 | 2-Acetylaminofluorene | |
U006 | 75-36-5 | Acetyl chloride | (C, R, T) |
U007 | 79-06-1 | Acrylamide | |
U007 | 79-06-1 | 2-Propenamide | |
U008 | 79-10-7 | Acrylic acid | (I) |
U008 | 79-10-7 | 2-Propenoic acid | (I) |
U009 | 107-13-1 | Acrylonitrile | |
U009 | 107-13-1 | 2-Propenenitrile | |
U010 | 50-07-7 | Azirino(2',3':3,4)pyrrolo(1,2-a)indole-4,7-dione, 6-amino-8-(((aminocarbonyl)oxy)methyl)-1,1a,2,8,8a,8b-hexahydro-8a-methoxy-5-methyl-, (1a-S-(1a a ,8 b ,8a a ,8b a ))- | |
U010 | 50-07-7 | Mitomycin C | |
U011 | 61-82-5 | Amitrole | |
U011 | 61-82-5 | 1H-1,2,4-Triazol-3-amine | |
U012 | 62-53-3 | Aniline | (I, T) |
U012 | 62-53-3 | Benzenamine | (I, T) |
U014 | 492-80-8 | Auramine | |
U014 | 492-80-8 | Benzenamine, 4,4'-carbonimidoylbis(N,N-dimethyl- | |
U015 | 115-02-6 | Azaserine | |
U015 | 115-02-6 | L-Serine, diazoacetate (ester) | |
U016 | 225-51-4 | Benz(c)acridine | |
U017 | 98-87-3 | Benzal chloride | |
U017 | 98-87-3 | Benzene, (dichloromethyl)- | |
U018 | 56-55-3 | Benz(a)anthracene | |
U019 | 71-43-2 | Benzene | (I, T) |
U020 | 98-09-9 | Benzenesulfonic acid chloride | (C, R) |
U020 | 98-09-9 | Benzenesulfonyl chloride | (C, R) |
U021 | 92-87-5 | Benzidene | |
U021 | 92-87-5 | (1,1'-Biphenyl)-4,4'-diamine | |
U022 | 50-32-8 | Benzo(a)pyrene | |
U023 | 98-07-7 | Benzene, (trichloromethyl)- | (C, R, T) |
U023 | 98-07-7 | Benzotrichloride | (C, R, T) |
U024 | 111-91-1 | Dichloromethoxy ethane | |
U024 | 111-91-1 | Ethane, 1,1'-(methylenebis(oxy))bis(2-chloro- | |
U025 | 111-44-4 | Dichloroethyl ether | |
U025 | 111-44-4 | Ethane, 1,1'-oxybis(2-chloro- | |
U026 | 494-03-1 | Chlornaphazin | |
U026 | 494-03-1 | Naphthaleneamine, N,N'-bis(2-chloroethyl)- | |
U027 | 108-60-1 | Dichloroisopropyl ether | |
U027 | 108-60-1 | Propane, 2,2'-oxybis(2-chloro- | |
U028 | 117-81-7 | 1,2-Benzenedicarboxylic acid, bis(2-ethylhexyl) ester | |
U028 | 117-81-7 | Diethylhexyl phthalate | |
U029 | 74-83-9 | Methane, bromo- | |
U029 | 74-83-9 | Methyl bromide | |
U030 | 101-55-3 | Benzene, 1-bromo-4-phenoxy- | |
U030 | 101-55-3 | 4-Bromophenyl phenyl ether | |
U031 | 71-36-3 | 1-Butanol | (I) |
U031 | 71-36-3 | n-Butyl alcohol | (I) |
U032 | 13765-19-0 | Calcium chromate | |
U032 | 13765-19-0 | Chromic acid H2CrO4, calcium salt | |
U033 | 353-50-4 | Carbonic difluoride | (R, T) |
U033 | 353-50-4 | Carbon oxyfluoride | (R, T) |
U034 | 75-87-6 | Acetaldehyde, trichloro- | |
U034 | 75-87-6 | Chloral | |
U035 | 305-03-3 | Benzenebutanoic acid, 4-(bis(2-chloroethyl)amino)- | |
U035 | 305-03-3 | Chlorambucil | |
U036 | 57-74-9 | Chlordane, a and g isomers | |
U036 | 57-74-9 | 4,7-Methano-1H-indene, 1,2,4,5,6,7,8,8-octachloro-2,3,3a,4,7,7a-hexahydro- | |
U037 | 108-90-7 | Benzene, chloro- | |
U037 | 108-90-7 | Chlorobenzene | |
U038 | 510-15-6 | Benzeneacetic acid, 4-chloro- a -(4-chlorophenyl)- a -hydroxy-, ethyl ester | |
U038 | 510-15-6 | Chlorobenzilate | |
U039 | 59-50-7 | p-Chloro-m-cresol | |
U039 | 59-50-7 | Phenol, 4-chloro-3-methyl- | |
U041 | 106-89-8 | Epichlorohydrin | |
U041 | 106-89-8 | Oxirane, (chloromethyl)- | |
U042 | 110-75-8 | 2-Chloroethyl vinyl ether | |
U042 | 110-75-8 | Ethene, (2-chloroethoxy)- | |
U043 | 75-01-4 | Ethene, chloro- | |
U043 | 75-01-4 | Vinyl chloride | |
U044 | 67-66-3 | Chloroform | |
U044 | 67-66-3 | Methane, trichloro- | |
U045 | 74-87-3 | Methane, chloro- | (I, T) |
U045 | 74-87-3 | Methyl chloride | (I, T) |
U046 | 107-30-2 | Chloromethyl methyl ether | |
U046 | 107-30-2 | Methane, chloromethoxy- | |
U047 | 91-58-7 | b -Chloronaphthalene | |
U047 | 91-58-7 | Naphthalene, 2-chloro- | |
U048 | 95-57-8 | o-Chlorophenol | |
U048 | 95-57-8 | Phenol, 2-chloro- | |
U049 | 3165-93-3 | Benzenamine, 4-chloro-2-methyl-, hydrochloride | |
U049 | 3165-93-3 | 4-Chloro-o-toluidine, hydrochloride | |
U050 | 218-01-9 | Chrysene | |
U051 | Creosote | ||
U052 | 1319-77-3 | Cresol (Cresylic acid) | |
U052 | 1319-77-3 | Phenol, methyl- | |
U053 | 4170-30-3 | 2-Butenal | |
U053 | 4170-30-3 | Crotonaldehyde | |
U055 | 98-82-8 | Benzene, (1-methylethyl)- | (I) |
U055 | 98-82-8 | Cumene | (I) |
U056 | 110-82-7 | Benzene, hexahydro- | (I) |
U056 | 110-82-7 | Cyclohexane | (I) |
U057 | 108-94-1 | Cyclohexanone | (I) |
U058 | 50-18-0 | Cyclophosphamide | |
U058 | 50-18-0 | 2H-1,3,2-Oxazaphosphorin-2-amine, N,N-bis(2-chloroethyl)tetrahydro-, 2-oxide | |
U059 | 20830-81-3 | Daunomycin | |
U059 | 20830-81-3 | 5,12-Naphthacenedione, 8-acetyl-10-((3-amino-2,3,6-trideoxy)- a -L-lyxo-hexapyranosyl)oxyl)-7,8,9,10-tetrahydro-6,8,11-trihydroxy-1-methoxy-, (8S-cis)- | |
U060 | 72-54-8 | Benzene, 1,1'-(2,2-dichloroethylidene)bis(4-chloro- | |
U060 | 72-54-8 | DDD | |
U061 | 50-29-3 | Benzene, 1,1'-(2,2,2-trichloroethylidene)bis(4-chloro- | |
U061 | 50-29-3 | DDT | |
U062 | 2303-16-4 | Carbamothioic acid, bis(1-methylethyl)-, S-(2,3-dichloro-2-propenyl) ester | |
U062 | 2303-16-4 | Diallate | |
U063 | 53-70-3 | Dibenz(a,h)anthracene | |
U064 | 189-55-9 | Benzo(rst)pentaphene | |
U064 | 189-55-9 | Dibenzo(a,i)pyrene | |
U066 | 96-12-8 | 1,2-Dibromo-3-chloropropane | |
U066 | 96-12-8 | Propane, 1,2-dibromo-3-chloro- | |
U067 | 106-93-4 | Ethane, 1,2-dibromo- | |
U067 | 106-93-4 | Ethylene dibromide | |
U068 | 74-95-3 | Methane, dibromo- | |
U068 | 74-95-3 | Methylene bromide | |
U069 | 84-74-2 | 1,2-Benzenedicarboxylic acid, dibutyl ester | |
U069 | 84-74-2 | Dibutyl phthalate | |
U070 | 95-50-1 | Benzene, 1,2-dichloro- | |
U070 | 95-50-1 | o-Dichlorobenzene | |
U071 | 541-73-1 | Benzene, 1,3-dichloro- | |
U071 | 541-73-1 | m-Dichlorobenzene | |
U072 | 106-46-7 | Benzene, 1,4-dichloro- | |
U072 | 106-46-7 | p-Dichlorobenzene | |
U073 | 91-94-1 | (1,1'-Biphenyl)-4,4'-diamine, 3,3'-dichloro- | |
U073 | 91-94-1 | 3,3'-Dichlorobenzidine | |
U074 | 764-41-0 | 2-Butene, 1,4-dichloro- | (I, T) |
U074 | 764-41-0 | 1,4-Dichloro-2-butene | (I, T) |
U075 | 75-71-8 | Dichlorodifluoromethane | |
U075 | 75-71-8 | Methane, dichlorodifluoro- | |
U076 | 75-34-3 | Ethane, 1,1-dichloro- | |
U076 | 75-34-3 | Ethylidene dichloride | |
U077 | 107-06-2 | Ethane, 1,2-dichloro- | |
U077 | 107-06-2 | Ethylene dichloride | |
U078 | 75-35-4 | 1,1-Dichloroethylene | |
U078 | 75-35-4 | Ethene, 1,1-dichloro- | |
U079 | 156-60-5 | 1,2-Dichloroethylene | |
U079 | 156-60-5 | Ethene, 1,2-dichloro-, (E)- | |
U080 | 75-09-2 | Methane, dichloro- | |
U080 | 75-09-2 | Methylene chloride | |
U081 | 120-83-2 | 2,4-Dichlorophenol | |
U081 | 120-83-2 | Phenol, 2,4-dichloro- | |
U082 | 87-65-0 | 2,6-Dichlorophenol | |
U082 | 87-65-0 | Phenol, 2,6-dichloro- | |
U083 | 78-87-5 | Propane, 1,2-dichloro- | |
U083 | 78-87-5 | Propylene dichloride | |
U084 | 542-75-6 | 1,3-Dichloropropene | |
U084 | 542-75-6 | 1-Propene, 1,3-dichloro- | |
U085 | 1464-53-5 | 2,2'-Bioxirane | (I, T) |
U085 | 1464-53-5 | 1,2:3,4-Diepoxybutane | (I, T) |
U086 | 1615-80-1 | N,N'-Diethylhydrazine | |
U086 | 1615-80-1 | Hydrazine, 1,2-diethyl- | |
U087 | 3288-58-2 | O,O-Diethyl S-methyl dithiophosphate | |
U087 | 3288-58-2 | Phosphorodithioic acid, O,O-diethyl S-methyl ester | |
U088 | 84-66-2 | 1,2-Benzenedicarboxylic acid, diethyl ester | |
U088 | 84-66-2 | Diethyl phthalate | |
U089 | 56-53-1 | Diethylstilbestrol | |
U089 | 56-53-1 | Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-, (E)- | |
U090 | 94-58-6 | 1,3-Benzodioxole, 5-propyl- | |
U090 | 94-58-6 | Dihydrosafrole | |
U091 | 119-90-4 | (1,1'-Biphenyl)-4,4'-diamine, 3,3'-dimethoxy- | |
U091 | 119-90-4 | 3,3'-Dimethoxybenzidine | |
U092 | 124-40-3 | Dimethylamine | (I) |
U092 | 124-40-3 | Methanamine, N-methyl- | (I) |
U093 | 60-11-7 | Benzenamine, N,N-dimethyl-4-(phenylazo)- | |
U093 | 60-11-7 | p-Dimethylaminoazobenzene | |
U094 | 57-97-6 | Benz(a)anthracene, 7,12-dimethyl- | |
U094 | 57-97-6 | 7,12-Dimethylbenz(a)anthracene | |
U095 | 119-93-7 | (1,1'-Biphenyl)-4,4'-diamine, 3,3'-dimethyl- | |
U095 | 119-93-7 | 3,3'-Dimethylbenzidine | |
U096 | 80-15-9 | a , a -Dimethylbenzylhydroperoxide | (R) |
U096 | 80-15-9 | Hydroperoxide, 1-methyl-1-phenylethyl- | (R) |
U097 | 79-44-7 | Carbamic chloride, dimethyl- | |
U097 | 79-44-7 | Dimethylcarbamoyl chloride | |
U098 | 57-14-7 | 1,1-Dimethylhydrazine | |
U098 | 57-14-7 | Hydrazine, 1,1-dimethyl- | |
U099 | 540-73-8 | 1,2-Dimethylhydrazine | |
U099 | 540-73-8 | Hydrazine, 1,2-dimethyl- | |
U101 | 105-67-9 | 2,4-Dimethylphenol | |
U101 | 105-67-9 | Phenol, 2,4-dimethyl- | |
U102 | 131-11-3 | 1,2-Benzenedicarboxylic acid, dimethyl ester | |
U102 | 131-11-3 | Dimethyl phthalate | |
U103 | 77-78-1 | Dimethyl sulfate | |
U103 | 77-78-1 | Sulfuric acid, dimethyl ester | |
U105 | 121-14-2 | Benzene, 1-methyl-2,4-dinitro- | |
U105 | 121-14-2 | 2,4-Dinitrotoluene | |
U106 | 606-20-2 | Benzene, 2-methyl-1,3-dinitro- | |
U106 | 606-20-2 | 2,6-Dinitrotoluene | |
U107 | 117-84-0 | 1,2-Benzenedicarboxylic acid, dioctyl ester | |
U107 | 117-84-0 | Di-n-octyl phthalate | |
U108 | 123-91-1 | 1,4-Diethyleneoxide | |
U108 | 123-91-1 | 1,4-Dioxane | |
U109 | 122-66-7 | 1,2-Diphenylhydrazine | |
U109 | 122-66-7 | Hydrazine, 1,2-diphenyl- | |
U110 | 142-84-7 | Dipropylamine | (I) |
U110 | 142-84-7 | 1-Propanamine, N-propyl- | (I) |
U111 | 621-64-7 | Di-n-propylnitrosamine | |
U111 | 621-64-7 | 1-Propanamine, N-nitroso-N-propyl- | |
U112 | 141-78-6 | Acetic acid, ethyl ester | (I) |
U112 | 141-78-6 | Ethyl acetate | (I) |
U113 | 140-88-5 | Ethyl acrylate | (I) |
U113 | 140-88-5 | 2-Propenoic acid, ethyl ester | (I) |
U114 | P 111-54-6 | Carbamodithioic acid, 1,2-ethanediylbis-, salts and esters | |
U114 | P 111-54-6 | Ethylenebisdithiocarbamic acid, salts and esters | |
U115 | 75-21-8 | Ethylene oxide | (I, T) |
U115 | 75-21-8 | Oxirane | (I, T) |
U116 | 96-45-7 | Ethylenethiourea | |
U116 | 96-45-7 | 2-Imidazolidinethione | |
U117 | 60-29-7 | Ethane, 1,1'-oxybis- | (I) |
U117 | 60-29-7 | Ethyl ether | (I) |
U118 | 97-63-2 | Ethyl methacrylate | |
U118 | 97-63-2 | 2-Propenoic acid, 2-methyl-, ethyl ester | |
U119 | 62-50-0 | Ethyl methanesulfonate | |
U119 | 62-50-0 | Methanesulfonic acid, ethyl ester | |
U120 | 206-44-0 | Fluoranthene | |
U121 | 75-69-4 | Methane, trichlorofluoro- | |
U121 | 75-69-4 | Trichloromonofluoromethane | |
U122 | 50-00-0 | Formaldehyde | |
U123 | 64-18-6 | Formic acid | (C, T) |
U124 | 110-00-9 | Furan | (I) |
U124 | 110-00-9 | Furfuran | (I) |
U125 | 98-01-1 | 2-Furancarboxaldehyde | (I) |
U125 | 98-01-1 | Furfural | (I) |
U126 | 765-34-4 | Glycidylaldehyde | |
U126 | 765-34-4 | Oxiranecarboxyaldehyde | |
U127 | 118-74-1 | Benzene, hexachloro- | |
U127 | 118-74-1 | Hexachlorobenzene | |
U128 | 87-68-3 | 1,3-Butadiene, 1,1,2,3,4,4-hexachloro- | |
U128 | 87-68-3 | Hexachlorobutadiene | |
U129 | 58-89-9 | Cyclohexane, 1,2,3,4,5,6-hexachloro-, (1 a ,2 a ,3 b ,4 a ,5 a ,6 b )- | |
U129 | 58-89-9 | Lindane | |
U130 | 77-47-4 | 1,3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro- | |
U130 | 77-47-4 | Hexachlorocyclopentadiene | |
U131 | 67-72-1 | Ethane, hexachloro- | |
U131 | 67-72-1 | Hexachloroethane | |
U132 | 70-30-4 | Hexachlorophene | |
U132 | 70-30-4 | Phenol, 2,2'-methylenebis(3,4,6-trichloro- | |
U133 | 302-01-2 | Hydrazine | (R, T) |
U134 | 7664-39-3 | Hydrofluoric acid | (C, T) |
U134 | 7664-39-3 | Hydrogen fluoride | (C, T) |
U135 | 7783-06-4 | Hydrogen sulfide | |
U135 | 7783-06-4 | Hydrogen sulfide H2S | |
U136 | 75-60-5 | Arsinic acid, dimethyl- | |
U136 | 75-60-5 | Cacodylic acid | |
U137 | 193-39-5 | Indeno(1,2,3-cd)pyrene | |
U138 | 74-88-4 | Methane, iodo- | |
U138 | 74-88-4 | Methyl iodide | |
U140 | 78-83-1 | Isobutyl alcohol | (I, T) |
U140 | 78-83-1 | 1-Propanol, 2-methyl- | (I, T) |
U141 | 120-58-1 | 1,3-Benzodioxole, 5-(1-propenyl)- | |
U141 | 120-58-1 | Isosafrole | |
U142 | 143-50-0 | Kepone | |
U142 | 143-50-0 | 1,3,4-Metheno-2H-cyclobuta(cd)pentalen-2-one, 1,1a,3,3a,4,5,5,5a,5b,6-decachlorooctahydro- | |
U143 | 303-34-4 | 2-Butenoic acid, 2-methyl-, 7-((2,3-dihydroxy-2-(1-methoxyethyl)-3-methyl-1-oxobutoxy)methyl)-2,3,5,7a-tetrahydro-1H-pyrrolizin-1-yl ester, (1S-(1 a (Z), 7(2S*,3R*), 7a a ))- | |
U143 | 303-34-4 | Lasiocarpene | |
U144 | 301-04-2 | Acetic acid, lead (2+) salt | |
U144 | 301-04-2 | Lead acetate | |
U145 | 7446-27-7 | Lead phosphate | |
U145 | 7446-27-7 | Phosphoric acid, lead (2+) salt (2:3) | |
U146 | 1335-32-6 | Lead, bis(acetato-O)tetrahydroxytri- | |
U146 | 1335-32-6 | Lead subacetate | |
U147 | 108-31-6 | 2,5-Furandione | |
U147 | 108-31-6 | Maleic anhydride | |
U148 | 123-33-1 | Maleic hydrazide | |
U148 | 123-33-1 | 3,6-Pyridazinedione, 1,2-dihydro- | |
U149 | 109-77-3 | Malononitrile | |
U149 | 109-77-3 | Propanedinitrile | |
U150 | 148-82-3 | Melphalan | |
U150 | 148-82-3 | L-Phenylalanine, 4-(bis(2-chloroethyl)amino)- | |
U151 | 7439-97-6 | Mercury | |
U152 | 126-98-7 | Methacrylonitrile | (I, T) |
U152 | 126-98-7 | 2-Propenenitrile, 2-methyl- | (I, T) |
U153 | 74-93-1 | Methanethiol | (I, T) |
U153 | 74-93-1 | Thiomethanol | (I, T) |
U154 | 67-56-1 | Methanol | (I) |
U154 | 67-56-1 | Methyl alcohol | (I) |
U155 | 91-80-5 | 1,2-Ethanediamine, N,N-dimethyl-N'-2-pyridinyl-N'-(2-thienylmethyl)- | |
U155 | 91-80-5 | Methapyrilene | |
U156 | 79-22-1 | Carbonochloridic acid, methyl ester | (I, T) |
U156 | 79-22-1 | Methyl chlorocarbonate | (I, T) |
U157 | 56-49-5 | Benz(j)aceanthrylene, 1,2-dihydro-3-methyl- | |
U157 | 56-49-5 | 3-Methylcholanthrene | |
U158 | 101-14-4 | Benzenamine, 4,4'-methylenebis(2-chloro- | |
U158 | 101-14-4 | 4,4'-Methylenebis(2-chloroaniline) | |
U159 | 78-93-3 | 2-Butanone | (I, T) |
U159 | 78-93-3 | Methyl ethyl ketone (MEK) | (I, T) |
U160 | 1338-23-4 | 2-Butanone, peroxide | (R, T) |
U160 | 1338-23-4 | Methyl ethyl ketone peroxide | (R, T) |
U161 | 108-10-1 | Methyl isobutyl ketone | (I) |
U161 | 108-10-1 | 4-Methyl-2-pentanone | (I) |
U161 | 108-10-1 | Pentanol, 4-methyl- | (I) |
U162 | 80-62-6 | Methyl methacrylate | (I, T) |
U162 | 80-62-6 | 2-Propenoic acid, 2-methyl-, methyl ester | (I, T) |
U163 | 70-25-7 | Guanidine, N-methyl-N’-nitro-N-nitroso- | |
U163 | 70-25-7 | MNNG | |
U164 | 56-04-2 | Methylthiouracil | |
U164 | 56-04-2 | 4(1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-thioxo- | |
U165 | 91-20-3 | Naphthalene | |
U166 | 130-15-4 | 1,4-Naphthalenedione | |
U166 | 130-15-4 | 1,4-Naphthoquinone | |
U167 | 134-32-7 | 1-Naphthalenamine | |
U167 | 134-32-7 | a -Naphthylamine | |
U168 | 91-59-8 | 2-Naphthalenamine | |
U168 | 91-59-8 | b -Naphthylamine | |
U169 | 98-95-3 | Benzene, nitro- | (I, T) |
U169 | 98-95-3 | Nitrobenzene | (I, T) |
U170 | 100-02-7 | p-Nitrophenol | |
U170 | 100-02-7 | Phenol, 4-nitro- | |
U171 | 79-46-9 | 2-Nitropropane | (I, T) |
U171 | 79-46-9 | Propane, 2-nitro- | (I, T) |
U172 | 924-16-3 | 1-Butanamine, N-butyl-N-nitroso- | |
U172 | 924-16-3 | N-Nitrosodi-n-butylamine | |
U173 | 1116-54-7 | Ethanol, 2,2'-(nitrosoimino)bis- | |
U173 | 1116-54-7 | N-Nitrosodiethanolamine | |
U174 | 55-18-5 | Ethanamine, N-ethyl-N-nitroso- | |
U174 | 55-18-5 | N-Nitrosodiethylamine | |
U176 | 759-73-9 | N-Nitroso-N-ethylurea | |
U176 | 759-73-9 | Urea, N-ethyl-N-nitroso- | |
U177 | 684-93-5 | N-Nitroso-N-methylurea | |
U177 | 684-93-5 | Urea, N-methyl-N-nitroso- | |
U178 | 615-53-2 | Carbamic acid, methylnitroso-, ethyl ester | |
U178 | 615-53-2 | N-Nitroso-N-methylurethane | |
U179 | 100-75-4 | N-Nitrosopiperidine | |
U179 | 100-75-4 | Piperidine, 1-nitroso- | |
U180 | 930-55-2 | N-Nitrosopyrrolidine | |
U180 | 930-55-2 | Pyrrolidine, 1-nitroso- | |
U181 | 99-55-8 | Benzenamine, 2-methyl-5-nitro- | |
U181 | 99-55-8 | 5-Nitro-o-toluidine | |
U182 | 123-63-7 | Paraldehyde | |
U182 | 123-63-7 | 1,3,5-Trioxane, 2,4,6-trimethyl- | |
U183 | 608-93-5 | Benzene, pentachloro- | |
U183 | 608-93-5 | Pentachlorobenzene | |
U184 | 76-01-7 | Ethane, pentachloro- | |
U184 | 76-01-7 | Pentachloroethane | |
U185 | 82-68-8 | Benzene, pentachloronitro- | |
U185 | 82-68-8 | Pentachloronitrobenzene (PCNB) | |
U186 | 504-60-9 | 1-Methylbutadiene | (I) |
U186 | 504-60-9 | 1,3-Pentadiene | (I) |
U187 | 62-44-2 | Acetamide, N-(4-ethoxyphenyl)- | |
U187 | 62-44-2 | Phenacetin | |
U188 | 108-95-2 | Phenol | |
U189 | 1314-80-3 | Phosphorus sulfide | (R) |
U189 | 1314-80-3 | Sulfur phosphide | (R) |
U190 | 85-44-9 | 1,3-Isobenzofurandione | |
U190 | 85-44-9 | Phthalic anhydride | |
U191 | 109-06-8 | 2-Picoline | |
U191 | 109-06-8 | Pyridine, 2-methyl- | |
U192 | 23950-58-5 | Benzamide, 3,5-dichloro-N-(1,1-dimethyl-2-propynyl)- | |
U192 | 23950-58-5 | Pronamide | |
U193 | 1120-71-4 | 1,2-Oxathiolane, 2,2-dioxide | |
U193 | 1120-71-4 | 1,3-Propane sultone | |
U194 | 107-10-8 | 1-Propanamine | (I, T) |
U194 | 107-10-8 | n-Propylamine | (I, T) |
U196 | 110-86-1 | Pyridine | |
U197 | 106-51-4 | p-Benzoquinone | |
U197 | 106-51-4 | 2,5-Cyclohexadiene-1,4-dione | |
U200 | 50-55-5 | Reserpine | |
U200 | 50-55-5 | Yohimban-16-carboxylic acid, 11,17-dimethoxy-18-((3,4,5-trimethoxybenzoyl)oxy)-, methyl ester, (3 b ,16 b ,17 a ,18 b ,20 a )- | |
U201 | 108-46-3 | 1,3-Benzenediol | |
U201 | 108-46-3 | Resorcinol | |
U203 | 94-59-7 | 1,3-Benzodioxole, 5-(2-propenyl)- | |
U203 | 94-59-7 | Safrole | |
U204 | 7783-00-8 | Selenious acid | |
U204 | 7783-00-8 | Selenium dioxide | |
U205 | 7488-56-4 | Selenium sulfide | (R, T) |
U205 | 7488-56-4 | Selenium sulfide SeS2 | (R, T) |
U206 | 18883-66-4 | Glucopyranose, 2-deoxy-2-(3-methyl-3-nitrosoureido)-, D- | |
U206 | 18883-66-4 | D-Glucose, 2-deoxy-2-(((methylnitrosoamino)-carbonyl)amino)- | |
U206 | 18883-66-4 | Streptozotocin | |
U207 | 95-94-3 | Benzene, 1,2,4,5-tetrachloro- | |
U207 | 95-94-3 | 1,2,4,5-Tetrachlorobenzene | |
U208 | 630-20-6 | Ethane, 1,1,1,2-tetrachloro- | |
U208 | 630-20-6 | 1,1,1,2-Tetrachloroethane | |
U209 | 79-34-5 | Ethane, 1,1,2,2-tetrachloro- | |
U209 | 79-34-5 | 1,1,2,2-Tetrachloroethane | |
U210 | 127-18-4 | Ethene, tetrachloro- | |
U210 | 127-18-4 | Tetrachloroethylene | |
U211 | 56-23-5 | Carbon tetrachloride | |
U211 | 56-23-5 | Methane, tetrachloro- | |
U213 | 109-99-9 | Furan, tetrahydro- | (I) |
U213 | 109-99-9 | Tetrahydrofuran | (I) |
U214 | 563-68-8 | Acetic acid, thallium (1+) salt | |
U214 | 563-68-8 | Thallium (I) acetate | |
U215 | 6533-73-9 | Carbonic acid, dithallium (1+) salt | |
U215 | 6533-73-9 | Thallium (I) carbonate | |
U216 | 7791-12-0 | Thallium (I) chloride | |
U216 | 7791-12-0 | Thallium chloride TlCl | |
U217 | 10102-45-1 | Nitric acid, thallium (1+) salt | |
U217 | 10102-45-1 | Thallium (I) nitrate | |
U218 | 62-55-5 | Ethanethioamide | |
U218 | 62-55-5 | Thioacetamide | |
U219 | 62-56-6 | Thiourea | |
U220 | 108-88-3 | Benzene, methyl- | |
U220 | 108-88-3 | Toluene | |
U221 | 25376-45-8 | Benzenediamine, ar-methyl- | |
U221 | 25376-45-8 | Toluenediamine | |
U222 | 636-21-5 | Benzenamine, 2-methyl-, hydrochloride | |
U222 | 636-21-5 | o-Toluidine hydrochloride | |
U223 | 26471-62-5 | Benzene, 1,3-diisocyanatomethyl- | (R, T) |
U223 | 26471-62-5 | Toluene diisocyanate | (R, T) |
U225 | 75-25-2 | Bromoform | |
U225 | 75-25-2 | Methane, tribromo- | |
U226 | 71-55-6 | Ethane, 1,1,1-trichloro- | |
U226 | 71-55-6 | Methylchloroform | |
U227 | 79-00-5 | Ethane, 1,1,2-trichloro- | |
U227 | 79-00-5 | 1,1,2-Trichloroethane | |
U228 | 79-01-6 | Ethene, trichloro- | |
U228 | 79-01-6 | Trichloroethylene | |
U234 | 99-35-4 | Benzene, 1,3,5-trinitro- | (R, T) |
U234 | 99-35-4 | 1,3,5-Trinitrobenzene | (R, T) |
U235 | 126-72-7 | 1-Propanol, 2,3-dibromo-, phosphate (3:1) | |
U235 | 126-72-7 | Tris(2,3-dibromopropyl) phosphate | |
U236 | 72-57-1 | 2,7-Naphthalenedisulfonic acid, 3,3'-((3,3'-dimethyl-(1,1'-biphenyl)-4,4'-diyl)bis(azo)bis(5-amino-4-hydroxy)-, tetrasodium salt | |
U236 | 72-57-1 | Trypan blue | |
U237 | 66-75-1 | 2,4-(1H,3H)-Pyrimidinedione, 5-(bis(2-chloroethyl)amino)- | |
U237 | 66-75-1 | Uracil mustard | |
U238 | 51-79-6 | Carbamic acid, ethyl ester | |
U238 | 51-79-6 | Ethyl carbamate (urethane) | |
U239 | 1330-20-7 | Benzene, dimethyl- | (I, T) |
U239 | 1330-20-7 | Xylene | (I, T) |
U240 | P 94-75-7 | Acetic acid, (2,4-dichlorophenoxy)-, salts and esters | |
U240 | P 94-75-7 | 2,4-D, salts and esters | |
U243 | 1888-71-7 | Hexachloropropene | |
U243 | 1888-71-7 | 1-Propene, 1,1,2,3,3,3-hexachloro- | |
U244 | 137-26-8 | Thioperoxydicarbonic diamide ((H2N)C(S))2S2, tetramethyl- | |
U244 | 137-26-8 | Thiram | |
U246 | 506-68-3 | Cyanogen bromide CNBr | |
U247 | 72-43-5 | Benzene, 1,1'-(2,2,2-trichloroethylidene)bis(4-methoxy- | |
U247 | 72-43-5 | Methoxychlor | |
U248 | 81-81-2 | 2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, and salts, when present at concentrations of 0.3 percent or less | |
U248 | 81-81-2 | Warfarin, and salts, when present at concentrations of 0.3 percent or less | |
U249 | 1314-84-7 | Zinc phosphide Zn3P2, when present at concentrations of 10 percent or less | |
U271 | 17804-35-2 | Benomyl | |
U271 | 17804-35-2 | Carbamic acid, (1-((butylamino)carbonyl)-1H-benzimidazol-2-yl)-, methyl ester | |
U278 | 22781-23-3 | Bendiocarb | |
U278 | 22781-23-3 | 1,3-Benzodioxol-4-ol, 2,2-dimethyl-, methyl carbamate | |
U279 | 63-25-2 | Carbaryl | |
U279 | 63-25-2 | 1-Naphthalenol, methylcarbamate | |
U280 | 101-27-9 | Barban | |
U280 | 101-27-9 | Carbamic acid, (3-chlorophenyl)-, 4-chloro-2-butynyl ester | |
U328 | 95-53-4 | Benzenamine, 2-methyl- | |
U328 | 95-53-4 | o-Toluidine | |
U353 | 106-49-0 | Benzenamine, 4-methyl- | |
U353 | 106-49-0 | p-Toluidine | |
U359 | 110-80-5 | Ethanol, 2-ethoxy- | |
U359 | 110-80-5 | Ethylene glycol monoethyl ether | |
U364 | 22961-82-6 | Bendiocarb phenol | |
U364 | 22961-82-6 | 1,3-Benzodioxol-4-ol, 2,2-dimethyl- | |
U367 | 1563-38-8 | 7-Benzofuranol, 2,3-dihydro-2,2-dimethyl- | |
U367 | 1563-38-8 | Carbofuran phenol | |
U372 | 10605-21-7 | Carbamic acid, 1H-benzimidazol-2-yl, methyl ester | |
U372 | 10605-21-7 | Carbendazim | |
U373 | 122-42-9 | Carbamic acid, phenyl-, 1-methylethyl ester | |
U373 | 122-42-9 | Propham | |
U387 | 52888-80-9 | Carbamothioic acid, dipropyl-, S-(phenylmethyl) ester | |
U387 | 52888-80-9 | Prosulfocarb | |
U389 | 2303-17-5 | Carbamothioic acid, bis(1-methylethyl)-, S-(2,3,3-trichloro-2-propenyl) ester | |
U389 | 2303-17-5 | Triallate | |
U394 | 30558-43-1 | A2213 | |
U394 | 30558-43-1 | Ethanimidothioic acid, 2-(dimethylamino)-N-hydroxy-2-oxo-, methyl ester | |
U395 | 5952-26-1 | Diethylene glycol, dicarbamate | |
U395 | 5952-26-1 | Ethanol, 2,2'-oxybis-, dicarbamate | |
U404 | 121-44-8 | Ethanamine, N,N-diethyl- | |
U404 | 121-44-8 | Triethylamine | |
U409 | 23564-05-8 | Carbamic acid, (1,2-phenylenebis(iminocarbonothioyl))bis-, dimethyl ester | |
U409 | 23564-05-8 | Thiophanate-methyl | |
U410 | 59669-26-0 | Ethanimidothioic acid, N,N'- (thiobis((methylimino)carbonyloxy))bis-, dimethyl ester | |
U410 | 59669-26-0 | Thiodicarb | |
U411 | 114-26-1 | Phenol, 2-(1-methylethoxy)-, methylcarbamate | |
U411 | 114-26-1 | Propoxur |
USEPA hazardous waste No. | Hazardous constituents for which listed |
F001 | Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, carbon tetrachloride, chlorinated fluorocarbons. |
F002 | Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, 1,1,2-trichlorethane, chlorobenzene, 1,1,2-trichloro-1,2,2-trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane. |
F003 | N.A. |
F004 | Cresols and cresylic acid, nitrobenzene. |
F005 | Toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, 2-ethoxyethanol, benzene, 2-nitropropane. |
F006 | Cadmium, hexavalent chromium, nickel, cyanide (complexed). |
F007 | Cyanide (salts). |
F008 | Cyanide (salts). |
F009 | Cyanide (salts). |
F010 | Cyanide (salts). |
F011 | Cyanide (salts). |
F012 | Cyanide (complexed). |
F019 | Hexavalent chromium, cyanide (complexed). |
F020 | Tetra- and pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans; tri- and tetrachlorophenols and their clorophenoxy derivative acids, esters, ethers, amines, and other salts. |
F021 | Penta- and hexachlorodibenzo-p-dioxins; penta- and hexachlorodibenzofurans; pentachlorophenol and its derivatives. |
F022 | Tetra-, penta- and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans. |
F023 | Tetra- and pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans; tri- and tetra- chlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines, and other salts. |
F024 | Chloromethane, dichloromethane, trichloromethane, carbon tetrachloride, chloroethylene, 1,1-dichloroethane, 1,2-dichloroethane, trans-1,2-dichloroethylene, 1,1-dichloroethylene, 1,1,1-trichloroethane, 1,1,2-trichloroethane, trichloroethylene, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane, tetrachloroethylene, pentachloroethane, hexachloroethane, allyl chloride (3-chloropropene), dichloropropane, dichloropropene, 2-chloro-1,3-butadiene, hexachloro-1,3-butadiene, hexachlorochylopentadiene, hexachlorocylohexane, benzene, chlorobenzene, dichlorobenzenes, 1,2,4-trichlorobenzene, tetrachlorobenzenes, pentachlorobenzene, hexachlorobenzene, toluene, naphthalene. |
F025 | Chloromethane, dicloromethane, trichloromethane; carbon tetrachloride; chloroethylene; 1,1-dichloroethane; 1,2-dichloroethane; trans-1,2-dichloroethylene; 1,1-dichloroethylene; 1,1,1-trichloroethane; 1,1,2-trichloroethane; trichloroethylene; 1,1,1,2-tetrachloroethane; 1,1,2,2-tetrachloroethane; tetrachloroethylene; pentachloroethane; hexachloroethane; allyl chloride (3-chloropropene); dichloropropane; dichloropropene; 2-chloro-1,3-butadiene; hexachloro-1,3-butadiene; hexachlorocyclopentadiene; benzene; chlorobenzene; dichlorobenzene; 1,2,4-trichlorobenzene; tetrachlorobenzene; pentachlorobenzene; hexachlorobenzene; toluene; naphthalene. |
F026 | Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans. |
F027 | Tetra-, penta, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans; tri-, tetra-, and pentachlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines, and other salts. |
F028 | Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans; tri-, tetra-, and pentachlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines, and other salts. |
F032 | Benz(a)anthracene; benzo(a)pyrene; dibenz(a,h)anthracene; indeno(1,2,3-cd)pyrene; pentachlorophenol; arsenic; chromium; tetra-, penta-, hexa-, and heptachlorordibenzo-p-dioxins; tetra-, penta-, hexa-, and heptachlorodibenzofurans. |
F034 | Benz(a)anthracene, benzo(k)fluoranthene, benzo(a)pyrene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene, naphthalene, arsenic, chromium. |
F035 | Arsenic, chromium, lead. |
F037 | Benzene, benzo(a)pyrene, chrysene, lead, chromium. |
F038 | Benzene, benzo(a)pyrene, chrysene, lead, chromium. |
F039 | All constituents for which treatment standards are specified for multi-source leachate (wastewaters and nonwastewaters) under Table B to 35 Ill. Adm. Code 728 (Constituent Concentrations in Waste). |
K001 | Pentachlorophenol, phenol, 2-chlorophenol, p-chloro-m-cresol, 2,4-dimethylphenol, 2,4- dinitrophenol, trichlorophenols, tetrachlorophenols, 2,4- dinitrophenol, creosote, chrysene, naphthalene, fluoranthene, benzo(b)fluoranthene, benzo(a)pyrene, indeno(1,2,3-cd)pyrene, benz(a) anthracene, dibenz(a)anthracene, acenaphthalene. |
K002 | Hexavalent chromium, lead. |
K003 | Hexavalent chromium, lead. |
K004 | Hexavalent chromium. |
K005 | Hexavalent chromium, lead. |
K006 | Hexavalent chromium. |
K007 | Cyanide (complexed), hexavalent chromium. |
K008 | Hexavalent chromium. |
K009 | Chloroform, formaldehyde, methylene chloride, methyl chloride, paraldehyde, formic acid. |
K010 | Chloroform, formaldehyde, methylene chloride, methyl chloride, paraldehyde, formic acid, chloroacetaldehyde. |
K011 | Acrylonitrile, acetonitrile, hydrocyanic acid. |
K013 | Hydrocyanic acid, acrylonitrile, acetonitrile. |
K014 | Acetonitrile, acrylamide. |
K015 | Benzyl chloride, chlorobenzene, toluene, benzotrichloride. |
K016 | Hexachlorobenzene, hexachlorobutadiene, carbon tetrachloride, hexachloroethane, perchloroethylene. |
K017 | Epichlorohydrin, chloroethers (bis(chloromethyl) ether and bis- (2-chloroethyl) ethers), trichloropropane, dichloropropanols. |
K018 | 1,2-dichloroethane, trichloroethylene, hexachlorobutadiene, hexachlorobenzene. |
K019 | Ethylene dichloride, 1,1,1-trichloroethane, 1,1,2-trichloroethane, tetrachloroethanes (1,1,2,2-tetrachloroethane and 1,1,1,2-tetrachloroethane), trichloroethylene, tetrachloroethylene, carbon tetrachloride, chloroform, vinyl chloride, vinylidene chloride. |
K020 | Ethylene dichloride, 1,1,1-trichloroethane, 1,1,2-trichloroethane, tetrachloroethanes (1,1,2,2-tetrachloroethane and 1,1,1,2-tetrachloroethane), trichloroethylene, tetrachloroethylene, carbon tetrachloride, chloroform, vinyl chloride, vinylidene chloride. |
K021 | Antimony, carbon tetrachloride, chloroform. |
K022 | Phenol, tars (polycyclic aromatic hydrocarbons). |
K023 | Phthalic anhydride, maleic anhydride. |
K024 | Phthalic anhydride, 1,4-naphthoguinone. |
K025 | Meta-dinitrobenzene, 2,4-dinitrotoluene. |
K026 | Paraldehyde, pyridines, 2-picoline. |
K027 | Toluene diisocyanate, toluene-2,4-diamine. |
K028 | 1,1,1-trichloroethane, vinyl chloride. |
K029 | 1,2-dichloroethane, 1,1,1-trichloroethane, vinyl chloride, vinylidene chloride, chloroform. |
K030 | Hexachlorobenzene, hexachlorobutadiene, hexachloroethane, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane, ethylene dichloride. |
K031 | Arsenic. |
K032 | Hexachlorocyclopentadiene. |
K033 | Hexachlorocyclopentadiene. |
K034 | Hexachlorocyclopentadiene. |
K035 | Creosote, chrysene, naphthalene, fluoranthene, benzo(b) fluoranthene, benzo(a)-pyrene, indeno(1,2,3-cd) pyrene, benzo(a)anthracene, dibenzo(a)anthracene, acenaphthalene. |
K036 | Toluene, phosphorodithioic and phosphorothioic acid esters. |
K037 | Toluene, phosphorodithioic and phosphorothioic acid esters. |
K038 | Phorate, formaldehyde, phosphorodithioic and phosphorothioic acid esters. |
K039 | Phosphorodithioic and phosphorothioic acid esters. |
K040 | Phorate, formaldehyde, phosphorodithioic and phosphorothioic acid esters. |
K041 | Toxaphene. |
K042 | Hexachlorobenzene, ortho-dichlorobenzene. |
K043 | 2,4-dichlorophenol, 2,6-dichlorophenol, 2,4,6-trichlorophenol. |
K044 | N.A. |
K045 | N.A. |
K046 | Lead. |
K047 | N.A. |
K048 | Hexavalent chromium, lead. |
K049 | Hexavalent chromium, lead. |
K050 | Hexavalent chromium. |
K051 | Hexavalent chromium, lead. |
K052 | Lead. |
K060 | Cyanide, naphthalene, phenolic compounds, arsenic. |
K061 | Hexavalent chromium, lead, cadmium. |
K062 | Hexavalent chromium, lead. |
K069 | Hexavalent chromium, lead, cadmium. |
K071 | Mercury. |
K073 | Chloroform, carbon tetrachloride, hexachloroethane, trichloroethane, tetrachloroethylene, dichloroethylene, 1,1,2,2-tetrachloroethane. |
K083 | Aniline, diphenylamine, nitrobenzene, phenylenediamine. |
K084 | Arsenic. |
K085 | Benzene, dichlorobenzenes, trichlorobenzenes, tetrachlorobenzenes, pentachlorobenzene, hexachlorobenzene, benzyl chloride. |
K086 | Lead, hexavalent chromium. |
K087 | Phenol, naphthalene. |
K088 | Cyanide (complexes). |
K093 | Phthalic anhydride, maleic anhydride. |
K094 | Phthalic anhydride. |
K095 | 1,1,2-trichloroethane, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane. |
K096 | 1,2-dichloroethane, 1,1,1-trichloroethane, 1,1,2-trichloroethane. |
K097 | Chlordane, heptachlor. |
K098 | Toxaphene. |
K099 | 2,4-dichlorophenol, 2,4,6-trichlorophenol. |
K100 | Hexavalent chromium, lead, cadmium. |
K101 | Arsenic. |
K102 | Arsenic. |
K103 | Aniline, nitrobenzene, phenylenediamine. |
K104 | Aniline, benzene, diphenylamine, nitrobenzene, phynylenediamine. |
K105 | Benzene, monochlorobenzene, dichlorobenzenes, 2,4,6-trichlorophenol. |
K106 | Mercury. |
K111 | 2,4-Dinitrotoluene. |
K112 | 2,4-Toluenediamine, o-toluidine, p-toluidine, aniline. |
K113 | 2,4-Toluenediamine, o-toluidine, p-toluidine, aniline. |
K114 | 2,4-Toluenediamine, o-toluidine, p-toluidine. |
K115 | 2,4-Toluenediamine. |
K116 | Carbon tetrachloride, tetrachloroethylene, chloroform, phosgene. |
K117 | Ethylene dibromide. |
K118 | Ethylene dibromide. |
K123 | Ethylene thiourea. |
K124 | Ethylene thiourea. |
K125 | Ethylene thiourea. |
K126 | Ethylene thiourea. |
K131 | Dimethyl sulfate, methyl bromide. |
K132 | Methyl bromide. |
K136 | Ethylene dibromide. |
K141 | Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene. |
K142 | Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene. |
K143 | Benzene, benz(a)anthracene, benzo(b)fluoranthene, benzo(k)fluoranthene. |
K144 | Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene. |
K145 | Benzene, benz(a)anthracene, benzo(a)pyrene, dibenz(a,h)anthracene, naphthalene. |
K147 | Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene. |
K148 | Benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene. |
K149 | Benzotrichloride, benzyl chloride, chloroform, chloromethane, chlorobenzene, 1,4-dichlorobenzene, hexachlorobenzene, pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, toluene. |
K150 | Carbon tetrachloride, chloroform, chloromethane, 1,4-dichlorobenzene, hexachlorobenzene, pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, 1,1,2,2-tetrachloroethane, tetrachloroethylene, 1,2,4-trichlorobenzene. |
K151 | Benzene, carbon tetrachloride, chloroform, hexachlorobenzene, pentachlorobenzene, toluene, 1,2,4,5-tetrachlorobenzene, tetrachloroethylene. |
K156 | Benomyl, carbaryl, carbendazim, carbofuran, carbosulfan, formaldehyde, methylene chloride, triethylamine. |
K157 | Carbon tetrachloride, formaldehyde, methyl chloride, methylene chloride, pyridine, triethylamine. |
K158 | Benomyl, carbendazim, carbofuran, carbosulfan, chloroform, methylene chloride. |
K159 | Benzene, butylate, EPTC, molinate, pebulate, vernolate. |
K161 | Antimony, arsenic, metam-sodium, ziram. |
K169 | Benzene. |
K170 | Benzo(a)pyrene, dibenz(a,h)anthracene, benzo (a) anthracene, benzo(b)fluoranthene, benzo(k)fluoranthene, 3-methylcholanthrene, 7,12-dimethylbenz(a)anthracene. |
K171 | Benzene, arsenic. |
K172 | Benzene, arsenic. |
K174 | 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD), 1,2,3,4,6,7,8-heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF), 1,2,3,4,7,8,9-heptachlorodibenzofuran (1,2,3,6,7,8,9-HpCDF), all hexachlorodibenzo-p-dioxins (HxCDDs), all hexachlorodibenzofurans (HxCDFs), all pentachlorodibenzo-p-dioxins (PeCDDs), 1,2,3,4,6,7,8,9-octachlorodibenzo-p-dioxin (OCDD), 1,2,3,4,6,7,8,9- octachlorodibenzofuran (OCDF), all pentachlorodibenzofurans (PeCDFs), all tetrachlorodibenzo-p-dioxins (TCDDs), all tetrachlorodibenzofurans (TCDFs). |
K175 | Mercury. |
K176 | Arsenic, lead. |
K177 | Antimony. |
K178 | Thallium. |
K181 | Aniline, o-anisidine, 4-chloroaniline, p-cresidine, 2,4-dimethylaniline, 1,2-phenylenediamine, 1,3-phenylenediamine. |
Common Name | Chemical Abstracts Name | Chemical Abstracts Number (CAS No.) | USEPA Hazardous Waste Number
|
A2213 | Ethanimidothioic acid, 2- (dimethylamino)-N-hydroxy-2-oxo-, methyl ester | 30558-43-1 | U394
|
Acetonitrile | Same | 75-05-8 | U003
|
Acetophenone | Ethanone, 1-phenyl- | 98-86-2 | U004
|
2-Acetylaminofluorene | Acetamide, N-9H-fluoren-2-yl- | 53-96-3 | U005
|
Acetyl chloride | Same | 75-36-5 | U006
|
1-Acetyl-2-thiourea | Acetamide, N-(aminothioxomethyl)- | 591-08-2 | P002
|
Acrolein | 2-Propenal | 107-02-8 | P003
|
Acrylamide | 2-Propenamide | 79-06-1 | U007
|
Acrylonitrile | 2-Propenenitrile | 107-13-1 | U009
|
Aflatoxins | Same | 1402-68-2 | |
Aldicarb | Propanal, 2-methyl-2-(methylthio)-, O-((methylamino)carbonyl)oxime | 116-06-3 | P070
|
Aldicarb sulfone | Propanal, 2-methyl-2- (methylsulfonyl)-, O-((methylamino)carbonyl)oxime | 1646-88-4 | P203
|
Aldrin | 1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1- a ,4- a ,4a- b ,5- a ,8- a ,8a- b )- | 309-00-2 | P004
|
Allyl alcohol | 2-Propen-1-ol | 107-18-6 | P005
|
Allyl chloride | 1-Propene, 3-chloro- | 107-05-1 | |
Aluminum phosphide | Same | 20859-73-8 | P006
|
4-Aminobiphenyl | (1,1'-Biphenyl)-4-amine | 92-67-1 | |
5-(Aminomethyl)-3-isoxazolol | 3(2H)-Isoxazolone, 5-(aminomethyl)- | 2763-96-4 | P007
|
4-Aminopyridine | 4-Pyridinamine | 504-24-5 | P008
|
Amitrole | 1H-1,2,4-Triazol-3-amine | 61-82-5 | U011
|
Ammonium vanadate | Vanadic acid, ammonium salt | 7803-55-6 | U119
|
Aniline | Benzenamine | 62-53-3 | U012
|
o-Anisidine (2-methoxyaniline) | Benzenamine, 2-Methoxy- | 90–04–0 | |
Antimony | Same | 7440-36-0 | |
Antimony compounds, N.O.S. (not otherwise specified) | |||
Aramite | Sulfurous acid, 2-chloroethyl-, 2-(4-(1,1-dimethylethyl)phenoxy)-1-methylethyl ester | 140-57-8 | |
Arsenic | Arsenic | 7440-38-2 | |
Arsenic compounds, N.O.S. | |||
Arsenic acid | Arsenic acid H3AsO4 | 7778-39-4 | P010
|
Arsenic pentoxide | Arsenic oxide As2O5 | 1303-28-2 | P011
|
Arsenic trioxide | Arsenic oxide As2O3 | 1327-53-3 | P012
|
Auramine | Benzenamine, 4,4'-carbonimidoylbis(N, N-dimethyl- | 492-80-8 | U014
|
Azaserine | L-Serine, diazoacetate (ester) | 115-02-6 | U015
|
Barban | Carbamic acid, (3-chlorophenyl)-, 4-chloro-2-butynyl ester | 101-27-9 | U280
|
Barium | Same | 7440-39-3 | |
Barium compounds, N.O.S. | |||
Barium cyanide | Same | 542-62-1 | P013
|
Bendiocarb | 1,3-Benzodioxol-4-ol-2,2-dimethyl-, methyl carbamate | 22781-23-3 | U278
|
Bendiocarb phenol | 1,3-Benzodioxol-4-ol-2,2-dimethyl-, | 22961-82-6 | U364
|
Benomyl | Carbamic acid, (1- ((butylamino)carbonyl)-1H-benzimidazol-2-yl)-, methyl ester | 17804-35-2 | U271
|
Benz(c)acridine | Same | 225-51-4 | U016
|
Benz(a)anthracene | Same | 56-55-3 | U018
|
Benzal chloride | Benzene, (dichloromethyl)- | 98-87-3 | U017
|
Benzene | Same | 71-43-2 | U018
|
Benzenearsonic acid | Arsonic acid, phenyl- | 98-05-5 | |
Benzidine | (1,1'-Biphenyl)-4,4'-diamine | 92-87-5 | U021
|
Benzo(b)fluoranthene | Benz(e)acephenanthrylene | 205-99-2 | |
Benzo(j)fluoranthene | Same | 205-82-3 | |
Benzo(k)fluoranthene | Same | 207-08-9 | |
Benzo(a)pyrene | Same | 50-32-8 | U022
|
p-Benzoquinone | 2,5-Cyclohexadiene-1,4-dione | 106-51-4 | U197
|
Benzotrichloride | Benzene, (trichloromethyl)- | 98-07-7 | U023
|
Benzyl chloride | Benzene, (chloromethyl)- | 100-44-7 | P028
|
Beryllium powder | Same | 7440-41-7 | P015
|
Beryllium compounds, N.O.S. | |||
Bis(pentamethylene)thiuram tetrasulfide | Piperidine, 1,1'-(tetrathiodicarbonothioyl)-bis- | 120-54-7 | |
Bromoacetone | 2-Propanone, 1-bromo- | 598-31-2 | P017
|
Bromoform | Methane, tribromo- | 75-25-2 | U225
|
4-Bromophenyl phenyl ether | Benzene, 1-bromo-4-phenoxy- | 101-55-3 | U030
|
Brucine | Strychnidin-10-one, 2,3-dimethoxy- | 357-57-3 | P018
|
Butylate | Carbamothioic acid, bis(2-methylpropyl)-, S-ethyl ester | 2008-41-5 | |
Butyl benzyl phthalate | 1,2-Benzenedicarboxylic acid, butyl phenylmethyl ester | 85-68-7 | |
Cacodylic acid | Arsenic acid, dimethyl- | 75-60-5 | U136
|
Cadmium | Same | 7440-43-9 | |
Cadmium compounds, N.O.S. | |||
Calcium chromate | Chromic acid H2CrO4, calcium salt | 13765-19-0 | U032
|
Calcium cyanide | Calcium cyanide Ca(CN)2 | 592-01-8 | P021
|
Carbaryl | 1-Naphthalenol, methylcarbamate | 63-25-2 | U279
|
Carbendazim | Carbamic acid, 1H-benzimidazol-2-yl, methyl ester | 10605-21-7 | U372
|
Carbofuran | 7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-, methylcarbamate | 1563-66-2 | P127
|
Carbofuran phenol | 7-Benzofuranol, 2,3-dihydro-2,2-dimethyl- | 1563-38-8 | U367
|
Carbosulfan | Carbamic acid, ((dibutylamino)thio)methyl-2,3-dihydro-2,2-dimethyl-7-benzofuranyl ester | 55285-14-8 | P189
|
Carbon disulfide | Same | 75-15-0 | P022
|
Carbon oxyfluoride | Carbonic difuoride | 353-50-4 | U033
|
Carbon tetrachloride | Methane, tetrachloro- | 56-23-5 | U211
|
Chloral | Acetaldehyde, trichloro- | 75-87-6 | U034
|
Chlorambucil | Benzenebutanoic acid, 4(bis-(2-chloroethyl)amino)- | 305-03-3 | U035
|
Chlordane | 4,7-Methano-1H-indene, 1,2,4,5,6,7,8,8-octachloro-2,3,3a,4,7,7a-hexahydro- | 57-74-9 | U036
|
Chlordane, a and g isomers | U036
|
||
Chlorinated benzenes, N.O.S. | |||
Chlorinated ethane, N.O.S. | |||
Chlorinated fluorocarbons, N.O.S.
|
|||
Chlorinated naphthalene, N.O.S. | |||
Chlorinated phenol, N.O.S. | |||
Chlornaphazine | Naphthalenamine, N,N'-bis(2-chloroethyl)- | 494-03-1 | U026
|
Chloroacetaldehyde | Acetaldehyde, chloro- | 107-20-0 | P023
|
Chloroalkyl ethers, N.O.S. | |||
p-Chloroaniline | Benzenamine, 4-chloro- | 106-47-8 | P024
|
Chlorobenzene | Benzene, chloro- | 108-90-7 | U037
|
Chlorobenzilate | Benzeneacetic acid, 4-chloro- a -(4-chlorophenyl)- a -hydroxy-, ethyl ester | 510-15-6 | U038
|
p-Chloro-m-cresol | Phenol, 4-chloro-3-methyl- | 59-50-7 | U039
|
2-Chloroethyl vinyl ether | Ethene, (2-chloroethoxy)- | 110-75-8 | U042
|
Chloroform | Methane, trichloro- | 67-66-3 | U044
|
Chloromethyl methyl ether | Methane, chloromethoxy- | 107-30-2 | U046
|
b -Chloronaphthalene | Naphthalene, 2-chloro- | 91-58-7 | U047
|
o-Chlorophenol | Phenol, 2-chloro- | 95-57-8 | U048
|
1-(o-Chlorophenyl)thiourea | Thiourea, (2-chlorophenyl)- | 5344-82-1 | P026
|
Chloroprene | 1,3-Butadiene, 2-chloro- | 126-99-8 | |
3-Chloropropionitrile | Propanenitrile, 3-chloro- | 542-76-7 | P027
|
Chromium | Same | 7440-47-3 | |
Chromium compounds, N.O.S. | |||
Chrysene | Same | 218-01-9 | U050
|
Citrus red No. 2 | 2-Naphthalenol, 1-((2,5-dimethoxyphenyl)azo)- | 6358-53-8 | |
Coal tar creosote | Same | 8007-45-2 | |
Copper cyanide | Copper cyanide CuCN | 544-92-3 | P029
|
Copper dimethyldithiocarbamate | Copper, bis(dimethylcarbamodithioato-S,S')-, | 137-29-1 | |
Creosote | Same | U051
|
|
p-Cresidine | 2-Methoxy-5-methylbenzenamine | 120–71–8 | |
Cresols (Cresylic acid) | Phenol, methyl- | 1319-77-3 | U052
|
Crotonaldehyde | 2-Butenal | 4170-30-3 | U053
|
m-Cumenyl methylcarbamate | Phenol, 3-(methylethyl)-, methyl carbamate | 64-00-6 | P202
|
Cyanides (soluble salts and complexes), N.O.S. | P030
|
||
Cyanogen | Ethanedinitrile | 460-19-5 | P031
|
Cyanogen bromide | Cyanogen bromide (CN)Br | 506-68-3 | U246
|
Cyanogen chloride | Cyanogen chloride (CN)Cl | 506-77-4 | P033
|
Cycasin | b -D-glucopyranoside, (methyl-ONN-azoxy)methyl- | 14901-08-7 | |
Cycloate | Carbamothioic acid, cyclohexylethyl-, S-ethyl ester | 1134-23-2 | |
2-Cyclohexyl-4,6-dinitrophenol | Phenol, 2-cyclohexyl-4,6-dinitro- | 131-89-5 | P034
|
Cyclophosphamide | 2H-1,3,2-Oxazaphosphorin-2-amine, N,N-bis(2-chloroethyl)tetrahydro-2-oxide | 50-18-0 | U058
|
2,4-D | Acetic acid, (2,4-dichlorophenoxy)- | 94-75-7 | U240
|
2,4-D, salts and esters | Acetic acid, (2,4-dichlorophenoxy)-, salts and esters | U240
|
|
Daunomycin | 5, 12-Naphthacenedione, 8-acetyl-10-((3-amino-2,3,6-trideoxy- a -L-lyxo-hexopyranosyl)oxy)-7,8,9,10-tetrahydro-6,8,11-trihydroxy-l-methoxy-, 8S-cis)- | 20830-81-3 | U059
|
Dazomet | 2H-1,3,5-thiadiazine-2-thione, tetrahydro-3,5-dimethyl | 533-74-4 | |
DDD | Benzene, 1,1'-(2,2-dichloroethylidene)bis(4-chloro- | 72-54-8 | U060
|
DDE | Benzene, 1,1'-(dichloroethenylidene)bis(4-chloro- | 72-55-9 | |
DDT | Benzene, 1,1'-(2,2,2-trichloroethylidene)bis(4-chloro- | 50-29-3 | U061
|
Diallate | Carbamothioic acid, bis(1-methylethyl)-, S-(2,3-dichloro-2-propenyl) ester | 2303-16-4 | U062
|
Dibenz(a,h)acridine | Same | 226-36-8 | |
Dibenz(a,j)acridine | Same | 224-42-0 | |
Dibenz(a,h)anthracene | Same | 53-70-3 | U063
|
7H-Dibenzo(c,g)carbazole | Same | 194-59-2 | |
Dibenzo(a,e)pyrene | Naphtho(1,2,3,4-def)chrysene | 192-65-4 | |
Dibenzo(a,h)pyrene | Dibenzo(b,def)chrysene | 189-64-0 | |
Dibenzo(a,i)pyrene | Benzo(rst)pentaphene | 189-55-9 | U064
|
1,2-Dibromo-3-chloropropane | Propane, 1,2-dibromo-3-chloro- | 96-12-8 | U066
|
Dibutyl phthalate | 1,2-Benzenedicarboxylic acid, dibutyl ester | 84-74-2 | U069
|
o-Dichlorobenzene | Benzene, 1,2-dichloro- | 95-50-1 | U070
|
m-Dichlorobenzene | Benzene, 1,3-dichloro- | 541-73-1 | U071
|
p-Dichlorobenzene | Benzene, 1,4-dichloro- | 106-46-7 | U072
|
Dichlorobenzene, N.O.S. | Benzene, dichloro- | 25321-22-6 | |
3,3'-Dichlorobenzidine | (1,1'-Biphenyl)-4,4'-diamine, 3,3'-dichloro- | 91-94-1 | U073
|
1,4-Dichloro-2-butene | 2-Butene, 1,4-dichloro- | 764-41-0 | U074
|
Dichlorodifluoromethane | Methane, dichlorodifluoro- | 75-71-8 | U075
|
Dichloroethylene, N.O.S. | Dichloroethylene | 25323-30-2 | |
1,1-Dichloroethylene | Ethene, 1,1-dichloro- | 75-35-4 | U078
|
1,2-Dichloroethylene | Ethene, 1,2-dichloro-, (E)- | 156-60-5 | U079
|
Dichloroethyl ether | Ethane, 1,1'-oxybis(2-chloro- | 111-44-4 | U025
|
Dichloroisopropyl ether | Propane, 2,2'-oxybis(2-chloro- | 108-60-1 | U027
|
Dichloromethoxyethane | Ethane, 1,1'-(methylenebis(oxy)bis(2-chloro- | 111-91-1 | U024
|
Dichloromethyl ether | Methane, oxybis(chloro- | 542-88-1 | P016
|
2,4-Dichlorophenol | Phenol, 2,4-dichloro- | 120-83-2 | U081
|
2,6-Dichlorophenol | Phenol, 2,6-dichloro- | 87-65-0 | U082
|
Dichlorophenylarsine | Arsonous dichloride, phenyl- | 696-28-6 | P036
|
Dichloropropane, N.O.S. | Propane, dichloro- | 26638-19-7 | |
Dichloropropanol, N.O.S. | Propanol, dichloro- | 26545-73-3 | |
Dichloropropene, N.O.S. | 1-Propene, dichloro- | 26952-23-8 | |
1,3-Dichloropropene | 1-Propene, 1,3-dichloro- | 542-75-6 | U084
|
Dieldrin | 2,7:3,6-Dimethanonaphth(2, 3-b)oxirene, 3,4,5,6,9,9-hexachloro-1a,2,2a,3,6, 6a,7,7a-octahydro-, (1a a ,2 b ,2a a ,3 b ,6 b ,6a a ,7 b ,7a a )- | 60-57-1 | P037
|
1,2:3,4-Diepoxybutane | 2,2'-Bioxirane | 1464-53-5 | U085
|
Diethylarsine | Arsine, diethyl- | 692-42-2 | P038
|
Diethylene glycol, dicarbamate | Ethanol, 2,2'-oxybis-, dicarbamate | 5952-26-1 | U395
|
1,4-Diethyleneoxide | 1,4-Dioxane | 123-91-1 | U108
|
Diethylhexyl phthalate | 1,2-Benzenedicarboxylic acid, bis(2-ethylhexyl) ester | 117-81-7 | U028
|
N,N'-Diethylhydrazine | Hydrazine, 1,2-diethyl- | 1615-80-1 | U086
|
O,O-Diethyl-S-methyl dithiophosphate | Phosphorodithioic acid, O,O-diethyl S-methyl ester | 3288-58-2 | U087
|
Diethyl-p-nitrophenyl phosphate | Phosphoric acid, diethyl 4-nitrophenyl ester | 311-45-5 | P041
|
Diethyl phthalate | 1,2-Benzenedicarboxylic acid, diethyl ester | 84-66-2 | U088
|
O,O-Diethyl O-pyrazinyl phosphorothioate | Phosphorothioic acid, O,O-diethyl O-pyrazinyl ester | 297-97-2 | P040
|
Diethylstilbestrol | Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-, (E)- | 56-53-1 | U089
|
Dihydrosafrole | 1,3-Benzodioxole, 5-propyl- | 94-58-6 | U090
|
Diisopropylfluorophosphate (DFP) | Phosphorofluoridic acid, bis(1-methylethyl) ester | 55-91-4 | P043
|
Dimethoate | Phosphorodithioic acid, O,O-dimethyl S-(2-(methylamino)-2-oxoethyl) ester | 60-51-5 | P044
|
3,3'-Dimethoxybenzidine | (1,1'-Biphenyl)-4,4'-diamine, 3,3'-dimethoxy- | 119-90-4 | U091
|
p-Dimethylaminoazobenzene | Benzenamine, N,N-dimethyl-4-(phenylazo)- | 60-11-7 | U093
|
2,4-Dimethylaniline (2,4-xylidine) | Benzenamine, 2,4-dimethyl- | 95–68–1 | |
7,12-Dimethylbenz(a)anthracene | Benz(a)anthracene, 7,12-dimethyl- | 57-97-6 | U094
|
3,3'-Dimethylbenzidine | (1,1'-Biphenyl)-4,4'-diamine, 3,3'-dimethyl- | 119-93-7 | U095
|
Dimethylcarbamoyl chloride | Carbamic chloride, dimethyl- | 79-44-7 | U097
|
1,1-Dimethylhydrazine | Hydrazine, 1,1-dimethyl- | 57-14-7 | U098
|
1,2-Dimethylhydrazine | Hydrazine, 1,2-dimethyl- | 540-73-8 | U099
|
a , a -Dimethylphenethylamine | Benzeneethanamine, a , a -dimethyl- | 122-09-8 | P046
|
2,4-Dimethylphenol | Phenol, 2,4-dimethyl- | 105-67-9 | U101
|
Dimethylphthalate | 1,2-Benzenedicarboxylic acid, dimethyl ester | 131-11-3 | U102
|
Dimethyl sulfate | Sulfuric acid, dimethyl ester | 77-78-1 | U103
|
Dimetilan | Carbamic acid, dimethyl-, 1- ((dimethylamino) carbonyl)-5-methyl-1H-pyrazol-3-yl ester | 644-64-4 | P191
|
Dinitrobenzene, N.O.S. | Benzene, dinitro- | 25154-54-5 | |
4,6-Dinitro-o-cresol | Phenol, 2-methyl-4,6-dinitro- | 534-52-1 | P047
|
4,6-Dinitro-o-cresol salts | P047
|
||
2,4-Dinitrophenol | Phenol, 2,4-dinitro- | 51-28-5 | P048
|
2,4-Dinitrotoluene | Benzene, 1-methyl-2,4-dinitro- | 121-14-2 | U105
|
2,6-Dinitrotoluene | Benzene, 2-methyl-1,3-dinitro- | 606-20-2 | U106
|
Dinoseb | Phenol, 2-(1-methylpropyl)-4,6-dinitro- | 88-85-7 | P020
|
Di-n-octyl phthalate | 1,2-Benzenedicarboxylic acid, dioctyl ester | 117-84-0 | U107
|
Diphenylamine | Benzenamine, N-phenyl- | 122-39-4 | |
1,2-Diphenylhydrazine | Hydrazine, 1,2-diphenyl- | 122-66-7 | U109
|
Di-n-propylnitrosamine | 1-Propanamine, N-nitroso-N-propyl- | 621-64-7 | U111
|
Disulfiram | Thioperoxydicarbonic diamide, tetraethyl | 97-77-8 | |
Disulfoton | Phosphorodithioic acid, O,O-diethyl S-(2-(ethylthio)ethyl) ester | 298-04-4 | P039
|
Dithiobiuret | Thioimidodicarbonic diamide ((H2N)C(S))2NH | 541-53-7 | P049
|
Endosulfan | 6, 9-Methano-2,4,3-benzodioxathiepen,6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide, | 115-29-7 | P050
|
Endothal | 7-Oxabicyclo(2.2.1)heptane-2,3-dicarboxylic acid | 145-73-3 | P088
|
Endrin | 2,7:3,6-Dimethanonaphth(2,3-b)oxirene, 3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-, (1a a ,2 b ,2a b ,3 a ,6 a ,6a b ,7 b ,7a a )-, | 72-20-8 | P051
|
Endrin metabolites | P051
|
||
Epichlorohydrin | Oxirane, (chloromethyl)- | 106-89-8 | U041
|
Epinephrine | 1,2-Benzenediol, 4-(1-hydroxy-2-(methylamino)ethyl)-, (R)- | 51-43-4 | P042
|
EPTC | Carbamothioic acid, dipropyl-, S-ethyl ester | 759-94-4 | |
Ethyl carbamate (urethane) | Carbamic acid, ethyl ester | 51-79-6 | U238
|
Ethyl cyanide | Propanenitrile | 107-12-0 | P101
|
Ethylenebisdithiocarbamic acid | Carbamodithioic acid, 1,2-ethanediylbis- | 111-54-6 | U114
|
Ethylenebisdithiocarbamic acid, salts and esters | U114
|
||
Ethylene dibromide | Ethane, 1,2-dibromo- | 106-93-4 | U067
|
Ethylene dichloride | Ethane, 1,2-dichloro- | 107-06-2 | |
Ethylene glycol monoethyl ether | Ethanol, 2-ethoxy- | 110-80-5 | U359
|
Ethyleneimine | Aziridine | 151-56-4 | P054
|
Ethylene oxide | Oxirane | 75-21-8 | U115
|
Ethylenethiourea | 2-Imidazolidinethione | 96-45-7 | U116
|
Ethylidine dichloride | Ethane, 1,1-dichloro- | 75-34-3 | U076
|
Ethyl methacrylate | 2-Propenoic acid, 2-methyl-, ethyl ester | 97-63-2 | U118
|
Ethyl methanesulfonate | Methanesulfonic acid, ethyl ester | 62-50-0 | U119
|
Ethyl Ziram | Zinc, bis(diethylcarbamodithioato-S,S')- | 14324-55-1 | U407
|
Famphur | Phosphorothioc acid, O-(4-((dimethylamino)sulfonyl)phenyl) O,O-dimethyl ester | 52-85-7 | P097
|
Ferbam | Iron, tris(dimethylcarbamodithioato-S,S')-, | 14484-64-1 | |
Fluoranthene | Same | 206-44-0 | U120
|
Fluorine | Same | 7782-41-4 | P056
|
Fluoroacetamide | Acetamide, 2-fluoro- | 640-19-7 | P057
|
Fluoroacetic acid, sodium salt | Acetic acid, fluoro-, sodium salt | 62-74-8 | P058
|
Formaldehyde | Same | 50-00-0 | U122
|
Formetanate hydrochloride | Methanimidamide, N,N-dimethyl-N'-(3-(((methylamino)carbonyl)oxy)phenyl)-, monohydrochloride | 23422-53-9 | P198
|
Formic acid | Same | 64-18-16 | U123
|
Formparanate | Methanimidamide, N,N-dimethyl-N'-(2-methyl-4-(((methylamino)carbonyl)oxy)phenyl)- | 17702-57-7 | P197
|
Glycidylaldehyde | Oxiranecarboxaldehyde | 765-34-4 | U126
|
Halomethanes, N.O.S. | |||
Heptachlor | 4,7-Methano-1H-indene,1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro- | 76-44-8 | P059
|
Heptachlor epoxide | 2,5-Methano-2H-indeno(1, 2b)oxirene, 2,3,4,5,6,7,7-heptachloro-1a,1b,5,5a,6,6a-hexahydro-, (1a a ,1b b ,2 a ,5 a ,5a b ,6 b ,6a a )- | 1024-57-3 | |
Heptachlor epoxide ( a , b , and g isomers) | |||
Heptachlorodibenzofurans | |||
Heptachlorodibenzo-p-dioxins | |||
Hexachlorobenzene | Benzene, hexachloro- | 118-74-1 | U127
|
Hexachlorobutadiene | 1,3-Butadiene, 1,1,2,3,4,4-hexachloro- | 87-68-3 | U128
|
Hexachlorocyclo-pentadiene | 1,3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro- | 77-47-4 | U130
|
Hexachlorodibenzo-p-dioxins | |||
Hexachlorodibenzofurans | |||
Hexachloroethane | Ethane, hexachloro- | 67-72-1 | U131
|
Hexachlorophene | Phenol, 2,2'-methylenebis(3,4,6-trichloro- | 70-30-4 | U132
|
Hexachloropropene | 1-Propene, 1,1,2,3,3,3-hexachloro- | 1888-71-7 | U243
|
Hexaethyltetraphosphate | Tetraphosphoric acid, hexaethyl ester | 757-58-4 | P062
|
Hydrazine | Same | 302-01-2 | U133
|
Hydrogen cyanide | Hydrocyanic acid | 74-90-8 | P063
|
Hydrogen fluoride | Hydrofluoric acid | 7664-39-3 | U134
|
Hydrogen sulfide | Hydrogen sulfide H2S | 7783-06-4 | U135
|
Indeno(1,2,3-cd)pyrene | Same | 193-39-5 | U137
|
3-Iodo-2-propynyl-n-butylcarbamate | Carbamic acid, butyl-, 3-iodo-2-propynyl ester | 55406-53-6 | |
Isobutyl alcohol | 1-Propanol, 2-methyl- | 78-83-1 | U140
|
Isodrin | 1,4:5,8-Dimethanonaphthalene,1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1 a ,4 a ,4a b ,5 b ,8 b ,8a b )-, | 465-73-6 | P060
|
Isolan | Carbamic acid, dimethyl-, 3-methyl-1-(1-methylethyl)-1H-pyrazol-5-yl ester | 119-38-0 | P192
|
Isosafrole | 1,3-Benzodioxole, 5-(1-propenyl)- | 120-58-1 | U141
|
Kepone | 1,3,4-Metheno-2H-cyclobuta(cd)pentalen-2-one, 1,1a,3,3a,4,5,5,5a,5b,6-decachlorooctahydro-, | 143-50-0 | U142
|
Lasiocarpine | 2-Butenoic acid, 2-methyl-, 7-((2,3-dihydroxy-2-(1-methoxyethyl)-3-methyl-1-oxobutoxy)methyl)-2,3,5,7a-tetrahydro-1H-pyrrolizin-l-yl ester, (1S-(1- a (Z),7(2S*,3R*),7a a ))- | 303-34-4 | U143
|
Lead | Same | 7439-92-1 | |
Lead and compounds, N.O.S. | |||
Lead acetate | Acetic acid, lead (2+) salt | 301-04-2 | U144
|
Lead phosphate | Phosphoric acid, lead (2+) salt (2:3) | 7446-27-7 | U145
|
Lead subacetate | Lead, bis(acetato-O)tetrahydroxytri- | 1335-32-6 | U146
|
Lindane | Cyclohexane, 1,2,3,4,5,6-hexachloro-, 1 a ,2 a ,3 b ,4 a ,5 a ,6 b )- | 58-89-9 | U129
|
Maleic anhydride | 2,5-Furandione | 108-31-6 | U147
|
Maleic hydrazide | 3,6-Pyridazinedione, 1,2-dihydro- | 123-33-1 | U148
|
Malononitrile | Propanedinitrile | 109-77-3 | U149
|
Manganese dimethyldithiocarbamate | Manganese, bis(dimethylcarbamodithioato-S,S')-, | 15339-36-3 | P196
|
Melphalan | L-Phenylalanine, 4-(bis(2-chloroethyl)amino)- | 148-82-3 | U150
|
Mercury | Same | 7439-97-6 | U151
|
Mercury compounds, N.O.S. | |||
Mercury fulminate | Fulminic acid, mercury (2+) salt | 628-86-4 | P065
|
Metam Sodium | Carbamodithioic acid, methyl-, monosodium salt | 137-42-8 | |
Methacrylonitrile | 2-Propenenitrile, 2-methyl- | 126-98-7 | U152
|
Methapyrilene | 1,2-Ethanediamine, N,N-dimethyl-N'-2-pyridinyl-N'-(2-thienylmethyl)- | 91-80-5 | U155
|
Methiocarb | Phenol, (3,5-dimethyl-4-(methylthio)-, methylcarbamate | 2032-65-7 | P199
|
Metholmyl | Ethanimidothioic acid, N-(((methylamino)carbonyl)oxy)-, methyl ester | 16752-77-5 | P066
|
Methoxychlor | Benzene, 1,1'-(2,2,2-trichloroethylidene)bis(4-methoxy- | 72-43-5 | U247
|
Methyl bromide | Methane, bromo- | 74-83-9 | U029
|
Methyl chloride | Methane, chloro- | 74-87-3 | U045
|
Methylchlorocarbonate | Carbonochloridic acid, methyl ester | 79-22-1 | U156
|
Methyl chloroform | Ethane, 1,1,1-trichloro- | 71-55-6 | U226
|
3-Methylcholanthrene | Benz(j)aceanthrylene, 1,2-dihydro-3-methyl- | 56-49-5 | U157
|
4,4'-Methylenebis(2-chloroaniline) | Benzenamine, 4,4'-methylenebis(2-chloro- | 101-14-4 | U158
|
Methylene bromide | Methane, dibromo- | 74-95-3 | U068
|
Methylene chloride | Methane, dichloro- | 75-09-2 | U080
|
Methyl ethyl ketone (MEK) | 2-Butanone | 78-93-3 | U159
|
Methyl ethyl ketone peroxide | 2-Butanone, peroxide | 1338-23-4 | U160
|
Methyl hydrazine | Hydrazine, methyl- | 60-34-4 | P068
|
Methyl iodide | Methane, iodo- | 74-88-4 | U138
|
Methyl isocyanate | Methane, isocyanato- | 624-83-9 | P064
|
2-Methyllactonitrile | Propanenitrile, 2-hydroxy-2-methyl- | 75-86-5 | P069
|
Methyl methacrylate | 2-Propenoic acid, 2-methyl-, methyl ester | 80-62-6 | U162
|
Methyl methanesulfonate | Methanesulfonic acid, methyl ester | 66-27-3 | |
Methyl parathion | Phosphorothioic acid, O,O-dimethyl O-(4-nitrophenyl) ester | 298-00-0 | P071
|
Methylthiouracil | 4-(1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-thioxo- | 56-04-2 | U164
|
Metolcarb | Carbamic acid, methyl-, 3-methylphenyl ester | 1129-41-5 | P190
|
Mexacarbate | Phenol, 4-(dimethylamino)-3,5-dimethyl-, methylcarbamate (ester) | 315-18-4 | P128
|
Mitomycin C | Azirino(2', 3':3, 4)pyrrolo(1, 2-a)indole-4, 7-dione, 6-amino-8-(((aminocarbonyl)oxy)methyl)-1,1a,2,8,8a,8b-hexahydro-8a-methoxy-5-methyl-, (1a-S-(1a a ,8 b ,8a a ,8b a ))-, | 50-07-7 | U010
|
Molinate | 1H-Azepine-1-carbothioic acid, hexahydro-, S-ethyl ester | 2212-67-1 | |
MNNG | Guanidine, N-methyl-N'-nitro-N-nitroso- | 70-25-7 | U163
|
Mustard gas | Ethane, 1,1'-thiobis(2-chloro- | 505-60-2 | U165
|
Naphthalene | Same | 91-20-3 | U165
|
1,4-Naphthoquinone | 1,4-Naphthalenedione | 130-15-4 | U166
|
a -Naphthylamine | 1-Naphthalenamine | 134-32-7 | U167
|
b -Naphthylamine | 2-Naphthalenamine | 91-59-8 | U168
|
a -Naphthylthiourea | Thiourea, 1-naphthalenyl- | 86-88-4 | P072
|
Nickel | Same | 7440-02-0 | |
Nickel compounds, N.O.S. | |||
Nickel carbonyl | Nickel carbonyl Ni(CO)4, (T-4)- | 13463-39-3 | P073
|
Nickel cyanide | Nickel cyanide Ni(CN)2 | 557-19-7 | P074
|
Nicotine | Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)- | 54-11-5 | P075
|
Nicotine salts | P075
|
||
Nitric oxide | Nitrogen oxide NO | 10102-43-9 | P076
|
p-Nitroaniline | Benzenamine, 4-nitro- | 100-01-6 | P077
|
Nitrobenzene | Benzene, nitro- | 98-95-3 | P078
|
Nitrogen dioxide | Nitrogen oxide NO2 | 10102-44-0 | P078
|
Nitrogen mustard | Ethanamine, 2-chloro-N-(2-chloroethyl)-N-methyl- | 51-75-2 | |
Nitrogen mustard, hydrochloride salt | |||
Nitrogen mustard N-oxide | Ethanamine, 2-chloro-N-(2-chloroethyl)-N-methyl-, N-oxide | 126-85-2 | |
Nitrogen mustard, N-oxide, hydrochloride salt | |||
Nitroglycerin | 1,2,3-Propanetriol, trinitrate | 55-63-0 | P081
|
p-Nitrophenol | Phenol, 4-nitro- | 100-02-7 | U170
|
2-Nitropropane | Propane, 2-nitro- | 79-46-9 | U171
|
Nitrosamines, N.O.S. | 35576-91-1 | ||
N-Nitrosodi-n-butylamine | 1-Butanamine, N-butyl-N-nitroso- | 924-16-3 | U172
|
N-Nitrosodiethanolamine | Ethanol, 2,2'-(nitrosoimino)bis- | 1116-54-7 | U173
|
N-Nitrosodiethylamine | Ethanamine, N-ethyl-N-nitroso- | 55-18-5 | U174
|
N-Nitrosodimethylamine | Methanamine, N-methyl-N-nitroso- | 62-75-9 | P082
|
N-Nitroso-N-ethylurea | Urea, N-ethyl-N-nitroso- | 759-73-9 | U176
|
N-Nitrosomethylethylamine | Ethanamine, N-methyl-N-nitroso- | 10595-95-6 | |
N-Nitroso-N-methylurea | Urea, N-methyl-N-nitroso- | 684-93-5 | U177
|
N-Nitroso-N-methylurethane | Carbamic acid, methylnitroso-, ethyl ester | 615-53-2 | U178
|
N-Nitrosomethylvinylamine | Vinylamine, N-methyl-N-nitroso- | 4549-40-0 | P084
|
N-Nitrosomorpholine | Morpholine, 4-nitroso- | 59-89-2 | |
N-Nitrosonornicotine | Pyridine, 3-(1-nitroso-2-pyrrolidinyl)-, (S)- | 16543-55-8 | |
N-Nitrosopiperidine | Piperidine, 1-nitroso- | 100-75-4 | U179
|
N-Nitrosopyrrolidine | Pyrrolidine, 1-nitroso- | 930-55-2 | U180
|
N-Nitrososarcosine | Glycine, N-methyl-N-nitroso- | 13256-22-9 | |
5-Nitro-o-toluidine | Benzenamine, 2-methyl-5-nitro- | 99-55-8 | U181
|
Octachlorodibenzo-p-dioxin (OCDD) | 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin. | 3268-87-9 | |
Octachlorodibenzofuran (OCDF) | 1,2,3,4,6,7,8,9-Octachlorodibenzofuran. | 39001-02-0 | |
Octamethylpyrophosphoramide | Diphosphoramide, octamethyl- | 152-16-9 | P085
|
Osmium tetroxide | Osmium oxide OsO4, (T-4) | 20816-12-0 | P087
|
Oxamyl | Ethanimidothioc acid, 2-(dimethylamino)-N-(((methylamino)carbonyl)oxy)-2-oxo-, methyl ester | 23135-22-0 | P194
|
Paraldehyde | 1,3,5-Trioxane, 2,4,6-trimethyl- | 123-63-7 | U182
|
Parathion | Phosphorothioic acid, O,O-diethyl O-(4-nitrophenyl) ester | 56-38-2 | P089
|
Pebulate | Carbamothioic acid, butylethyl-, S-propyl ester | 1114-71-2 | |
Pentachlorobenzene | Benzene, pentachloro- | 608-93-5 | U183
|
Pentachlorodibenzo-p-dioxins | |||
Pentachlorodibenzofurans | |||
Pentachloroethane | Ethane, pentachloro- | 76-01-7 | U184
|
Pentachloronitrobenzene (PCNB) | Benzene, pentachloronitro- | 82-68-8 | U185
|
Pentachlorophenol | Phenol, pentachloro- | 87-86-5 | See F027
|
Phenacetin | Acetamide, N-(4-ethoxyphenyl)- | 62-44-2 | U187
|
Phenol | Same | 108-95-2 | U188
|
Phenylenediamine | Benzenediamine | 25265-76-3 | |
1,2-Phenylenediamine | 1,2-Benzenediamine | 95–54–5 | |
1,3-Phenylenediamine | 1,3-Benzenediamine | 108–45–2 | |
Phenylmercury acetate | Mercury, (acetato-O)phenyl- | 62-38-4 | P092
|
Phenylthiourea | Thiourea, phenyl- | 103-85-5 | P093
|
Phosgene | Carbonic dichloride | 75-44-5 | P095
|
Phosphine | Same | 7803-51-2 | P096
|
Phorate | Phosphorodithioic acid, O,O-diethyl S-((ethylthio)methyl) ester | 298-02-2 | P094
|
Phthalic acid esters, N.O.S. | |||
Phthalic anhydride | 1,3-Isobenzofurandione | 85-44-9 | U190
|
Physostigmine | Pyrrolo(2,3-b)indol-5-ol, 1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethyl-, methylcarbamate (ester), (3aS-cis)- | 57-47-6 | P204
|
Physostigmine salicylate | Benzoic acid, 2-hydroxy-, compound with (3aS-cis)-1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethylpyrrolo(2,3-b)indol-5-yl methylcarbamate ester (1:1) | 57-64-7 | P188
|
2-Picoline | Pyridine, 2-methyl- | 109-06-8 | U191
|
Polychlorinated biphenyls, N.O.S. | |||
Potassium cyanide | Same | 151-50-8 | P098
|
Potassium dimethyldithiocarbamate | Carbamodithioc acid, dimethyl, potassium salt | 128-03-0 | |
Potassium n-hydroxymethyl-n-methyl-dithiocarbamate | Carbamodithioc acid, (hydroxymethyl)methyl-, monopotassium salt | 51026-28-9 | |
Potassium n-methyldithiocarbamate | Carbamodithioc acid, methyl-monopotassium salt | 137-41-7 | |
Potassium silver cyanide | Argentate(1-), bis(cyano-C)-, potassium) | 506-61-6 | P099
|
Potassium pentachlorophenate | Pentachlorophenol, potassium salt | 7778736 | None
|
Promecarb | Phenol, 3-methyl-5-(1-methylethyl)-, methyl carbamate | 2631-37-0 | P201
|
Pronamide | Benzamide, 3,5-dichloro-N-(1,1-dimethyl-2-propynyl)- | 23950-58-5 | U192
|
1,3-Propane sultone | 1,2-Oxathiolane, 2,2-dioxide | 1120-71-4 | U193
|
Propham | Carbamic acid, phenyl-, 1-methylethyl ester | 122-42-9 | U373
|
Propoxur | Phenol, 2-(1-methylethoxy)-, methylcarbamate | 114-26-1 | U411
|
n-Propylamine | 1-Propanamine | 107-10-8 | U194
|
Propargyl alcohol | 2-Propyn-1-ol | 107-19-7 | P102
|
Propylene dichloride | Propane, 1,2-dichloro- | 78-87-5 | U083
|
1,2-Propylenimine | Aziridine, 2-methyl- | 75-55-8 | P067
|
Propylthiouracil | 4(1H)-Pyrimidinone, 2,3-dihydro-6-propyl-2-thioxo- | 51-52-5 | |
Prosulfocarb | Carbamothioic acid, dipropyl-, S-(phenylmethyl) ester | 52888-80-9 | U387
|
Pyridine | Same | 110-86-1 | U196
|
Reserpine | Yohimban-16-carboxylic acid, 11,17-dimethoxy-18-((3,4,5-trimethoxybenzoyl)oxy)-, methyl ester, (3 b ,16 b ,17 a ,18 b ,20 a )-, | 50-55-5 | U200
|
Resorcinol | 1,3-Benzenediol | 108-46-3 | U201
|
Safrole | 1,3-Benzodioxole, 5-(2-propenyl)- | 94-59-7 | U203
|
Selenium | Same | 7782-49-2 | |
Selenium compounds, N.O.S. | |||
Selenium dioxide | Selenious acid | 7783-00-8 | U204
|
Selenium sulfide | Selenium sulfide SeS2 | 7488-56-4 | U205
|
Selenium, tetrakis(dimethyl-dithiocarbamate | Carbamodithioic acid, dimethyl-, tetraanhydrosulfide with orthothioselenious acid | 144-34-3 | |
Selenourea | Same | 630-10-4 | P103
|
Silver | Same | 7440-22-4 | |
Silver compounds, N.O.S. | |||
Silver cyanide | Silver cyanide AgCN | 506-64-9 | P104
|
Silvex (2,4,5-TP) | Propanoic acid, 2-(2,4,5-trichlorophenoxy)- | 93-72-1 | See F027
|
Sodium cyanide | Sodium cyanide NaCN | 143-33-9 | P106
|
Sodium dibutyldithiocarbamate | Carbamodithioic acid, dibutyl-, sodium salt | 136-30-1 | |
Sodium diethyldithiocarbamate | Carbamodithioic acid, diethyl-, sodium salt | 148-18-5 | |
Sodium dimethyldithiocarbamate | Carbamodithioic acid, dimethyl-, sodium salt | 128-04-1 | |
Sodium pentachlorophenate | Pentachlorophenol, sodium salt | 131522 | None
|
Streptozotocin | D-Glucose, 2-deoxy-2-(((methylnitrosoamino)carbonyl)amino)- | 18883-66-4 | U206
|
Strychnine | Strychnidin-10-one | 57-24-9 | P108
|
Strychnine salts | P108
|
||
Sulfallate | Carbamodithioic acid, diethyl-, 2-chloro-2-propenyl ester | 95-06-7 | |
TCDD | Dibenzo(b,e)(1,4)dioxin, 2,3,7,8-tetrachloro- | 1746-01-6 | |
Tetrabutylthiuram disulfide | Thioperoxydicarbonic diamide, tetrabutyl | 1634-02-2 | |
Tetramethylthiuram monosulfide | Bis(dimethylthiocarbamoyl) sulfide | 97-74-5 | |
1,2,4,5-Tetrachlorobenzene | Benzene, 1,2,4,5-tetrachloro- | 95-94-3 | U207
|
Tetrachlorodibenzo-p-dioxins | |||
Tetrachlorodibenzofurans | |||
Tetrachloroethane, N.O.S. | Ethane, tetrachloro-, N.O.S. | 25322-20-7 | |
1,1,1,2-Tetrachloroethane | Ethane, 1,1,1,2-tetrachloro- | 630-20-6 | U208
|
1,1,2,2-Tetrachloroethane | Ethane, 1,1,2,2-tetrachloro- | 79-34-5 | U209
|
Tetrachloroethylene | Ethene, tetrachloro- | 127-18-4 | U210
|
2,3,4,6-Tetrachlorophenol | Phenol, 2,3,4,6-tetrachloro- | 58-90-2 | See F027
|
2,3,4,6-Tetrachlorophenol, potassium salt | Same | 53535276 | None
|
2,3,4,6-Tetrachlorophenol, sodium salt | Same | 25567559 | None
|
Tetraethyldithiopyrophosphate | Thiodiphosphoric acid, tetraethyl ester | 3689-24-5 | P109
|
Tetraethyl lead | Plumbane, tetraethyl- | 78-00-2 | P110
|
Tetraethylpyrophosphate | Diphosphoric acid, tetraethyl ester | 107-49-3 | P111
|
Tetranitromethane | Methane, tetranitro- | 509-14-8 | P112
|
Thallium | Same | 7440-28-0 | |
Thallium compounds | |||
Thallic oxide | Thallium oxide Tl2O3 | 1314-32-5 | P113
|
Thallium (I) acetate | Acetic acid, thallium (1+) salt | 563-68-8 | U214
|
Thallium (I) carbonate | Carbonic acid, dithallium (1+) salt | 6533-73-9 | U215
|
Thallium (I) chloride | Thallium chloride TlCl | 7791-12-0 | U216
|
Thallium (I) nitrate | Nitric acid, thallium (1+) salt | 10102-45-1 | U217
|
Thallium selenite | Selenious acid, dithallium (1+) salt | 12039-52-0 | P114
|
Thallium (I) sulfate | Sulfuric acid, dithallium (1+) salt | 7446-18-6 | P115
|
Thioacetamide | Ethanethioamide | 62-55-5 | U218
|
Thiodicarb | Ethanimidothioic acid, N,N'-(thiobis((methylimino)carbonyloxy))-bis-, dimethyl ester | 59669-26-0 | U410
|
Thiofanox | 2-Butanone, 3,3-dimethyl-1-(methylthio)-, O-((methylamino)carbonyl)oxime | 39196-18-4 | P045
|
Thiophanate-methyl | Carbamic acid, (1,2-phyenylenebis(iminocarbonothioyl))-bis-, dimethyl ester | 23564-05-8 | U409
|
Thiomethanol | Methanethiol | 74-93-1 | U153
|
Thiophenol | Benzenethiol | 108-98-5 | P014
|
Thiosemicarbazide | Hydrazinecarbothioamide | 79-19-6 | P116
|
Thiourea | Same | 62-56-6 | P219
|
Thiram | Thioperoxydicarbonic diamide ((H2N)C(S))2S2, tetramethyl- | 137-26-8 | U244
|
Tirpate | 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O-((methylamino)carbonyl)oxime | 26419-73-8 | P185
|
Toluene | Benzene, methyl- | 108-88-3 | U220
|
Toluenediamine | Benzenediamine, ar-methyl- | 25376-45-8 | U221
|
Toluene-2,4-diamine | 1,3-Benzenediamine, 4-methyl- | 95-80-7 | |
Toluene-2,6-diamine | 1,3-Benzenediamine, 2-methyl- | 823-40-5 | |
Toluene-3,4-diamine | 1,2-Benzenediamine, 4-methyl- | 496-72-0 | |
Toluene diisocyanate | Benzene, 1,3-diisocyanatomethyl- | 26471-62-5 | U223
|
o-Toluidine | Benzenamine, 2-methyl- | 95-53-4 | U328
|
o-Toluidine hydrochloride | Benzeneamine, 2-methyl-, hydrochloride | 636-21-5 | U222
|
p-Toluidine | Benzenamine, 4-methyl- | 106-49-0 | U353
|
Toxaphene | Same | 8001-35-2 | P123
|
Triallate | Carbamothioic acid, bis(1-methylethyl)-, S-(2,3,3-trichloro-2-propenyl) ester | 2303-17-5 | U389
|
1,2,4-Trichlorobenzene | Benzene, 1,2,4-trichloro- | 120-82-1 | |
1,1,2-Trichloroethane | Ethane, 1,1,2-trichloro- | 79-00-5 | U227
|
Trichloroethylene | Ethene, trichloro- | 79-01-6 | U228
|
Trichloromethanethiol | Methanethiol, trichloro- | 75-70-7 | P118
|
Trichloromonofluoromethane | Methane, trichlorofluoro- | 75-69-4 | U121
|
2,4,5-Trichlorophenol | Phenol, 2,4,5-trichloro- | 95-95-4 | See F027
|
2,4,6-Trichlorophenol | Phenol, 2,4,6-trichloro- | 88-06-2 | See F027
|
2,4,5-T | Acetic acid, (2,4,5-trichlorophenoxy)- | 93-76-5 | See F027
|
Trichloropropane, N.O.S. | 25735-29-9 | ||
1,2,3-Trichloropropane | Propane, 1,2,3-trichloro- | 96-18-4 | |
Triethylamine | Ethanamine, N,N-diethyl- | 121-44-8 | U404
|
O,O,O-Triethylphosphorothioate | Phosphorothioic acid, O,O,O-triethyl ester | 126-68-1 | |
1,3,5-Trinitrobenzene | Benzene, 1,3,5-trinitro- | 99-35-4 | U234
|
Tris(l-aziridinyl)phosphine sulfide | Aziridine, 1,1',1”-phosphinothioylidynetris- | 52-24-4 | |
Tris(2,3-dibromopropyl) phosphate | 1-Propanol, 2,3-dibromo-, phosphate (3:1) | 126-72-7 | U235
|
Trypan blue | 2,7-Naphthalenedisulfonic acid, 3,3'-((3,3'-dimethyl(1,1'-biphenyl)-4,4'-diyl)bis(azo))bis(5-amino-4-hydroxy)-, tetrasodium salt | 72-57-1 | U236
|
Uracil mustard | 2,4-(1H,3H)-Pyrimidinedione, 5-(bis(2-chloroethyl)amino)- | 66-75-1 | U237
|
Vanadium pentoxide | Vanadium oxide V2O5 | 1314-62-1 | P120
|
Vernolate | Carbamothioc acid, dipropyl-, S-propyl ester | 1929-77-7 | |
Vinyl chloride | Ethene, chloro- | 75-01-4 | U043
|
Warfarin | 2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, when present at concentrations less than 0.3 percent | 81-81-2 | U248
|
Warfarin | 2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, when present at concentrations greater than 0.3 percent | 81-81-2 | P001
|
Warfarin salts, when present at concentrations less than 0.3 percent | U248
|
||
Warfarin salts, when present at concentrations greater than 0.3 percent | P001
|
||
Zinc cyanide | Zinc cyanide Zn(CN)2 | 557-21-1 | P121
|
Zinc phosphide | Zinc phosphide P2Zn3, when present at concentrations greater than 10 percent | 1314-84-7 | P122
|
Zinc phosphide | Zinc phosphide P2Zn3, when present at concentrations of 10 percent or less | 1314-84-7 | U249
|
Ziram | Zinc, bis(dimethylcarbamodithioato-S,S')- (T-4)- | 137-30-4 | P205
|
Facility Address | Waste Description |
(None excluded from an Illinois source at this time) |
Facility Address | Waste Description |
Amoco Oil Company
Wood River, Illinois |
150 million gallons of DAF float from petroleum refining contained in four surge ponds after treatment with the Chemfix stabilization process. This waste contains USEPA hazardous waste number K048. This exclusion applies to the 150 million gallons of waste after chemical stabilization as long as the mixing ratios of the reagent with the waste are monitored continuously and do not vary outside of the limits presented in the demonstration samples and one grab sample is taken each hour from each treatment unit, composited, and TCLP tests performed on each sample. If the levels of lead or total chromium exceed 0.5 ppm in the EP extract, then the waste that was processed during the compositing period is considered hazardous; the treatment residue must be pumped into bermed cells to ensure that the waste is identifiable in the event that removal is necessary. |
Conversion Systems, Inc.
Horsham, Pennsylvania (Sterling, Illinois operations) |
Chemically stabilized electric arc furnace dust (CSEAFD) that is generated by Conversion Systems, Inc. (CSI) (using the Super Detox® treatment process, as modified by CSI to treat electric arc furnace dust (EAFD) (USEPA hazardous waste no. K061)), at the following site and which is disposed of in a RCRA Subtitle D municipal solid waste landfill (MSWLF): Northwestern Steel, Sterling, Illinois.
CSI must implement a testing program for each site that meets the following conditions: 1. Verification testing requirements: Sample collection and analyses, including quality control procedures, must be performed using appropriate methods. As applicable to the method-defined parameters of concern, analyses requiring the use of methods in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a), must be used without substitution. As applicable, the EPA-530/SW-846 methods might include Methods 0010, 0011, 0020, 0023A, 0030, 0031, 0040, 0050, 0051, 0060, 0061, 1010A, 1020B, 1110A, 1310B, 1311, 1312, 1320, 1330A, 9010C, 9012B, 9040C, 9045D, 9060A, 9070A (uses USEPA Method 1664, Rev. A), 9071B, and 9095B. A. Initial verification testing: During the first 20 days of full-scale operation of a newly-constructed Super Detox® treatment facility, CSI must analyze a minimum of four composite samples of CSEAFD representative of the full 20-day period. Composite samples must be composed of representative samples collected from every batch generated. The CSEAFD samples must be analyzed for the constituents listed in condition 3 below. CSI must report the operational and analytical test data, including quality control information, obtained during this initial period no later than 60 days after the generation of the first batch of CSEAFD. B. Addition of new Super Detox® treatment facilities to the exclusion: Option 1: If USEPA approves additional facilities, CSI may petition the Board for identical-in substance amendment of this exclusion pursuant to Section 22.4 for the Act and 35 Ill. Adm. Code 102 and 720.120(a), or Option 2: If USEPA has not approved such amendment, CSI may petition the Board for amendment pursuant to the general rulemaking procedures of Section 27 of the Act and 35 Ill. Adm. Code 102 and 720.120(b); or Option 3: Alternatively to options 1 or 2 above, CSI may petition the Board for a hazardous waste delisting pursuant to Section 28.1 of the Act and Subpart D of 35 Ill. Adm. Code 104 and 35 Ill. Adm. Code 720.122. If CSI pursues general rulemaking (option 2 above) or hazardous waste delisting (option 3 above), it must demonstrate that the CSEAFD generated by a specific Super Detox® treatment facility consistently meets the delisting levels specified in condition 3 below. C. Subsequent verification testing: For the approved facility, CSI must collect and analyze at least one composite sample of CSEAFD each month. The composite samples must be composed of representative samples collected from all batches treated in each month. These monthly representative samples must be analyzed, prior to the disposal of the CSEAFD, for the constituents listed in condition 3 below. CSI may, at its discretion, analyze composite samples gathered more frequently to demonstrate that smaller batches of waste are non-hazardous. 2. Waste holding and handling: CSI must store as hazardous all CSEAFD generated until verification testing, as specified in condition 1A or 1C above, as appropriate, is completed and valid analyses demonstrate that condition 3 below is satisfied. If the levels of constituents measured in the samples of CSEAFD do not exceed the levels set forth in condition 3, then the CSEAFD is non-hazardous and may be disposed of in a RCRA Subtitle D municipal solid waste landfill. If constituent levels in a sample exceed any of the delisting levels set forth in condition 3 below, the CSEAFD generated during the time period corresponding to this sample must be retreated until it meets these levels or managed and disposed of as hazardous waste, in accordance with 35 Ill. Adm. Code 702 through 705, 720 through 728, 733, 738, and 739. CSEAFD generated by a new CSI treatment facility must be managed as a hazardous waste prior to the addition of the name and location of the facility to this exclusion pursuant to condition 1C above. After addition of the new facility to the exclusion pursuant to condition 1B above, CSEAFD generated during the verification testing in condition 1A is also non-hazardous if the delisting levels in condition 3 are satisfied. 3. Delisting levels: All leachable concentrations for metals must not exceed the following levels (in parts per million (ppm)): antimony—0.06; arsenic—0.50; barium—7.6; beryllium—0.010; cadmium—0.050; chromium—0.33; lead—0.15; mercury—0.009; nickel—1; selenium—0.16; silver—0.30; thallium—0.020; vanadium—2; and zinc—70. Metal concentrations must be measured in the waste leachate by the method specified in Section 721.124. 4. Changes in operating conditions: After initiating subsequent testing, as described in condition 1C, if CSI significantly changes the stabilization process established pursuant to condition 1 (e.g., use of new stabilization reagents), CSI must seek amendment of this exclusion using one of the options set forth in condition 1B above. After written amendment of this exclusion, CSI may manage CSEAFD wastes generated from the new process as non-hazardous if the wastes meet the delisting levels set forth in condition 3 above. 5. Data submittals: At least one month prior to operation of a new Super Detox® treatment facility, CSI must notify the Agency in writing when the Super Detox® treatment facility is scheduled to be on-line. The data obtained through condition 1A must be submitted to the Agency within the time period specified. Records of operating conditions and analytical data from condition 1 must be compiled, summarized, and maintained on site for a minimum of five years. These records and data must be furnished to the Agency upon request and made available for inspection. Failure to submit the required data within the specified time period or to maintain the required records on site for the specified time will be considered a violation of the Act and Board regulations. All data submitted must be accompanied by a signed copy of the following certification statement to attest to the truth and accuracy of the data submitted: “Under civil and criminal penalty of law for the making or submission of false or fraudulent statements or representations, I certify that the information contained in or accompanying this document is true, accurate, and complete. “As to (those) identified section(s) of this document for which I cannot personally verify its (their) truth and accuracy, I certify as the company official having supervisory responsibility for the persons who, acting under my direct instructions, made the verification that this information is true, accurate, and complete. “In the event that any of this information is determined by the Board or a court of law to be false, inaccurate, or incomplete, and upon conveyance of this fact to the company, I recognize and agree that this exclusion of waste will be void as if it never had effect or to the extent directed by the Board or court and that the company will be liable for any actions taken in contravention of the company’s obligations under the federal RCRA and Comprehensive Environmental Response, Compensation and Liability Act (42 USC 9601 et seq.) and corresponding provisions of the Act premised upon the company’s reliance on the void exclusion.” BOARD NOTE: The obligations of this exclusion are derived from but also distinct from the obligations under the corresponding federally-granted exclusion of table 2 of appendix IX to 40 CFR 261. |
Facility Address | Waste Description |
(None excluded from an Illinois source at this time) |
Chemical name | CAS No | Concentration limit (mg/kg at 10,000 Btu/lb) | Minimum required detection limit (mg/kg) |
Total Nitrogen as N | NA
|
4,900
|
|
Total Halogens as Cl | NA
|
540
|
|
Total Organic Halogens as Cl | NA
|
(Note 1)
|
|
Polychlorinated biphenyls, total (Aroclors, total) | 1336-36-3
|
ND
|
1.4
|
Cyanide, total | 57-12-5
|
ND
|
1.0
|
Metals: | |||
Antimony, total | 7440-36-0
|
12
|
|
Arsenic, total | 7440-38-2
|
0.23
|
|
Barium, total | 7440-39-3
|
23
|
|
Beryllium, total | 7440-41-7
|
1.2
|
|
Cadmium, total | 7440-43-9
|
1.2
|
|
Chromium, total | 7440-47-3
|
2.3
|
|
Cobalt | 7440-48-4
|
4.6
|
|
Lead, total | 7439-92-1
|
31
|
|
Manganese | 7439-96-5
|
1.2
|
|
Mercury, total | 7439-97-6
|
0.25
|
|
Nickel, total | 7440-02-0
|
58
|
|
Selenium, total | 7782-49-2
|
0.23
|
|
Silver, total | 7440-22-4
|
2.3
|
|
Thallium, total | 7440-28-0
|
23
|
|
Hydrocarbons: | |||
Benzo(a)anthracene | 56-55-3
|
2,400
|
|
Benzene | 71-43-2
|
4,100
|
|
Benzo(b)fluoranthene | 205-99-2
|
2,400
|
|
Benzo(k)fluoranthene | 207-08-9
|
2,400
|
|
Benzo(a)pyrene | 50-32-8
|
2,400
|
|
Chrysene | 218-01-9
|
2,400
|
|
Dibenz(a,h)anthracene | 53-70-3
|
2,400
|
|
7,12-Dimethylbenz(a)anthracene | 57-97-6
|
2,400
|
|
Fluoranthene | 206-44-0
|
2,400
|
|
Indeno(1,2,3-cd)pyrene | 193-39-5
|
2,400
|
|
3-Methylcholanthrene | 56-49-5
|
2,400
|
|
Naphthalene | 91-20-3
|
3,200
|
|
Toluene | 108-88-3
|
36,000
|
|
Oxygenates: | |||
Acetophenone | 98-86-2
|
2,400
|
|
Acrolein | 107-02-8
|
39
|
|
Allyl alcohol | 107-18-6
|
30
|
|
Bis(2-ethylhexyl)phthalate
(Di(2-ethylhexyl) phthalate) |
117-81-7
|
2,400
|
|
Butyl benzyl phthalate | 85-68-7
|
2,400
|
|
o-Cresol
(2-Methyl phenol) |
95-48-7
|
2,400
|
|
m-Cresol
(3-Methyl phenol) |
108-39-4
|
2,400
|
|
p-Cresol
(4-Methyl phenol) |
106-44-5
|
2,400
|
|
Di-n-butyl phthalate | 84-74-2
|
2,400
|
|
Diethyl phthalate | 84-66-2
|
2,400
|
|
2,4-Dimethylphenol | 105-67-9
|
2,400
|
|
Dimethyl phthalate | 131-11-3
|
2,400
|
|
Di-n-octyl phthalate | 117-84-0
|
2,400
|
|
Endothall | 145-73-3
|
100
|
|
Ethyl methacrylate | 97-63-2
|
39
|
|
2-Ethoxyethanol
(Ethylene glycol monoethyl ether) |
110-80-5
|
100
|
|
Isobutyl alcohol | 78-83-1
|
39
|
|
Isosafrole | 120-58-1
|
2,400
|
|
Methyl ethyl ketone
(2-Butanone) |
78-93-3
|
39
|
|
Methyl methacrylate | 80-62-6
|
39
|
|
1,4-Naphthoquinone | 130-15-4
|
2,400
|
|
Phenol | 108-95-2
|
2,400
|
|
Propargyl alcohol
(2-Propyn-l-ol) |
107-19-7
|
30
|
|
Safrole | 94-59-7
|
2,400
|
|
Sulfonated Organics: | |||
Carbon disulfide | 75-15-0
|
ND
|
39
|
Disulfoton | 298-04-4
|
ND
|
2,400
|
Ethyl methanesulfonate | 62-50-0
|
ND
|
2,400
|
Methyl methanesulfonate | 66-27-3
|
ND
|
2,400
|
Phorate | 298-02-2
|
ND
|
2,400
|
1,3-Propane sultone | 1120-71-4
|
ND
|
100
|
Tetraethyldithiopyrophosphate
(Sulfotepp) |
3689-24-5
|
ND
|
2,400
|
Thiophenol
(Benzenethiol) |
108-98-5
|
ND
|
30
|
O,O,O-Triethyl phosphorothioate | 126-68-1
|
ND
|
2,400
|
Nitrogenated Organics: | |||
Acetonitrile (Methyl cyanide) | 75-05-8
|
ND
|
39
|
2-Acetylaminofluorene (2-AAF) | 53-96-3
|
ND
|
2,400
|
Acrylonitrile | 107-13-1
|
ND
|
39
|
4-Aminobiphenyl | 92-67-1
|
ND
|
2,400
|
4-Aminopyridine | 504-24-5
|
ND
|
100
|
Aniline | 62-53-3
|
ND
|
2,400
|
Benzidine | 92-87-5
|
ND
|
2,400
|
Dibenz(a,j)acridine | 224-42-0
|
ND
|
2,400
|
O,O-Diethyl O-pyrazinyl phosphoro-thioate
(Thionazin) |
297-97-2
|
ND
|
2,400
|
Dimethoate | 60-51-5
|
ND
|
2,400
|
p-(Dimethylamino)azobenzene
(4-Dimethylaminoazobenzene) |
60-11-7
|
ND
|
2,400
|
3,3'-Dimethylbenzidine | 119-93-7
|
ND
|
2,400
|
α,α-Dimethylphenethylamine | 122-09-8
|
ND
|
2,400
|
3,3'-Dimethoxybenzidine | 119-90-4
|
ND
|
100
|
1,3-Dinitrobenzene
(m-Dinitrobenzene) |
99-65-0
|
ND
|
2,400
|
4,6-Dinitro-o-cresol | 534-52-1
|
ND
|
2,400
|
2,4-Dinitrophenol | 51-28-5
|
ND
|
2,400
|
2,4-Dinitrotoluene | 121-14-2
|
ND
|
2,400
|
2,6-Dinitrotoluene | 606-20-2
|
ND
|
2,400
|
Dinoseb
(2-sec-Butyl-4,6-dinitrophenol) |
88-85-7
|
ND
|
2,400
|
Diphenylamine | 122-39-4
|
ND
|
2,400
|
Ethyl carbamate
(Urethane) |
51-79-6
|
ND
|
100
|
Ethylenethiourea
(2-Imidazolidinethione) |
96-45-7
|
ND
|
110
|
Famphur | 52-85-7
|
ND
|
2,400
|
Methacrylonitrile | 126-98-7
|
ND
|
39
|
Methapyrilene | 91-80-5
|
ND
|
2,400
|
Methomyl | 16752-77-5
|
ND
|
57
|
2-Methyllactonitrile
(Acetone cyanohydrin ) |
75-86-5
|
ND
|
100
|
Methyl parathion | 298-00-0
|
ND
|
2,400
|
MNNG
(N-Metyl-N-nitroso-N'-nitroguanidine) |
70-25-7
|
ND
|
110
|
1-Naphthylamine
( a -Naphthylamine] |
134-32-7
|
ND
|
2,400
|
2-Naphthylamine
( b -Naphthylamine) |
91-59-8
|
ND
|
2,400
|
Nicotine | 54-11-5
|
ND
|
100
|
4-Nitroaniline
(p-Nitroaniline) |
100-01-6
|
ND
|
2,400
|
Nitrobenzene | 98-95-3
|
ND
|
2,400
|
p-Nitrophenol
(4-Nitrophenol) |
100-02-7
|
ND
|
2,400
|
5-Nitro-o-toluidine | 99-55-8
|
ND
|
2,400
|
N-Nitrosodi-n-butylamine | 924-16-3
|
ND
|
2,400
|
N-Nitrosodiethylamine | 55-18-5
|
ND
|
2,400
|
N-Nitrosodiphenylamine
(Diphenylnitrosamine) |
86-30-6
|
ND
|
2,400
|
N-Nitroso-N-methylethylamine | 10595-95-6
|
ND
|
2,400
|
N-Nitrosomorpholine | 59-89-2
|
ND
|
2,400
|
N-Nitrosopiperidine | 100-75-4
|
ND
|
2,400
|
N-Nitrosopyrrolidine | 930-55-2
|
ND
|
2,400
|
2-Nitropropane | 79-46-9
|
ND
|
30
|
Parathion | 56-38-2
|
ND
|
2,400
|
Phenacetin | 62-44-2
|
ND
|
2,400
|
1,4-Phenylene diamine
(p-Phenylenediamine) |
106-50-3
|
ND
|
2,400
|
N-Phenylthiourea | 103-85-5
|
ND
|
57
|
2-Picoline
(α-Picoline) |
109-06-8
|
ND
|
2,400
|
Propythioracil
(6-Propyl-2-thiouracil) |
51-52-5
|
ND
|
100
|
Pyridine | 110-86-1
|
ND
|
2,400
|
Strychnine | 57-24-9
|
ND
|
100
|
Thioacetamide | 62-55-5
|
ND
|
57
|
Thiofanox | 39196-18-4
|
ND
|
100
|
Thiourea | 62-56-6
|
ND
|
57
|
Toluene-2,4-diamine
(2,4-Diaminotoluene) |
95-80-7
|
ND
|
57
|
Toluene-2,6-diamine
(2,6-Diaminotoluene) |
823-40-5
|
ND
|
57
|
o-Toluidine | 95-53-4
|
ND
|
2,400
|
p-Toluidine | 106-49-0
|
ND
|
100
|
1,3,5-Trinitrobenzene
(sym-Trinitrobenzene) |
99-35-4
|
ND
|
2,400
|
Halogenated Organics: | |||
Allyl chloride | 107-05-1
|
ND
|
39
|
Aramite | 140-57-8
|
ND
|
2,400
|
Benzal chloride
(Dichloromethyl benzene) |
98-87-3
|
ND
|
100
|
Benzyl chloride | 100-44-77
|
ND
|
100
|
bis(2-Chloroethyl)ether
(Dichloroethyl ether) |
111-44-4
|
ND
|
2,400
|
Bromoform
(Tribromomethane) |
75-25-2
|
ND
|
39
|
Bromomethane
(Methyl bromide) |
74-83-9
|
ND
|
39
|
4-Bromophenyl phenyl ether
(p-Bromodiphenyl ether) |
101-55-3
|
ND
|
2,400
|
Carbon tetrachloride | 56-23-5
|
ND
|
39
|
Chlordane | 57-74-9
|
ND
|
14
|
p-Chloroaniline | 106-47-8
|
ND
|
2,400
|
Chlorobenzene | 108-90-7
|
ND
|
39
|
Chlorobenzilate | 510-15-6
|
ND
|
2,400
|
p-Chloro-m-cresol | 59-50-7
|
ND
|
2,400
|
2-Chloroethyl vinyl ether | 110-75-8
|
ND
|
39
|
Chloroform | 67-66-3
|
ND
|
39
|
Chloromethane
(Methyl chloride) |
74-87-3
|
ND
|
39
|
2-Chloronaphthalene
(β-Chlorophthalene) |
91-58-7
|
ND
|
2,400
|
2-Chlorophenol
(o-Chlorophenol) |
95-57-8
|
ND
|
2,400
|
Chloroprene
(2-Chloro-1,3-butadiene) |
1126-99-8
|
ND
|
39
|
2,4-D
(2,4-Dichlorophenoxyacetic acid) |
94-75-7
|
ND
|
7.0
|
Diallate | 2303-16-4
|
ND
|
2,400
|
1,2-Dibromo-3-chloropropane | 96-12-8
|
ND
|
39
|
1,2-Dichlorobenzene
(o-Dichlorobenzene) |
95-50-1
|
ND
|
2,400
|
1,3-Dichlorobenzene
(m-Dichlorobenzene) |
541-73-1
|
ND
|
2,400
|
1,4-Dichlorobenzene
(p-Dichlorobenzene) |
106-46-7
|
ND
|
2,400
|
3,3'-Dichlorobenzidine | 91-94-1
|
ND
|
2,400
|
Dichlorodifluoromethane
(CFC-12) |
75-71-8
|
ND
|
39
|
1,2-Dichloroethane
(Ethylene dichloride) |
107-06-2
|
ND
|
39
|
1,1-Dichloroethylene
(Vinylidene chloride) |
75-35-4
|
ND
|
39
|
Dichloromethoxy ethane
(bis(2-Chloroethoxy)methane) |
111-91-1
|
ND
|
2,400
|
2,4-Dichlorophenol | 120-83-2
|
ND
|
2,400
|
2,6-Dichlorophenol | 87-65-0
|
ND
|
2,400
|
1,2-Dichloropropane
(Propylene dichloride) |
78-87-5
|
ND
|
39
|
cis-1,3-Dichloropropylene | 10061-01-5
|
ND
|
39
|
trans-1,3-Dichloropropylene | 10061-02-6
|
ND
|
39
|
1,3-Dichloro-2-propanol | 96-23-1
|
ND
|
30
|
Endosulfan I | 959-98-8
|
ND
|
1.4
|
Endosulfan II | 33213-65-9
|
ND
|
1.4
|
Endrin | 72-20-8
|
ND
|
1.4
|
Endrin aldehyde | 7421-93-4
|
ND
|
1.4
|
Endrin Ketone | 53494-70-5
|
ND
|
1.4
|
Epichlorohydrin
(1-Chloro-2,3-epoxy propane) |
106-89-8
|
ND
|
30
|
Ethylidene dichloride
(1,1-Dichloroethane) |
75-34-3
|
ND
|
39
|
2-Fluoroacetamide | 640-19-7
|
ND
|
100
|
Heptachlor | 76-44-8
|
ND
|
1.4
|
Heptachlor epoxide | 1024-57-3
|
ND
|
2.8
|
Hexachlorobenzene | 118-74-1
|
ND
|
2,400
|
Hexachloro-1,3-butadiene
(Hexachlorobutadiene) |
87-68-3
|
ND
|
2,400
|
Hexachlorocyclopentadiene | 77-47-4
|
ND
|
2,400
|
Hexachloroethane | 67-72-1
|
ND
|
2,400
|
Hexachlorophene | 70-30-4
|
ND
|
59,000
|
Hexachloropropene
(Hexachloropropylene) |
1888-71-7
|
ND
|
2,400
|
Isodrin | 465-73-6
|
ND
|
2,400
|
Kepone
(Chlordecone) |
143-50-0
|
ND
|
4,700
|
Lindane
(γ-Hexachlorocyclohexane) (γ-BHC) |
58-89-9
|
ND
|
1.4
|
Methylene chloride
(Dichloromethane) |
75-09-2
|
ND
|
39
|
4,4'-methylene-bis(2-chloroaniline) | 101-14-4
|
ND
|
100
|
Methyl iodide
(Iodomethane) |
74-88-4
|
ND
|
39
|
Pentachlorobenzene | 608-93-5
|
ND
|
2,400
|
Pentachloroethane | 76-01-7
|
ND
|
39
|
Pentachloronitrobenzene
(PCNB) (Quintobenzene) (Quintozene) |
82-68-8
|
ND
|
2,400
|
Pentachlorophenol | 87-86-5
|
ND
|
2,400
|
Pronamide | 23950-58-5
|
ND
|
2,400
|
Silvex
(2,4,5-Trichlorophenoxypropionic acid) |
93-72-1
|
ND
|
7.0
|
2,3,7,8-Tetrachlorodibenzo-p-dioxin
(2,3,7,8-TCDD) |
1746-01-6
|
ND
|
30
|
1,2,4,5-Tetrachlorobenzene | 95-94-3
|
ND
|
2,400
|
1,1,2,2-Tetrachloroethane | 79-34-5
|
ND
|
39
|
Tetrachloroethylene
(Perchloroethylene) |
127-18-4
|
ND
|
39
|
2,3,4,6-Tetrachlorophenol | 58-90-2
|
ND
|
2,400
|
1,2,4-Trichlorobenzene | 120-82-1
|
ND
|
2,400
|
1,1,1-Trichloroethane
(Methyl chloroform) |
71-55-6
|
ND
|
39
|
1,1,2-Trichloroethane
(Vinyl trichloride) |
79-00-5
|
ND
|
39
|
Trichloroethylene | 79-01-6
|
ND
|
39
|
Trichlorofluoromethane
(Trichloromonofluoromethane) |
75-69-4
|
ND
|
39
|
2,4,5-Trichlorophenol | 95-95-4
|
ND
|
2,400
|
2,4,6-Trichlorophenol | 88-06-2
|
ND
|
2,400
|
1,2,3-Trichloropropane | 96-18-4
|
ND
|
39
|
Vinyl Chloride | 75-01-4
|
ND
|
39
|
1 | 2 | 3 | 4 | |
Use constituting disposal | Burning for energy recovery or use to produce a fuel | Reclamation (except as provided in Sections 721.102(a)(2)(B) or 721.104(a)(17), (a)(23), (a)(24), or (a)(25)) | Speculative accumulation | |
Applicable Subsection of Section 721.102: | (c)(1) | (c)(2) | (c)(3) | (c)(4) |
Spent materials | Yes | Yes | Yes | Yes |
Sludges (listed in Section 721.131 or 721.132) | Yes | Yes | Yes | Yes |
Sludges exhibiting a characteristic of hazardous waste | Yes | Yes | No | Yes |
By-products (listed in Section 721.131 or 721.132) | Yes | Yes | Yes | Yes |
By-products exhibiting a characteristic of hazardous waste | Yes | Yes | No | Yes |
Commercial chemical products listed in Section 721.133 | Yes | Yes | No | No |
Scrap metal that is not excluded pursuant to Section 721.104(a)(13) | Yes | Yes | Yes | Yes |