Table
| IN THE MATTER OF: | ) | |
| RCRA SUBTITLE C UPDATE, USEPA AMENDMENTS (January 1, 2008 through June 30, 2008) | )
) ) |
R09-3
(Identical-in-Substance Rulemaking - Public Water Supply) |
| 720.101 | Purpose, Scope, and Applicability |
| 720.102 | Availability of Information; Confidentiality of Information |
| 720.103 | Use of Number and Gender |
| 720.104 | Electronic Reporting |
| 720.110 | Definitions |
| 720.111 | References |
| 720.120 | Rulemaking |
| 720.121 | Alternative Equivalent Testing Methods |
| 720.122 | Waste Delisting |
| 720.123 | Petitions for Regulation as Universal Waste |
| 720.130 | Procedures for Solid Waste Determinations |
| 720.131 | Solid Waste Determinations |
| 720.132 | Boiler Determinations |
| 720.133 | Procedures for Determinations |
| 720.140 | Additional Regulation of Certain Hazardous Waste Recycling Activities on a Case-by-Case Basis |
| 720.141 | Procedures for Case-by-Case Regulation of Hazardous Waste Recycling Activities |
| 720.Appendix A | Overview of Federal RCRA Subtitle C (Hazardous Waste) Regulations |
| Section 720.110 | Definitions |
| Section 720.111 | References |
| a) | Non-Regulatory Government Publications and Publications of Recognized Organizations and Associations: |
| b) | Code of Federal Regulations. Available from the Superintendent of Documents, U.S. Government Printing Office, Washington, D.C. 20401, 202-783-3238: |
| c) | Federal Statutes: |
| d) | This Section incorporates no later editions or amendments. |
| Section 720.122 | Waste Delisting |
| a) | Any person seeking to exclude a waste from a particular generating facility from the lists in Subpart D of 35 Ill. Adm. Code 721 may file a petition, as specified in subsection (n) of this Section. The Board will grant the petition if the following occur: |
| 1) | The petitioner demonstrates that the waste produced by a particular generating facility does not meet any of the criteria under which the waste was listed as a hazardous or acute hazardous waste; and |
| 2) | The Board determines that there is a reasonable basis to believe that factors (including additional constituents) other than those for which the waste was listed could cause the waste to be a hazardous waste, that such factors do not warrant retaining the waste as a hazardous waste. A Board determination under the preceding sentence must be made by reliance on, and in a manner consistent with, “EPA RCRA Delisting Program |
| b) | Listed wastes and mixtures. A person may also petition the Board to exclude from 35 Ill. Adm. Code 721.103(a)(2)(B) or (a)(2)(C), a waste that is described in these Sections and is either a waste listed in Subpart D of 35 Ill. Adm. Code 721, or is derived from a waste listed in that Subpart. This exclusion may only be granted for a particular generating, storage, treatment, or disposal facility. The petitioner must make the same demonstration as required by subsection (a) of this Section. Where the waste is a mixture of a solid waste and one or more listed hazardous wastes or is derived from one or more listed hazardous wastes, the demonstration must be made with respect to the waste mixture as a whole; analyses must be conducted for not only those constituents for which the listed waste contained in the mixture was listed as hazardous, but also for factors (including additional constituents) that could cause the waste mixture to be a hazardous waste. A waste that is so excluded may still be a hazardous waste by operation of Subpart C of 35 Ill. Adm. Code 721. |
| c) | Ignitable, corrosive, reactive and toxicity characteristic wastes. If the waste is listed in codes “I,” “C,” “R,” or “E” in Subpart D of 35 Ill. Adm. Code 721, the following requirements apply: |
| 1) | The petitioner must demonstrate that the waste does not exhibit the relevant characteristic for which the waste was listed, as defined in 35 Ill. Adm. Code 721.121, 721.122, 721.123, or 721.124, using any applicable methods prescribed in those Sections. The petitioner must also show that the waste does not exhibit any of the other characteristics, defined in those Sections, using any applicable methods prescribed in those Sections; and |
| 2) | Based on a complete petition, the Board will determine, if it has a reasonable basis to believe that factors (including additional constituents) other than those for which the waste was listed could cause the waste to be hazardous waste, that such factors do not warrant retaining the waste as a hazardous waste. A Board determination under the preceding sentence must be made by reliance on, and in a manner consistent with, “EPA RCRA Delisting Program |
| d) | Toxic waste. If the waste is listed in code “T” in Subpart D of 35 Ill. Adm. Code 721, the following requirements apply: |
| 1) | The petitioner must demonstrate that the waste fulfills the following criteria: |
| A) | It does not contain the constituent or constituents (as defined in Appendix G of 35 Ill. Adm. Code 721) that caused USEPA to list the waste; or |
| B) | Although containing one or more of the hazardous constituents (as defined in Appendix G of 35 Ill. Adm. Code 721) that caused USEPA to list the waste, the waste does not meet the criterion of 35 Ill. Adm. Code 721.111(a)(3) when considering the factors used in 35 Ill. Adm. Code 721.111(a)(3)(A) through (a)(3)(K) under which the waste was listed as hazardous. |
| 2) | Based on a complete petition, the Board will determine, if it has a reasonable basis to believe that factors (including additional constituents) other than those for which the waste was listed could cause the waste to be hazardous waste, that such factors do not warrant retaining the waste as a hazardous waste. |
| 3) | The petitioner must demonstrate that the waste does not exhibit any of the characteristics, defined in 35 Ill. Adm. Code 721.121, 721.122, 721.123, or 721.124, using any applicable methods prescribed in those Sections. |
| 4) | A waste that is so excluded, however, may still be a hazardous waste by operation of Subpart C of 35 Ill. Adm. Code 721. |
| e) | Acute hazardous waste. If the waste is listed with the code “H” in Subpart D of 35 Ill. Adm. Code 721, the following requirements apply: |
| 1) | The petitioner must demonstrate that the waste does not meet the criterion of 35 Ill. Adm. Code 721.111(a)(2); and |
| 2) | Based on a complete petition, the Board will determine, if it has a reasonable basis to believe that factors (including additional constituents) other than those for which the waste was listed could cause the waste to be hazardous waste, that such factors do not warrant retaining the waste as a hazardous waste. A Board determination under the preceding sentence must be made by reliance on, and in a manner consistent with, “EPA RCRA Delisting Program |
| 3) | The petitioner must demonstrate that the waste does not exhibit any of the characteristics, defined in 35 Ill. Adm. Code 721.121, 721.122, 721.123, or 721.124, using any applicable methods prescribed in those Sections. |
| 4) | A waste that is so excluded, however, may still be a hazardous waste by operation of Subpart C of 35 Ill. Adm. Code 721. |
| f) | This subsection (f) corresponds with 40 CFR 260.22(f), which USEPA has marked “reserved.” This statement maintains structural consistency with the federal regulations. |
| g) | This subsection (g) corresponds with 40 CFR 260.22(g), which USEPA has marked “reserved.” This statement maintains structural consistency with the federal regulations. |
| h) | Demonstration samples must consist of enough representative samples, but in no case less than four samples, taken over a period of time sufficient to represent the variability or the uniformity of the waste. |
| i) | Each petition must include, in addition to the information required by subsection (n) of this Section: |
| 1) | The name and address of the laboratory facility performing the sampling or tests of the waste; |
| 2) | The names and qualifications of the persons sampling and testing the waste; |
| 3) | The dates of sampling and testing; |
| 4) | The location of the generating facility; |
| 5) | A description of the manufacturing processes or other operations and feed materials producing the waste and an assessment of whether such processes, operations, or feed materials can or might produce a waste that is not covered by the demonstration; |
| 6) | A description of the waste and an estimate of the average and maximum monthly and annual quantities of waste covered by the demonstration; |
| 7) | Pertinent data on and discussion of the factors delineated in the respective criterion for listing a hazardous waste, where the demonstration is based on the factors in 35 Ill. Adm. Code 721.111(a)(3); |
| 8) | A description of the methodologies and equipment used to obtain the representative samples; |
| 9) | A description of the sample handling and preparation techniques, including techniques used for extraction, containerization, and preservation of the samples; |
| 10) | A description of the tests performed (including results); |
| 11) | The names and model numbers of the instruments used in performing the tests; and |
| 12) | The following statement signed by the generator or the generator’s authorized representative: |
| j) | After receiving a petition, the Board may request any additional information that the Board needs to evaluate the petition. |
| k) | An exclusion will only apply to the waste generated at the individual facility covered by the demonstration and will not apply to waste from any other facility. |
| l) | The Board will exclude only part of the waste for which the demonstration is submitted if the Board determines that variability of the waste justifies a partial exclusion. |
| m) | Delisting of specific wastes from specific sources that have been adopted by USEPA may be proposed as State regulations that are identical in substance pursuant to Section 720.120(a). |
| n) | Delistings that have not been adopted by USEPA may be proposed to the Board pursuant to a petition for adjusted standard pursuant to Section 28.1 of the Act [415 ILCS 5/28.1] and Subpart D of 35 Ill. Adm. Code 104. The justification for the adjusted standard is as specified in subsections (a) through (g) of this Section, as applicable to the waste in question. The petition must be clearly labeled as a RCRA delisting adjusted standard petition. |
| 1) | In accordance with 35 Ill. Adm. Code 101.304, the petitioner must serve copies of the petition, and any other documents filed with the Board, on USEPA at the following addresses: |
| 2) | The Board will mail copies of all opinions and orders to USEPA at the above addresses. |
| 3) | In conjunction with the normal updating of the RCRA regulations, the Board will maintain, in Appendix I of 35 Ill. Adm. Code 721, a listing of all adjusted standards granted by the Board. |
| o) | The Agency may determine in a permit or a letter directed to a generator that, based on 35 Ill. Adm. Code 721, a waste from a particular source is not subject to these regulations. Such a finding is evidence against the Agency in any subsequent proceedings but will not be conclusive with reference to other persons or the Board. |
| p) | Any petition to delist directed to the Board or request for determination directed to the Agency must include a showing that the waste will be generated or managed in Illinois. |
| q) | The Board will not grant any petition that would render the Illinois RCRA program less stringent than if the decision were made by USEPA. |
| r) | Delistings apply only within Illinois. Generators must comply with 35 Ill. Adm. Code 722 for waste that is hazardous in any state to which it is to be transported. |
| 721.101 | Purpose and Scope |
| 721.102 | Definition of Solid Waste |
| 721.103 | Definition of Hazardous Waste |
| 721.104 | Exclusions |
| 721.105 | Special Requirements for Hazardous Waste Generated by Small Quantity Generators |
| 721.106 | Requirements for Recyclable Materials |
| 721.107 | Residues of Hazardous Waste in Empty Containers |
| 721.108 | PCB Wastes Regulated under TSCA |
| 721.109 | Requirements for Universal Waste |
| 721.110 | Criteria for Identifying the Characteristics of Hazardous Waste |
| 721.111 | Criteria for Listing Hazardous Waste |
| 721.120 | General |
| 721.121 | Characteristic of Ignitability |
| 721.122 | Characteristic of Corrosivity |
| 721.123 | Characteristic of Reactivity |
| 721.124 | Toxicity Characteristic |
| 721.130 | General |
| 721.131 | Hazardous Wastes from Nonspecific Sources |
| 721.132 | Hazardous Waste from Specific Sources |
| 721.133 | Discarded Commercial Chemical Products, Off-Specification Species, Container Residues, and Spill Residues Thereof |
| 721.135 | Wood Preserving Wastes |
| 721.138 | Comparable or Syngas Fuel Exclusion |
| 721.139 | 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 |
| 721.Appendix A | Representative Sampling Methods |
| 721.Appendix B | Method 1311 Toxicity Characteristic Leaching Procedure (TCLP) |
| 721.Appendix C | Chemical Analysis Test Methods |
| 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 |
| 721.Appendix Z | Table to Section 721.102 |
| Section 721.102 | Definition of Solid Waste |
| a) | Solid waste. |
| 1) | A solid waste is any discarded material that is not excluded by Section 721.104(a) or that is not excluded pursuant to 35 Ill. Adm. Code 720.130 and 720.131. |
| 2) | A discarded material is any material that is described as follows: |
| A) | Abandoned, as explained in subsection (b) of this Section; |
| B) | Recycled, as explained in subsection (c) of this Section; |
| C) | Considered inherently waste-like, as explained in subsection (d) of this Section; or |
| D) | A military munition identified as a solid waste in 35 Ill. Adm. Code 726.302. |
| b) | 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 |
| 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 “yes” in column 3 of the table in Appendix Z of this Part is a solid waste when reclaimed (except as provided under Section 721.104(a)(17)). A material noted with a “ |
| 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 solid a 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. |
| Section 721.104 | Exclusions |
| a) | Materials that are not solid wastes. The following materials are not solid wastes for the purpose of this Part: |
| 1) | Sewage. |
| A) | Domestic sewage (untreated sanitary wastes that pass through a sewer system); and |
| B) | Any mixture of domestic sewage and other waste that passes through a sewer system to publicly-owned treatment works for treatment. |
| 2) | Industrial wastewater discharges that are point source discharges with National Pollutant Discharge Elimination System (NPDES) permits issued by the Agency pursuant to Section 12(f) of the Environmental Protection Act [415 ILCS 5/12(f)] and 35 Ill. Adm. Code 309. |
| 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, unless it is accumulated speculatively, as defined in Section 721.101(c). |
| 8) | Secondary materials that are reclaimed and returned to the original process or processes in which they were generated, where they are reused in the production process, provided 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 which are reclaimed and reused for their original intended purpose; |
| B) | Wastewaters from the wood preserving process that have been reclaimed and which are reused to treat wood; and |
| C) | Prior to reuse, the wood preserving wastewaters and spent wood preserving solutions described in subsections (a)(9)(A) and (a)(9)(B) of this Section, so long as they meet all of the following conditions: |
| i) | The wood preserving wastewaters and spent wood preserving solutions are reused on-site at water-borne plants in the production process for their original intended purpose; |
| ii) | Prior to reuse, the wastewaters and spent wood preserving solutions are managed to prevent release to either land or groundwater or both; |
| iii) | Any unit used to manage wastewaters or spent wood preserving solutions prior to reuse can be visually or otherwise determined to prevent such releases; |
| iv) | Any drip pad used to manage the wastewaters or spent wood preserving solutions prior to reuse complies with the standards in 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 pursuant to 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 pursuant to Section 40 of the Act [415 ILCS 5/40]. |
| 10) | Hazardous waste numbers K060, K087, K141, K142, K143, K144, K145, K147, and K148, and any wastes from the coke by-products processes that are hazardous only because they exhibit the toxicity characteristic specified in Section 721.124, when subsequent to generation these materials are recycled to coke ovens, to the tar recovery process as a feedstock to produce coal tar, or are mixed with coal tar prior to the tar’s sale or refining. This exclusion is conditioned on there being no land disposal of the waste from the point it is generated to the point it is recycled to coke ovens, to tar recovery, to the tar refining processes, or prior to when it is mixed with coal. |
| 11) | Nonwastewater splash condenser dross residue from the treatment of hazardous waste number K061 in high temperature metals recovery units, provided it is shipped in drums (if shipped) and not land disposed before recovery. |
| 12) | Certain oil-bearing hazardous secondary materials and recovered oil, as follows: |
| A) | Oil-bearing hazardous secondary materials (i.e., sludges, 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, gasification (as defined in 35 Ill. Adm. Code 720.110), or thermal cracking units (i.e., cokers)), unless the material is placed on the land, or speculatively accumulated before being so recycled. Materials inserted into thermal cracking units are excluded under this subsection (a)(12), provided that the coke product also does not exhibit a characteristic of hazardous waste. Oil-bearing hazardous secondary materials may be inserted into the same petroleum refinery where they are generated or sent directly to another petroleum refinery and still be excluded under this provision. Except as provided in subsection (a)(12)(B) of this Section, oil-bearing hazardous secondary materials generated elsewhere in the petroleum industry (i.e., from sources other than petroleum refineries) are not excluded under this Section. Residuals generated from processing or recycling materials excluded under this subsection (a)(12)(A), where such materials as generated would have otherwise met a listing under Subpart D of this Part, are designated as USEPA hazardous waste number F037 listed wastes when disposed of or intended for disposal. |
| B) | Recovered oil that is recycled in the same manner and with the same conditions as described in subsection (a)(12)(A) of this Section. Recovered oil is oil that has been reclaimed from secondary materials (including wastewater) generated from normal petroleum industry practices, including refining, exploration and production, bulk storage, and transportation incident thereto (SIC codes 1311, 1321, 1381, 1382, 1389, 2911, 4612, 4613, 4922, 4923, 4789, 5171, and 5172). Recovered oil does not include oil-bearing hazardous wastes listed in Subpart D of this Part; however, oil recovered from such wastes may be considered recovered oil. Recovered oil does not include used oil, as defined in 35 Ill. Adm. Code 739.100. |
| 13) | Excluded scrap metal (processed scrap metal, unprocessed home scrap metal, and unprocessed prompt scrap metal) being recycled. |
| 14) | Shredded circuit boards being recycled, provided that they meet the following conditions: |
| A) | The circuit boards are stored in containers sufficient to prevent a release to the environment prior to recovery; and |
| B) | The circuit boards are free of mercury switches, mercury relays, nickel-cadmium batteries, and lithium batteries. |
| 15) | Condensates derived from the overhead gases from kraft mill steam strippers that are used to comply with federal Clean Air Act regulation 40 CFR 63.446(e). The exemption applies only to combustion at the mill generating the condensates. |
| 16) | Comparable fuels or comparable syngas fuels (i.e., comparable or syngas fuels) that meet the requirements of Section 721.138. |
| 17) | Spent materials (as defined in Section 721.101) (other than hazardous wastes listed in Subpart D of this Part) generated within the primary mineral processing industry from which minerals, acids, cyanide, water, or other values are recovered by mineral processing or by benefication, provided that 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) of this Section, 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 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 runon and runoff 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. |
| 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 non-land-based units. This notification must be updated when there is a change in the type of materials recycled or the location of the recycling process. |
| F) | For purposes of subsection (b)(7) of this Section, mineral processing spent materials must be the result of mineral processing and may not include any listed hazardous wastes. Listed hazardous wastes and characteristic hazardous wastes generated by non-mineral processing industries are not eligible for the conditional exclusion from the definition of solid waste. |
| 18) | Petrochemical recovered oil from an associated organic chemical manufacturing facility, where the oil is to be inserted into the petroleum refining process (SIC code 2911) along with normal petroleum refinery process streams, provided that both of the following conditions are true of the oil: |
| A) | The oil is hazardous only because it exhibits the characteristic of ignitability (as defined in Section 721.121) or toxicity for benzene (Section 721.124, USEPA hazardous waste code D018); |
| B) | The oil generated by the organic chemical manufacturing facility is not placed on the land, or speculatively accumulated before being recycled into the petroleum refining process. An “associated organic chemical manufacturing facility” is a facility for which all of the following is true: its primary SIC code is 2869, but its operations may also include SIC codes 2821, 2822, and 2865; it is physically co-located with a petroleum refinery; and the petroleum refinery to which the oil being recycled is returned also provides hydrocarbon feedstocks to the organic chemical manufacturing facility. “Petrochemical recovered oil” is oil that has been reclaimed from secondary materials (i.e., sludges, 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 which 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) of this Section: |
| 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) of this Section. |
| 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) of this Section. |
| 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 which 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) of this Section, 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. |
| 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. |
| 21) | Zinc fertilizers made from hazardous wastes or hazardous secondary materials that are excluded under subsection (a)(20) of this Section, 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
|
| ii) | For dioxin contaminants, the fertilizer must contain no more than eight parts per trillion of dioxin, measured as toxic equivalent (TEQ). |
| 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) of this Section. 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). |
| 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. |
| 2) | Solid wastes generated by any of the following that are returned to the soil as fertilizers: |
| A) | The growing and harvesting of agricultural crops, or |
| B) | The raising of animals, including animal manures. |
| 3) | Mining overburden returned to the mine site. |
| 4) | Fly ash waste, bottom ash waste, slag waste, and flue gas emission control waste generated primarily from the combustion of coal or other fossil fuels, except as provided in 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste. |
| 5) | Drilling fluids, produced waters, and other wastes associated with the exploration, development, or production of crude oil, natural gas, or geothermal energy. |
| 6) | Chromium wastes. |
| A) | Wastes that fail the test for the toxicity characteristic (Section 721.124 and Appendix B to this Part) because chromium is present or which are listed in Subpart D of this Part due to the presence of chromium, that do not fail the test for the toxicity characteristic for any other constituent or which are not listed due to the presence of any other constituent, and that do not fail the test for any other characteristic, if 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) of this Section (so long as they do not fail the test for the toxicity characteristic for any other constituent and do not exhibit any other characteristic): |
| i) | Chrome (blue) trimmings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling; |
| ii) | Chrome (blue) shavings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling; |
| iii) | Buffing dust generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue; |
| iv) | Sewer screenings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling; |
| v) | Wastewater treatment sludges generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling; |
| vi) | Wastewater treatment sludges generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, and through-the-blue; |
| vii) | Waste scrap leather from the leather tanning industry, the shoe manufacturing industry, and other leather product manufacturing industries; and |
| viii) | Wastewater treatment sludges from the production of titanium dioxide pigment using chromium-bearing ores by the chloride process. |
| 7) | Solid waste from the extraction, beneficiation, and processing of ores and minerals (including coal, phosphate rock, and overburden from the mining of uranium ore), except as provided by 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste. |
| A) | For purposes of this subsection (b)(7), beneficiation of ores and minerals is restricted to the following activities: crushing; grinding; washing; dissolution; crystallization; filtration; sorting; sizing; drying; sintering; pelletizing; briquetting; calcining to remove water or carbon dioxide; roasting; autoclaving or chlorination in preparation for leaching (except where the roasting (or autoclaving or chlorination) and leaching sequence produces a final or intermediate product that does not undergo further beneficiation or processing); gravity concentration; magnetic separation; electrostatic separation; floatation; ion exchange; solvent extraction; electrowinning; precipitation; amalgamation; and heap, dump, vat tank, and in situ leaching. |
| B) | For the purposes of this subsection (b)(7), solid waste from the processing of ores and minerals includes only the following wastes as generated: |
| i) | Slag from primary copper processing; |
| ii) | Slag from primary lead processing; |
| iii) | Red and brown muds from bauxite refining; |
| iv) | Phosphogypsum from phosphoric acid production; |
| v) | Slag from elemental phosphorus production; |
| vi) | Gasifier ash from coal gasification; |
| vii) | Process wastewater from coal gasification; |
| viii) | Calcium sulfate wastewater treatment plant sludge from primary copper processing; |
| ix) | Slag tailings from primary copper processing; |
| x) | Fluorogypsum from hydrofluoric acid production; |
| xi) | Process wastewater from hydrofluoric acid production; |
| xii) | Air pollution control dust or sludge from iron blast furnaces; |
| xiii) | Iron blast furnace slag; |
| xiv) | Treated residue from roasting and leaching of chrome ore; |
| xv) | Process wastewater from primary magnesium processing by the anhydrous process; |
| xvi) | Process wastewater from phosphoric acid production; |
| xvii) | Basic oxygen furnace and open hearth furnace air pollution control dust or sludge from carbon steel production; |
| xviii) | Basic oxygen furnace and open hearth furnace slag from carbon steel production; |
| xix) | Chloride processing waste solids from titanium tetrachloride production; and |
| xx) | Slag from primary zinc production. |
| C) | A residue derived from co-processing mineral processing secondary materials with normal beneficiation raw materials or with normal mineral processing raw materials remains excluded under this subsection (b) if the following conditions are fulfilled: |
| i) | The owner or operator processes at least 50 percent by weight normal beneficiation raw materials or normal mineral processing raw materials; and |
| ii) | The owner or operator legitimately reclaims the secondary mineral processing materials. |
| 8) | Cement kiln dust waste, except as provided by 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste. |
| 9) | Solid waste that consists of discarded arsenical-treated wood or wood products that fails the test for the toxicity characteristic for hazardous waste codes D004 through D017 and which is not a hazardous waste for any other reason if the waste is generated by persons that utilize the arsenical-treated wood and wood products for these materials’ intended end use. |
| 10) | Petroleum-contaminated media and debris that fail the test for the toxicity characteristic of Section 721.124 (hazardous waste codes D018 through D043 only) and which are subject to corrective action regulations under 35 Ill. Adm. Code 731. |
| 11) | This subsection (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 of this Part, if these oil filters have been gravity hot-drained using one of the following methods: |
| A) | Puncturing the filter anti-drain back valve or the filter dome end and hot-draining; |
| B) | Hot-draining and crushing; |
| C) | Dismantling and hot-draining; or |
| D) | Any other equivalent hot-draining method that will remove used oil. |
| 14) | Used oil re-refining distillation bottoms that are used as feedstock to manufacture asphalt products. |
| 15) | Leachate or gas condensate collected from landfills where certain solid wastes have been disposed of, under 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 |
| ii) | The solid wastes described in subsection (b)(15)(A)(i) of this Section were disposed of prior to the effective date of the listing (as set forth in that subsection); |
| iii) | The leachate or gas condensate does not exhibit any characteristic of hazardous waste nor is derived from any other listed hazardous waste; and |
| iv) | Discharge of the leachate or gas condensate, including leachate or gas condensate transferred from the landfill to a POTW by truck, rail, or dedicated pipe, is subject to regulation under section 307(b) or 402 of the federal Clean Water Act. |
| B) | Leachate or gas condensate derived from K169, K170, K171, K172, K176, K177, or K178 waste will no longer be exempt if it is stored or managed in a surface impoundment prior to discharge. After February 26, 2007, leachate or gas condensate derived from 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. |
| 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 until it exits the unit in which it was generated, unless the unit is a surface impoundment, or unless the hazardous waste remains in the unit more than 90 days after the unit ceases to be operated for manufacturing or for storage or transportation of product or raw materials. |
| d) | Samples. |
| 1) | Except as provided in subsection (d)(2) of this Section, a sample of solid waste or a sample of water, soil, or air that is collected for the sole purpose of testing to determine its characteristics or composition is not subject to any requirements of this Part or 35 Ill. Adm. Code 702, 703, 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 where further testing of the sample may be necessary). |
| 2) | In order to qualify for the exemption in subsection (d)(1)(A) or (d)(1)(B) of this Section, a sample collector shipping samples to a laboratory and a laboratory returning samples to a sample collector must do the following: |
| A) | Comply with U.S. Department of Transportation (USDOT), U.S. Postal Service (USPS), or any other applicable shipping requirements; or |
| B) | Comply with the following requirements if the sample collector determines that USDOT, USPS, or other shipping requirements do not apply to the shipment of the sample: |
| i) | Assure that the following information accompanies the sample: The sample collector’s name, mailing address, and telephone number; the laboratory’s name, mailing address, and telephone number; the quantity of the sample; the date of the shipment; and a description of the sample; 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) of this Section. |
| e) | Treatability study samples. |
| 1) | Except as is provided in subsection (e)(2) of this Section, a person that generates or collects samples for the purpose of conducting treatability studies, as defined in 35 Ill. Adm. Code 720.110, are not subject to any requirement of 35 Ill. Adm. Code 721 through 723 or to the notification requirements of section 3010 of the Resource Conservation and Recovery Act. Nor are such samples included in the quantity determinations of Section 721.105 and 35 Ill. Adm. Code 722.134(d) when: |
| A) | The sample is being collected and prepared for transportation by the generator or sample collector; |
| B) | The sample is being accumulated or stored by the generator or sample collector prior to transportation to a laboratory or testing facility; or |
| C) | The sample is being transported to the laboratory or testing facility for the purpose of conducting a treatability study. |
| 2) | The exemption in subsection (e)(1) of this Section is applicable to samples of hazardous waste being collected and shipped for the purpose of conducting treatability studies provided that 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) of this Section are met. |
| i) | The transportation of each sample shipment complies with U.S. Department of Transportation (USDOT), U.S. Postal Service (USPS), or any other applicable shipping requirements; or |
| ii) | If the USDOT, USPS, or other shipping requirements do not apply to the shipment of the sample, the following information must accompany the sample: The name, mailing address, and telephone number of the originator of the sample; the name, address, and telephone number of the facility that will perform the treatability study; the quantity of the sample; the date of the shipment; and, a description of the sample, including its USEPA hazardous waste number; |
| D) | The sample is shipped to a laboratory or testing facility that is exempt under subsection (f) of this Section, or has an appropriate RCRA permit or interim status; |
| E) | The generator or sample collector maintains the following records for a period ending three years after completion of the treatability study: |
| i) | Copies of the shipping documents; |
| ii) | A copy of the contract with the facility conducting the treatability study; 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) of this Section in its report under 35 Ill. Adm. Code 722.141. |
| 3) | The Agency may grant requests on a case-by-case basis for up to an additional two years for treatability studies involving bioremediation. The Agency may grant requests, on a case-by-case basis, for quantity limits in excess of those specified in subsections (e)(2)(A), (e)(2)(B), and (f)(4) of this Section, for up to an additional 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) of this Section, subject to the limitations of subsection (e)(3)(C) of this Section: |
| 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 allowed and timeframes allowed in subsections (e)(3)(A) and (e)(3)(B) of this Section are subject to all the provisions in subsections (e)(1) and (e)(2)(B) through (e)(2)(F) of this Section. The generator or sample collector 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) | Final Agency determinations pursuant to this subsection (e) may be appealed to the Board. |
| f) | Samples undergoing treatability studies at laboratories or testing facilities. Samples undergoing treatability studies and the laboratory or testing facility conducting such treatability studies (to the extent such facilities are not otherwise subject to RCRA requirements) are not subject to any requirement of this Part, or of 35 Ill. Adm. Code 702, 703, 722 through 726, and 728 or to the notification requirements of Section 3010 of the Resource Conservation and Recovery Act, provided that the requirements of subsections (f)(1) through (f)(11) of this Section are met. A mobile treatment unit may qualify as a testing facility subject to subsections (f)(1) through (f)(11) of this Section. Where a group of mobile treatment units are located at the same site, the limitations specified in subsections (f)(1) through (f)(11) of this Section apply to the entire group of mobile treatment units collectively as if the group were one mobile treatment unit. |
| 1) | No less than 45 days before conducting treatability studies, the facility notifies the Agency in writing that it intends to conduct treatability studies under this subsection (f). |
| 2) | The laboratory or testing facility conducting the treatability study has a USEPA identification number. |
| 3) | No more than a total of 10,000 kg of “as received” media contaminated with non-acute hazardous waste, 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) of this Section. |
| 11) | The facility notifies the Agency by letter when the facility is no longer planning to conduct any treatability studies at the site. |
| g) | Dredged material that is not a hazardous waste. Dredged material that is subject to the requirements of a permit that has been issued under section 404 of the Federal Water Pollution Control Act (33 USC 1344) is not a hazardous waste. For the purposes of this subsection (g), the following definitions apply: |
| 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 |
| b) | A solid waste that exhibits the characteristic of reactivity has the USEPA hazardous waste number of D003. |
| Section 721.131 | Hazardous Wastes from Nonspecific Sources |
| a) | The following solid wastes are listed hazardous wastes from non-specific sources, unless they are excluded under 35 Ill. Adm. Code 720.120 and 720.122 and listed in Appendix I of this Part. |
| USEPA Hazardous Waste No. | Industry and Hazardous Waste | Hazard Code |
| 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 | Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one restricted waste classified as hazardous under Subpart D. (Leachate resulting from the disposal of one or more of the following USEPA hazardous wastes and no other hazardous wastes retains its USEPA hazardous waste number(s): F020, F021, F022, F026, F027, or F028.) | (T) |
| b) | Listing-specific definitions. |
| 1) | For the purpose of the F037 and F038 listings, “oil/water/solids” is defined as oil or water or solids. |
| 2) | For the purposes of the F037 and F038 listings, the following apply: |
| A) | “Aggressive biological treatment units” are defined as units that employ one of the following four treatment methods: activated sludge, trickling filter, rotating biological contactor for the continuous accelerated biological oxidation of wastewaters, or high-rate aeration. “High-rate aeration” is a system of surface impoundments or tanks in which intense mechanical aeration is used to completely mix the wastes, enhance biological activity, and the following is true: |
| i) | The units employ a minimum of six horsepower per million gallons of treatment volume; and either |
| ii) | The hydraulic retention time of the unit is no longer than five days; or |
| iii) | The hydraulic retention time is no longer than 30 days and the unit does not generate a sludge that is a hazardous waste by the toxicity characteristic. |
| B) | Generators and treatment, storage, or disposal (TSD) facilities have the burden of proving that their sludges are exempt from listing as F037 or F038 wastes under this definition. Generators and TSD facilities must maintain, in their operating or other on site records, documents and data sufficient to prove the following: |
| i) | The unit is an aggressive biological treatment unit, as defined in this subsection; and |
| ii) | The sludges sought to be exempted from F037 or F038 were actually generated in the aggressive biological treatment unit. |
| 3) | Time of generation. For the purposes of the designated waste, the “time of generation” is defined as follows: |
| A) | For the F037 listing, sludges are considered to be generated at the moment of deposition in the unit, where deposition is defined as at least a temporary cessation of lateral particle movement. |
| B) | For the F038 listing: |
| i) | Sludges are considered to be generated at the moment of deposition in the unit, where deposition is defined as at least a temporary cessation of lateral particle movement; and |
| ii) | Floats are considered to be generated at the moment they are formed in the top of the unit. |
| 4) | For the purposes of the F019 hazardous waste listing, the following apply to wastewater treatment sludges from the manufacturing of motor vehicles using a zinc phosphating process: |
| A) | “Motor vehicle manufacturing” is defined to include the manufacture of automobiles and light trucks or utility vehicles (including light duty vans, pick-up trucks, minivans, and sport utility vehicles). A faciliy owner or operator must be engaged in manufacturing complete vehicles (body and chassis or unibody) or chassis only; and |
| B) | The generator must maintain in its on-site records documentation and information sufficient to prove that the wastewater treatment sludge to be exempted from the F019 listing meets the conditions of the listing. These records must include the following information: the volumes of waste generated and disposed of off site; documentation showing when the waste volumes were generated and sent off site; the name and address of the receiving facility; and documentation confirming receipt of the waste by the receiving facility. The generator must maintain these documents on site for no less than three years. The retention period for the documentation is automatically extended during the pendency of any enforcement action or as requested by USEPA or by the Agency in writing. |
| Section 721.133 | Discarded Commercial Chemical Products, Off-Specification Species, Container Residues, and Spill Residues Thereof |
| a) | Any commercial chemical product or manufacturing chemical intermediate having the generic name listed in subsection (e) or (f) of this Section. |
| 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) of this Section. |
| 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) of this Section, unless the container is empty, as defined in Section 721.107(b)(3). |
| 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) of this Section 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) of this Section. |
| 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) of this Section are identified as acute hazardous waste (H) and are subject to the small quantity exclusion defined in Section 721.105(e). These wastes and their corresponding USEPA hazardous waste numbers are the following: |
| USEPA Hazardous Waste No. | Chemical Abstracts No. (CAS No.) | Substance |
| 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 | Ethylenimine |
| 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 |
| 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 |
| 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 |
| 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 | Ethylenimine |
| 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 |
| P075 | 54-11-5* | Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)- and salts |
| 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) of this Section, are identified as toxic wastes (T) unless otherwise designated and are subject to the small quantity exclusion defined in Section 721.105(a) and (g). These wastes and their corresponding USEPA hazardous waste numbers are the following: |
| USEPA Hazardous Waste No. | Chemical Abstracts No. (CAS No.) |
Substance |
| 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, T) |
| 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- |
| 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)- |
| U234 | 99-35-4 | Benzene, 1,3,5-trinitro- |
| U021 | 92-87-5 | Benzidene |
| U202 | P 81-07-2 | 1,2-Benzisothiazol-3(2H)-one, 1,1-dioxide, and salts |
| 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 | P 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 |
| 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 |
| 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 | |
| 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 |
| 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- |
| 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 | 58-04-2 | 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 |
| U202 | P 81-07-2 | Saccharin and salts |
| U203 | 94-59-7 | Safrole |
| U204 | 7783-00-8 | Selenious acid |
| U204 | 7783-00-8 | Selenium dioxide |
| U205 | 7488-56-4 | Selenium sulfide |
| 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 | 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 | P 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 |
| 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)- |
| 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 |
| 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 | |
| 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 |
| 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 |
| 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- |
| 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 | 58-04-2 | 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- |
| 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 |
| U202 | P 81-07-2 | 1,2-Benzisothiazol-3(2H)-one, 1,1-dioxide, and salts |
| U202 | P 81-07-2 | Saccharin and salts |
| 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 |
| 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- |
| 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) |
| 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 | P 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 | P 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 |
| Section 721.Appendix G | |
| Basis for Listing Hazardous Wastes | |
| USEPA hazardous waste No. | Hazardous constituents for which listed |
| F001 | Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, carbon tetrachloride, chlorinated fluorocarbons. |
| F002 | Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, 1,1,2-trichlorethane, chlorobenzene, 1,1,2-trichloro-1,2,2-trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane. |
| F003 | N.A. |
| F004 | Cresols and cresylic acid, nitrobenzene. |
| F005 | Toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, 2-ethoxyethanol, benzene, 2-nitropropane. |
| F006 | Cadmium, hexavalent chromium, nickel, cyanide (complexed). |
| F007 | Cyanide (salts). |
| F008 | Cyanide (salts). |
| F009 | Cyanide (salts). |
| F010 | Cyanide (salts). |
| F011 | Cyanide (salts). |
| F012 | Cyanide (complexed). |
| F019 | Hexavalent chromium, cyanide (complexed). |
| F020 | Tetra- and pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans; tri- and tetrachlorophenols and their clorophenoxy derivative acids, esters, ethers, amines, and other salts. |
| F021 | Penta- and hexachlorodibenzo-p-dioxins; penta- and hexachlorodibenzofurans; pentachlorophenol and its derivatives. |
| F022 | Tetra-, penta- and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans. |
| F023 | Tetra- and pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans; tri- and tetra- chlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines, and other salts. |
| F024 | Chloromethane, dichloromethane, trichloromethane, carbon tetrachloride, chloroethylene, 1,1-dichloroethane, 1,2-dichloroethane, trans-1,2-dichloroethylene, 1,1-dichloroethylene, 1,1,1-trichloroethane, 1,1,2-trichloroethane, trichloroethylene, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane, tetrachloroethylene, pentachloroethane, hexachloroethane, allyl chloride (3-chloropropene), dichloropropane, dichloropropene, 2-chloro-1,3-butadiene, hexachloro-1,3-butadiene, hexachlorochylopentadiene, hexachlorocylohexane, benzene, chlorobenzene, dichlorobenzenes, 1,2,4-trichlorobenzene, tetrachlorobenzenes, pentachlorobenzene, hexachlorobenzene, toluene, naphthalene. |
| F025 | Chloromethane, dicloromethane, trichloromethane; carbon tetrachloride; chloroethylene; 1,1-dichloroethane; 1,2-dichloroethane; trans-1,2-dichloroethylene; 1,1-dichloroethylene; 1,1,1-trichloroethane; 1,1,2-trichloroethane; trichloroethylene; 1,1,1,2-tetrachloroethane; 1,1,2,2-tetrachloroethane; tetrachloroethylene; pentachloroethane; hexachloroethane; allyl chloride (3-chloropropene); dichloropropane; dichloropropene; 2-chloro-1,3-butadiene; hexachloro-1,3-butadiene; hexachlorocyclopentadiene; benzene; chlorobenzene; dichlorobenzene; 1,2,4-trichlorobenzene; tetrachlorobenzene; pentachlorobenzene; hexachlorobenzene; toluene; naphthalene. |
| F026 | Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans. |
| F027 | Tetra-, penta, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans; tri-, tetra-, and pentachlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines, and other salts. |
| F028 | Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans; tri-, tetra-, and pentachlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines, and other salts. |
| F032 | Benz(a)anthracene; benzo(a)pyrene; dibenz(a,h)anthracene; indeno(1,2,3-cd)pyrene; pentachlorophenol; arsenic; chromium; tetra-, penta-, hexa-, and heptachlorordibenzo-p-dioxins; tetra-, penta-, hexa-, and heptachlorodibenzofurans. |
| F034 | Benz(a)anthracene, benzo(k)fluoranthene, benzo(a)pyrene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene, naphthalene, arsenic, chromium. |
| F035 | Arsenic, chromium, 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. |
| K064 | Lead, cadmium. |
| K065 | Lead, cadmium. |
| K066 | Lead, cadmium. |
| K069 | Hexavalent chromium, lead, cadmium. |
| K071 | Mercury. |
| K073 | Chloroform, carbon tetrachloride, hexachloroethane, trichloroethane, tetrachloroethylene, dichloroethylene, 1,1,2,2-tetrachloroethane. |
| K083 | Aniline, diphenylamine, nitrobenzene, phenylenediamine. |
| K084 | Arsenic. |
| K085 | Benzene, dichlorobenzenes, trichlorobenzenes, tetrachlorobenzenes, pentachlorobenzene, hexachlorobenzene, benzyl chloride. |
| K086 | Lead, hexavalent chromium. |
| K087 | Phenol, naphthalene. |
| K088 | Cyanide (complexes). |
| K090 | Chromium. |
| K091 | Chromium. |
| K093 | Phthalic anhydride, maleic anhydride. |
| K094 | Phthalic anhydride. |
| K095 | 1,1,2-trichloroethane, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane. |
| K096 | 1,2-dichloroethane, 1,1,1-trichloroethane, 1,1,2-trichloroethane. |
| K097 | Chlordane, heptachlor. |
| K098 | Toxaphene. |
| K099 | 2,4-dichlorophenol, 2,4,6-trichlorophenol. |
| K100 | Hexavalent chromium, lead, cadmium. |
| K101 | Arsenic. |
| K102 | Arsenic. |
| K103 | Aniline, nitrobenzene, phenylenediamine. |
| K104 | Aniline, benzene, diphenylamine, nitrobenzene, phynylenediamine. |
| K105 | Benzene, monochlorobenzene, dichlorobenzenes, 2,4,6-trichlorophenol. |
| K106 | Mercury. |
| K111 | 2,4-Dinitrotoluene. |
| K112 | 2,4-Toluenediamine, o-toluidine, p-toluidine, aniline. |
| K113 | 2,4-Toluenediamine, o-toluidine, p-toluidine, aniline. |
| K114 | 2,4-Toluenediamine, o-toluidine, p-toluidine. |
| K115 | 2,4-Toluenediamine. |
| K116 | Carbon tetrachloride, tetrachloroethylene, chloroform, phosgene. |
| K117 | Ethylene dibromide. |
| K118 | Ethylene dibromide. |
| K123 | Ethylene thiourea. |
| K124 | Ethylene thiourea. |
| K125 | Ethylene thiourea. |
| K126 | Ethylene thiourea. |
| K131 | Dimethyl sulfate, methyl bromide. |
| K132 | Methyl bromide. |
| K136 | Ethylene dibromide. |
| K141 | Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene. |
| K142 | Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene. |
| K143 | Benzene, benz(a)anthracene, benzo(b)fluoranthene, benzo(k)fluoranthene. |
| K144 | Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene. |
| K145 | Benzene, benz(a)anthracene, benzo(a)pyrene, dibenz(a,h)anthracene, naphthalene. |
| K147 | Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene. |
| K148 | Benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene. |
| K149 | Benzotrichloride, benzyl chloride, chloroform, chloromethane, chlorobenzene, 1,4-dichlorobenzene, hexachlorobenzene, pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, toluene. |
| K150 | Carbon tetrachloride, chloroform, chloromethane, 1,4-dichlorobenzene, hexachlorobenzene, pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, 1,1,2,2-tetrachloroethane, tetrachloroethylene, 1,2,4-trichlorobenzene. |
| K151 | Benzene, carbon tetrachloride, chloroform, hexachlorobenzene, pentachlorobenzene, toluene, 1,2,4,5-tetrachlorobenzene, tetrachloroethylene. |
| K156 | Benomyl, carbaryl, carbendazim, carbofuran, carbosulfan, formaldehyde, methylene chloride, triethylamine. |
| K157 | Carbon tetrachloride, formaldehyde, methyl chloride, methylene chloride, pyridine, triethylamine. |
| K158 | Benomyl, carbendazim, carbofuran, carbosulfan, chloroform, methylene chloride. |
| K159 | Benzene, butylate, EPTC, molinate, pebulate, vernolate. |
| K161 | Antimony, arsenic, metam-sodium, ziram. |
| K169 | Benzene. |
| K170 | Benzo(a)pyrene, dibenz(a,h)anthracene, benzo (a) anthracene, benzo(b)fluoranthene, benzo(k)fluoranthene, 3-methylcholanthrene, 7,12-dimethylbenz(a)anthracene. |
| K171 | Benzene, arsenic. |
| K172 | Benzene, arsenic. |
| K174 | 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD), 1,2,3,4,6,7,8-heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF), 1,2,3,4,7,8,9-heptachlorodibenzofuran (1,2,3,6,7,8,9-HpCDF), all hexachlorodibenzo-p-dioxins (HxCDDs), all hexachlorodibenzofurans (HxCDFs), all pentachlorodibenzo-p-dioxins (PeCDDs), 1,2,3,4,6,7,8,9-octachlorodibenzo-p-dioxin (OCDD), 1,2,3,4,6,7,8,9- octachlorodibenzofuran (OCDF), all pentachlorodibenzofurans (PeCDFs), all tetrachlorodibenzo-p-dioxins (TCDDs), all tetrachlorodibenzofurans (TCDFs). |
| K175 | Mercury. |
| K176 | Arsenic, lead. |
| K177 | Antimony. |
| K178 | Thallium. |
| K181 | Aniline, o-anisidine, 4-chloroaniline, p-cresidine, 2,4-dimethylaniline, 1,2-phenylenediamine, 1,3-phenylenediamine. |
| Section 721.Appendix Y | |
| Table to Section 721.138 | |
| Chemical name | CAS No | Composite value (mg/kg) | Heating value (BTU/lb) | Concentration limit (mg/kg at 10,000 Btu/lb) | Minimum required detection limit (mg/kg) |
| Total Nitrogen as N | NA
|
9,000
|
18,400
|
4,900
|
|
| Total Halogens as Cl | NA
|
1,000
|
18,400
|
540
|
|
| Total Organic Halogens as Cl | NA
|
(Note 1)
|
|||
| Polychlorinated biphenyls, total (Arocolors, total) | 1336-36-3
|
ND
|
ND
|
1.4
|
|
| Cyanide, total | 57-12-5
|
ND
|
ND
|
1.0
|
|
| Metals: | |||||
| Antimony, total | 7440-36-0
|
ND
|
12
|
||
| Arsenic, total | 7440-38-2
|
ND
|
0.23
|
||
| Barium, total | 7440-39-3
|
ND
|
23
|
||
| Beryllium, total | 7440-41-7
|
ND
|
1.2
|
||
| Cadmium, total | 7440-43-9
|
ND
|
1.2
|
||
| Chromium, total | 7440-47-3
|
ND
|
2.3
|
||
| Cobalt | 7440-48-4
|
ND
|
4.6
|
||
| Lead, total | 7439-92-1
|
57
|
18,100
|
31
|
|
| Manganese | 7439-96-5
|
ND
|
1.2
|
||
| Mercury, total | 7439-97-6
|
ND
|
0.25
|
||
| Nickel, total | 7440-02-0
|
106
|
18,400
|
58
|
|
| Selenium, total | 7782-49-2
|
ND
|
0.23
|
||
| Silver, total | 7440-22-4
|
ND
|
2.3
|
||
| Thallium, total | 7440-28-0
|
ND
|
23
|
||
| Hydrocarbons: | |||||
| Benzo(a)anthracene | 56-55-3
|
ND
|
2,400
|
||
| Benzene | 71-43-2
|
8,000
|
19,600
|
4,100
|
|
| Benzo(b)fluoranthene | 205-99-2
|
ND
|
2,400
|
||
| Benzo(k)fluoranthene | 207-08-9
|
ND
|
2,400
|
||
| Benzo(a)pyrene | 50-32-8
|
ND
|
2,400
|
||
| Chrysene | 218-01-9
|
ND
|
2,400
|
||
| Dibenzo(a,h)anthracene | 53-70-3
|
ND
|
2,400
|
||
| 7,12-Dimethylbenz(a)anthracene | 57-97-6
|
ND
|
2,400
|
||
| Fluoranthene | 206-44-0
|
ND
|
2,400
|
||
| Indeno(1,2,3-cd)pyrene | 193-39-5
|
ND
|
2,400
|
||
| 3-Methylcholanthrene | 56-49-5
|
ND
|
2,400
|
||
| Naphthalene | 91-20-3
|
6,200
|
19,400
|
3,200
|
|
| Toluene | 108-88-3
|
69,000
|
19,400
|
36,000
|
|
| Oxygenates: | |||||
| Acetophenone | 98-86-2
|
ND
|
2,400
|
||
| Acrolein | 107-02-8
|
ND
|
39
|
||
| Allyl alcohol | 107-18-6
|
ND
|
30
|
||
| Bis(2-ethylhexyl)phthalate (Di-2-ethylhexyl phthalate) | 117-81-7
|
ND
|
2,400
|
||
| Butyl benzyl phthalate | 85-68-7
|
ND
|
2,400
|
||
| o-Cresol (2-Methyl phenol) | 95-48-7
|
ND
|
2,400
|
||
| m-Cresol (3-M ethyl phenol) | 108-39-4
|
ND
|
2,400
|
||
| p-Cresol (4-Methyl phenol) | 106-44-5
|
ND
|
2,400
|
||
| Di-n-butyl phthalate | 84-74-2
|
ND
|
2,400
|
||
| Diethyl phthalate | 84-66-2
|
ND
|
2,400
|
||
| 2,4-Dimethylphenol | 105-67-9
|
ND
|
2,400
|
||
| Dimethyl phthalate | 131-11-3
|
ND
|
2,400
|
||
| Di-n-octyl phthalate | 117-84-0
|
ND
|
2,400
|
||
| Endothall | 145-73-3
|
ND
|
100
|
||
| Ethyl methacrylate | 97-63-2
|
ND
|
39
|
||
| 2-Ethoxyethanol (Ethylene glycol monoethyl ether) | 110-80-5
|
ND
|
100
|
||
| Isobutyl alcohol | 78-83-1
|
ND
|
39
|
||
| Isosafrole | 120-58-1
|
ND
|
2,400
|
||
| Methyl ethyl ketone (2-Butanone) | 78-93-3
|
ND
|
39
|
||
| Methyl methacrylate | 80-62-6
|
ND
|
39
|
||
| 1,4-Naphthoquinone | 130-15-4
|
ND
|
2,400
|
||
| Phenol | 108-95-2
|
ND
|
2,400
|
||
| Propargyl alcohol (2-Propyn-l-ol) | 107-19-7
|
ND
|
30.
|
||
| Safrole | 94-59-7
|
ND
|
2,400
|
||
| Sulfonated Organics: | |||||
| Carbon disulfide | 75-15-0
|
ND
|
ND
|
39
|
|
| Disulfoton | 298-04-4
|
ND
|
ND
|
2,400
|
|
| Ethyl methanesulfonate | 62-50-0
|
ND
|
ND
|
2,400
|
|
| Methyl methanesulfonate | 66-27-3
|
ND
|
ND
|
2,400
|
|
| Phorate | 298-02-2
|
ND
|
ND
|
2,400
|
|
| 1,3-Propane sultone | 1120-71-4
|
ND
|
ND
|
100
|
|
| Tetraethyldithiopyrophosphate (Sulfotepp) | 3689-24-5
|
ND
|
ND
|
2,400
|
|
| Thiophenol (Benzenethiol) | 108-98-5
|
ND
|
ND
|
30
|
|
| O,O,O-Triethyl phosphorothioate | 126-68-1
|
ND
|
ND
|
2,400
|
|
| Nitrogenated Organics: | |||||
| Acetonitrile (Methyl cyanide) | 75-05-8
|
ND
|
ND
|
39
|
|
| 2-Acetylaminofluorene (2-AAF) | 53-96-3
|
ND
|
ND
|
2,400
|
|
| Acrylonitrile | 107-13-1
|
ND
|
ND
|
39
|
|
| 4-Aminobiphenyl | 92-67-1
|
ND
|
ND
|
2,400
|
|
| 4-Aminopyridine | 504-24-5
|
ND
|
ND
|
100
|
|
| Aniline | 62-53-3
|
ND
|
ND
|
2,400
|
|
| Benzidine | 92-87-5
|
ND
|
ND
|
2,400
|
|
| Dibenz(a,j)acridine | 224-42-0
|
ND
|
ND
|
2,400
|
|
| O,O-Diethyl O-pyrazinyl phophoro-thioate (Thionazin) | 297-97-2
|
ND
|
ND
|
2,400
|
|
| Dimethoate | 60-51-5
|
ND
|
ND
|
2,400
|
|
| p-(Dimethylamino)azobenzene (4-Dimethylaminoazobenzene) | 60-11-7
|
ND
|
ND
|
2,400
|
|
| 3,3'-Dimethylbenzidine | 119-93-7
|
ND
|
ND
|
2,400
|
|
| a,a-Dimethylphenethylamine | 122-09-8
|
ND
|
ND
|
2,400
|
|
| 3,3'-Dimethoxybenzidine | 119-90-4
|
ND
|
ND
|
100
|
|
| 1,3-Dinitrobenzene (m-Dinitrobenzene) | 99-65-0
|
ND
|
ND
|
2,400
|
|
| 4,6-Dinitro-o-cresol | 534-52-1
|
ND
|
ND
|
2,400
|
|
| 2,4-Dinitrophenol | 51-28-5
|
ND
|
ND
|
2,400
|
|
| 2,4-Dinitrotoluene | 121-14-2
|
ND
|
ND
|
2,400
|
|
| 2,6-Dinitrotoluene | 606-20-2
|
ND
|
ND
|
2,400
|
|
| Dinoseb (2-sec-Butyl-4,6-dinitrophenol) | 88-85-7
|
ND
|
ND
|
2,400
|
|
| Diphenylamine | 122-39-4
|
ND
|
ND
|
2,400
|
|
| Ethyl carbamate (Urethane) | 51-79-6
|
ND
|
ND
|
100
|
|
| Ethylenethiourea (2-Imidazolidinethione) | 96-45-7
|
ND
|
ND
|
110
|
|
| Famphur | 52-85-7
|
ND
|
ND
|
2,400
|
|
| Methacrylonitrile | 126-98-7
|
ND
|
ND
|
39
|
|
| Methapyrilene | 91-80-5
|
ND
|
ND
|
2,400
|
|
| Methomyl | 16752-77-5
|
ND
|
ND
|
57
|
|
| 2-Methyllactonitrile (Acetone cyanohydrin ) | 75-86-5
|
ND
|
ND
|
100
|
|
| Methyl parathion | 298-00-0
|
ND
|
ND
|
2,400
|
|
| MNNG (N-Metyl-N-nitroso-N'-nitroguanidine) | 70-25-7
|
ND
|
ND
|
110
|
|
| 1-Naphthylamine (a-Naphthylamine] | 134-32-7
|
ND
|
ND
|
2,400
|
|
| 2-Naphthylamine ( b -Naphthylamine) | 91-59-8
|
ND
|
ND
|
2,400
|
|
| Nicotine | 54-11-5
|
ND
|
ND
|
100
|
|
| 4-Nitroaniline (p-Nitroaniline) | 100-01-6
|
ND
|
ND
|
2,400
|
|
| Nitrobenzene | 98-95-3
|
ND
|
ND
|
2,400
|
|
| p-Nitrophenol (p-Nitrophenol) | 100-02-7
|
ND
|
ND
|
2,400
|
|
| 5-Nitro-o-toluidine | 99-55-8
|
ND
|
ND
|
2,400
|
|
| N-Nitrosodi-n-butylamine | 924-16-3
|
ND
|
ND
|
2,400
|
|
| N-Nitrosodiethylamine | 55-18-5
|
ND
|
ND
|
2,400
|
|
| N-Nitrosodiphenylamine (Diphenylnitrosamine) | 86-30-6
|
ND
|
ND
|
2,400
|
|
| N-Nitroso-N-methylethylamine | 10595-95-6
|
ND
|
ND
|
2,400
|
|
| N-Nitrosomorpholine | 59-89-2
|
ND
|
ND
|
2,400
|
|
| N-Nitrosopiperidine | 100-75-4
|
ND
|
ND
|
2,400
|
|
| N-Nitrosopyrrolidine | 930-55-2
|
ND
|
ND
|
2,400
|
|
| 2-Nitropropane | 79-46-9
|
ND
|
ND
|
30
|
|
| Parathion | 56-38-2
|
ND
|
ND
|
2,400
|
|
| Phenacetin | 62-44-2
|
ND
|
ND
|
2,400
|
|
| 1,4-Phenylene diamine, (p-Phenylenediamine) | 106-50-3
|
ND
|
ND
|
2,400
|
|
| N-Phenylthiourea | 103-85-5
|
ND
|
ND
|
57
|
|
| 2-Picoline (alpha-Picoline) | 109-06-8
|
ND
|
ND
|
2,400
|
|
| Propythioracil (6-Propyl-2-thiouracil) | 51-52-5
|
ND
|
ND
|
100
|
|
| Pyridine | 110-86-1
|
ND
|
ND
|
2,400
|
|
| Strychnine | 57-24-9
|
ND
|
ND
|
100
|
|
| Thioacetamide | 62-55-5
|
ND
|
ND
|
57
|
|
| Thiofanox | 39196-18-4
|
ND
|
ND
|
100
|
|
| Thiourea | 62-56-6
|
ND
|
ND
|
57
|
|
| Toluene-2,4-diamine (2,4-Diaminotoluene) | 95-80-7
|
ND
|
ND
|
57
|
|
| Toluene-2,6-diamine (2,6-Diaminotoluene) | 823-40-5
|
ND
|
ND
|
57
|
|
| o-Toluidine | 95-53-4
|
ND
|
ND
|
2,400
|
|
| p-Toluidine | 106-49-0
|
ND
|
ND
|
100
|
|
| 1,3,5-Trinitrobenzene, (sym-Trinitrobenzene) | 99-35-4
|
ND
|
ND
|
2,400
|
|
| Halogenated Organics: | |||||
| Allyl chloride | 107-05-1
|
ND
|
ND
|
39
|
|
| Aramite | 140-57-8
|
ND
|
ND
|
2,400
|
|
| Benzal chloride (Dichloromethyl benzene) | 98-87-3
|
ND
|
ND
|
100
|
|
| Benzyl chloride | 100-44-77
|
ND
|
ND
|
100
|
|
| Bis(2-chloroethyl)ether (Dichloroethyl ether) | 111-44-4
|
ND
|
ND
|
2,400
|
|
| Bromoform (Tribromomethane) | 75-25-2
|
ND
|
ND
|
39
|
|
| Bromomethane (Methyl bromide) | 74-83-9
|
ND
|
ND
|
39
|
|
| 4-Bromophenyl phenyl ether (p-Bromodiphenyl ether) | 101-55-3
|
ND
|
ND
|
2,400
|
|
| Carbon tetrachloride | 56-23-5
|
ND
|
ND
|
39
|
|
| Chlordane | 57-74-9
|
ND
|
ND
|
14
|
|
| p-Chloroaniline | 106-47-8
|
ND
|
ND
|
2,400
|
|
| Chlorobenzene | 108-90-7
|
ND
|
ND
|
39
|
|
| Chlorobenzilate | 510-15-6
|
ND
|
ND
|
2,400
|
|
| p-Chloro-m-cresol | 59-50-7
|
ND
|
ND
|
2,400
|
|
| 2-Chloroethyl vinyl ether | 110-75-8
|
ND
|
ND
|
39
|
|
| Chloroform | 67-66-3
|
ND
|
ND
|
39
|
|
| Chloromethane (Methyl chloride) | 74-87-3
|
ND
|
ND
|
39
|
|
| 2-Chloronaphthalene (β-Chlorophthalene) | 91-58-7
|
ND
|
ND
|
2,400
|
|
| 2-Chlorophenol (o-Chlorophenol) | 95-57-8
|
ND
|
ND
|
2,400
|
|
| Chloroprene (2-Chloro-1,3-butadiene) | 1126-99-8
|
ND
|
ND
|
39
|
|
| 2,4-D (2,4-Dichlorophenoxyacetic acid) | 94-75-7
|
ND
|
ND
|
7.0
|
|
| Diallate | 2303-16-4
|
ND
|
ND
|
2,400
|
|
| 1,2-Dibromo-3-chloropropane | 96-12-8
|
ND
|
ND
|
39
|
|
| 1,2-Dichlorobenzene (o-Dichlorobenzene) | 95-50-1
|
ND
|
ND
|
2,400
|
|
| 1,3-Dichlorobenzene (m-Dichlorobenzene) | 541-73-1
|
ND
|
ND
|
2,400
|
|
| 1,4-Dichlorobenzene (p-Dichlorobenzene) | 106-46-7
|
ND
|
ND
|
2,400
|
|
| 3,3'-Dichlorobenzidine | 91-94-1
|
ND
|
ND
|
2,400
|
|
| Dichlorodifluoromethane (CFC-12) | 75-71-8
|
ND
|
ND
|
39
|
|
| 1,2-Dichloroethane (Ethylene dichloride) | 107-06-2
|
ND
|
ND
|
39
|
|
| 1,1-Dichloroethylene (Vinylidene chloride) | 75-35-4
|
ND
|
ND
|
39
|
|
| Dichloromethoxy ethane (Bis(2-chloroethoxy)methane) | 111-91-1
|
ND
|
ND
|
2,400
|
|
| 2,4-Dichlorophenol | 120-83-2
|
ND
|
ND
|
2,400
|
|
| 2,6-Dichlorophenol | 87-65-0
|
ND
|
ND
|
2,400
|
|
| 1,2-Dichloropropane (Propylene dichloride) | 78-87-5
|
ND
|
ND
|
39
|
|
| cis-1,3-Dichloropropylene | 10061-01-5
|
ND
|
ND
|
39
|
|
| trans-1,3-Dichloropropylene | 10061-02-6
|
ND
|
ND
|
39
|
|
| 1,3-Dichloro-2-propanol | 96-23-1
|
ND
|
ND
|
30
|
|
| Endosulfan I | 959-98-8
|
ND
|
ND
|
1.4
|
|
| Endosulfan II | 33213-65-9
|
ND
|
ND
|
1.4
|
|
| Endrin | 72-20-8
|
ND
|
ND
|
1.4
|
|
| Endrin aldehyde | 7421-93-4
|
ND
|
ND
|
1.4
|
|
| Endrin Ketone | 53494-70-5
|
ND
|
ND
|
1.4
|
|
| Epichlorohydrin (1-Chloro-2,3-epoxy propane) | 106-89-8
|
ND
|
ND
|
30
|
|
| Ethylidene dichloride (1,1-Dichloroethane) | 75-34-3
|
ND
|
ND
|
39
|
|
| 2-Fluoroacetamide | 640-19-7
|
ND
|
ND
|
100
|
|
| Heptachlor | 76-44-8
|
ND
|
ND
|
1.4
|
|
| Heptachlor epoxide | 1024-57-3
|
ND
|
ND
|
2.8
|
|
| Hexachlorobenzene | 118-74-1
|
ND
|
ND
|
2,400
|
|
| Hexachloro-1,3-butadiene (Hexachlorobutadiene) | 87-68-3
|
ND
|
ND
|
2,400
|
|
| Hexachlorocyclopentadiene | 77-47-4
|
ND
|
ND
|
2,400
|
|
| Hexachloroethane | 67-72-1
|
ND
|
ND
|
2,400
|
|
| Hexachlorophene | 70-30-4
|
ND
|
ND
|
59,000
|
|
| Hexachloropropene (Hexachloropropylene) | 1888-71-7
|
ND
|
ND
|
2,400
|
|
| Isodrin | 465-73-6
|
ND
|
ND
|
2,400
|
|
| Kepone (Chlordecone) | 143-50-0
|
ND
|
ND
|
4,700
|
|
| Lindane (gamma-Hexachlorocyclohexane) (γ-BHC) | 58-89-9
|
ND
|
ND
|
1.4
|
|
| Methylene chloride (Dichloromethane) | 75-09-2
|
ND
|
ND
|
39
|
|
| 4,4'-methylene-bis(2-chloroaniline) | 101-14-4
|
ND
|
ND
|
100
|
|
| Methyl iodide (Iodomethane) | 74-88-4
|
ND
|
ND
|
39
|
|
| Pentachlorobenzene | 608-93-5
|
ND
|
ND
|
2,400
|
|
| Pentachloroethane | 76-01-7
|
ND
|
ND
|
39
|
|
| Pentachloronitrobenzene (PCNB) (Quintobenzene) (Quintozene) | 82-68-8
|
ND
|
ND
|
2,400
|
|
| Pentachlorophenol | 87-86-5
|
ND
|
ND
|
2,400
|
|
| Pronamide | 23950-58-5
|
ND
|
ND
|
2,400
|
|
| Silvex (2,4,5-Trichlorophenoxypropionic acid) | 93-72-1
|
ND
|
ND
|
7.0
|
|
| 2,3,7,8-Tetrachlorodibenzo-p-dioxin (2,3,7,8-TCDD) | 1746-01-6
|
ND
|
ND
|
30
|
|
| 1,2,4,5-Tetrachlorobenzene | 95-94-3
|
ND
|
ND
|
2,400
|
|
| 1,1,2,2-Tetrachloroethane | 79-34-5
|
ND
|
ND
|
39
|
|
| Tetrachloroethylene (Perchloroethylene) | 127-18-4
|
ND
|
ND
|
39
|
|
| 2,3,4,6-Tetrachlorophenol | 58-90-2
|
ND
|
ND
|
2,400
|
|
| 1,2,4-Trichlorobenzene | 120-82-1
|
ND
|
ND
|
2,400
|
|
| 1,1,1-Trichloroethane (Methyl chloroform) | 71-55-6
|
ND
|
ND
|
39
|
|
| 1,1,2-Trichloroethane (Vinyl trichloride) | 79-00-5
|
ND
|
ND
|
39
|
|
| Trichloroethylene | 79-01-6
|
ND
|
ND
|
39
|
|
| Trichlorofluoromethane (Trichloromonofluoromethane) | 75-69-4
|
ND
|
ND
|
39
|
|
| 2,4,5-Trichlorophenol | 95-95-4
|
ND
|
ND
|
2,400
|
|
| 2,4,6-Trichlorophenol | 88-06-2
|
ND
|
ND
|
2,400
|
|
| 1,2,3-Trichloropropane | 96-18-4
|
ND
|
ND
|
39
|
|
| Vinyl Chloride | 75-01-4
|
ND
|
ND
|
39
|
| Section 721.Appendix Z | |
| Table to Section 721.102 | |
| 1 | 2 | 3 | 4 | |
| Use constituting disposal | Burning for energy recovery or use to produce a fuel | Reclamation (except as provided in Section 721.104(a)(17) for mineral processing secondary materials) | 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 | 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 | Yes |
| Commercial chemical products listed in Section 721.133 | Yes | Yes |
| Scrap metal other than excluded scrap metal (see Section 721.101(c)(9)) | Yes | Yes | Yes | Yes |
| 724.101 | Purpose, Scope, and Applicability |
| 724.103 | Relationship to Interim Status Standards |
| 724.104 | Electronic Reporting |
| 724.110 | Applicability |
| 724.111 | USEPA Identification Number |
| 724.112 | Required Notices |
| 724.113 | General Waste Analysis |
| 724.114 | Security |
| 724.115 | General Inspection Requirements |
| 724.116 | Personnel Training |
| 724.117 | General Requirements for Ignitable, Reactive, or Incompatible Wastes |
| 724.118 | Location Standards |
| 724.119 | Construction Quality Assurance Program |
| 724.130 | Applicability |
| 724.131 | Design and Operation of Facility |
| 724.132 | Required Equipment |
| 724.133 | Testing and Maintenance of Equipment |
| 724.134 | Access to Communications or Alarm System |
| 724.135 | Required Aisle Space |
| 724.137 | Arrangements with Local Authorities |
| 724.150 | Applicability |
| 724.151 | Purpose and Implementation of Contingency Plan |
| 724.152 | Content of Contingency Plan |
| 724.153 | Copies of Contingency Plan |
| 724.154 | Amendment of Contingency Plan |
| 724.155 | Emergency Coordinator |
| 724.156 | Emergency Procedures |
| 724.170 | Applicability |
| 724.171 | Use of Manifest System |
| 724.172 | Manifest Discrepancies |
| 724.173 | Operating Record |
| 724.174 | Availability, Retention, and Disposition of Records |
| 724.175 | Annual Facility Activities Report |
| 724.176 | Unmanifested Waste Report |
| 724.177 | Additional Reports |
| 724.190 | Applicability |
| 724.191 | Required Programs |
| 724.192 | Groundwater Protection Standard |
| 724.193 | Hazardous Constituents |
| 724.194 | Concentration Limits |
| 724.195 | Point of Compliance |
| 724.196 | Compliance Period |
| 724.197 | General Groundwater Monitoring Requirements |
| 724.198 | Detection Monitoring Program |
| 724.199 | Compliance Monitoring Program |
| 724.200 | Corrective Action Program |
| 724.201 | Corrective Action for Solid Waste Management Units |
| 724.210 | Applicability |
| 724.211 | Closure Performance Standard |
| 724.212 | Closure Plan; Amendment of Plan |
| 724.213 | Closure; Time Allowed For Closure |
| 724.214 | Disposal or Decontamination of Equipment, Structures, and Soils |
| 724.215 | Certification of Closure |
| 724.216 | Survey Plat |
| 724.217 | Post-Closure Care and Use of Property |
| 724.218 | Post-Closure Care Plan; Amendment of Plan |
| 724.219 | Post-Closure Notices |
| 724.220 | Certification of Completion of Post-Closure Care |
| 724.240 | Applicability |
| 724.241 | Definitions of Terms as Used in This Subpart |
| 724.242 | Cost Estimate for Closure |
| 724.243 | Financial Assurance for Closure |
| 724.244 | Cost Estimate for Post-Closure Care |
| 724.245 | Financial Assurance for Post-Closure Care |
| 724.246 | Use of a Mechanism for Financial Assurance of Both Closure and Post-Closure Care |
| 724.247 | Liability Requirements |
| 724.248 | Incapacity of Owners or Operators, Guarantors, or Financial Institutions |
| 724.251 | Wording of the Instruments |
| 724.270 | Applicability |
| 724.271 | Condition of Containers |
| 724.272 | Compatibility of Waste with Container |
| 724.273 | Management of Containers |
| 724.274 | Inspections |
| 724.275 | Containment |
| 724.276 | Special Requirements for Ignitable or Reactive Waste |
| 724.277 | Special Requirements for Incompatible Wastes |
| 724.278 | Closure |
| 724.279 | Air Emission Standards |
| 724.290 | Applicability |
| 724.291 | Assessment of Existing Tank System Integrity |
| 724.292 | Design and Installation of New Tank Systems or Components |
| 724.293 | Containment and Detection of Releases |
| 724.294 | General Operating Requirements |
| 724.295 | Inspections |
| 724.296 | Response to Leaks or Spills and Disposition of Leaking or Unfit-for-Use Tank Systems |
| 724.297 | Closure and Post-Closure Care |
| 724.298 | Special Requirements for Ignitable or Reactive Waste |
| 724.299 | Special Requirements for Incompatible Wastes |
| 724.300 | Air Emission Standards |
| 724.320 | Applicability |
| 724.321 | Design and Operating Requirements |
| 724.322 | Action Leakage Rate |
| 724.323 | Response Actions |
| 724.326 | Monitoring and Inspection |
| 724.327 | Emergency Repairs; Contingency Plans |
| 724.328 | Closure and Post-Closure Care |
| 724.329 | Special Requirements for Ignitable or Reactive Waste |
| 724.330 | Special Requirements for Incompatible Wastes |
| 724.331 | Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026, and F027 |
| 724.332 | Air Emission Standards |
| 724.350 | Applicability |
| 724.351 | Design and Operating Requirements |
| 724.352 | Action Leakage Rate |
| 724.353 | Response Action Plan |
| 724.354 | Monitoring and Inspection |
| 724.356 | Special Requirements for Ignitable or Reactive Waste |
| 724.357 | Special Requirements for Incompatible Wastes |
| 724.358 | Closure and Post-Closure Care |
| 724.359 | Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026, and F027 |
| 724.370 | Applicability |
| 724.371 | Treatment Program |
| 724.372 | Treatment Demonstration |
| 724.373 | Design and Operating Requirements |
| 724.376 | Food-Chain Crops |
| 724.378 | Unsaturated Zone Monitoring |
| 724.379 | Recordkeeping |
| 724.380 | Closure and Post-Closure Care |
| 724.381 | Special Requirements for Ignitable or Reactive Waste |
| 724.382 | Special Requirements for Incompatible Wastes |
| 724.383 | Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026, and F027 |
| 724.400 | Applicability |
| 724.401 | Design and Operating Requirements |
| 724.402 | Action Leakage Rate |
| 724.403 | Monitoring and Inspection |
| 724.404 | Response Actions |
| 724.409 | Surveying and Recordkeeping |
| 724.410 | Closure and Post-Closure Care |
| 724.412 | Special Requirements for Ignitable or Reactive Waste |
| 724.413 | Special Requirements for Incompatible Wastes |
| 724.414 | Special Requirements for Bulk and Containerized Liquids |
| 724.415 | Special Requirements for Containers |
| 724.416 | Disposal of Small Containers of Hazardous Waste in Overpacked Drums (Lab Packs) |
| 724.417 | Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026, and F027 |
| 724.440 | Applicability |
| 724.441 | Waste Analysis |
| 724.442 | Principal Organic Hazardous Constituents (POHCs) |
| 724.443 | Performance Standards |
| 724.444 | Hazardous Waste Incinerator Permits |
| 724.445 | Operating Requirements |
| 724.447 | Monitoring and Inspections |
| 724.451 | Closure |
| 724.650 | Applicability of Corrective Action Management Unit Regulations |
| 724.651 | Grandfathered Corrective Action Management Units |
| 724.652 | Corrective Action Management Units |
| 724.653 | Temporary Units |
| 724.654 | Staging Piles |
| 724.655 | Disposal of CAMU-Eligible Wastes in Permitted Hazardous Waste Landfills |
| 724.670 | Applicability |
| 724.671 | Assessment of Existing Drip Pad Integrity |
| 724.672 | Design and Installation of New Drip Pads |
| 724.673 | Design and Operating Requirements |
| 724.674 | Inspections |
| 724.675 | Closure |
| 724.700 | Applicability |
| 724.701 | Environmental Performance Standards |
| 724.702 | Monitoring, Analysis, Inspection, Response, Reporting, and Corrective Action |
| 724.703 | Post-Closure Care |
| 724.930 | Applicability |
| 724.931 | Definitions |
| 724.932 | Standards: Process Vents |
| 724.933 | Standards: Closed-Vent Systems and Control Devices |
| 724.934 | Test Methods and Procedures |
| 724.935 | Recordkeeping Requirements |
| 724.936 | Reporting Requirements |
| 724.950 | Applicability |
| 724.951 | Definitions |
| 724.952 | Standards: Pumps in Light Liquid Service |
| 724.953 | Standards: Compressors |
| 724.954 | Standards: Pressure Relief Devices in Gas/Vapor Service |
| 724.955 | Standards: Sampling Connecting Systems |
| 724.956 | Standards: Open-ended Valves or Lines |
| 724.957 | Standards: Valves in Gas/Vapor or Light Liquid Service |
| 724.958 | Standards: Pumps, Valves, Pressure Relief Devices, and Other Connectors |
| 724.959 | Standards: Delay of Repair |
| 724.960 | Standards: Closed-Vent Systems and Control Devices |
| 724.961 | Alternative Percentage Standard for Valves |
| 724.962 | Skip Period Alternative for Valves |
| 724.963 | Test Methods and Procedures |
| 724.964 | Recordkeeping Requirements |
| 724.965 | Reporting Requirements |
| 724.980 | Applicability |
| 724.981 | Definitions |
| 724.982 | Standards: General |
| 724.983 | Waste Determination Procedures |
| 724.984 | Standards: Tanks |
| 724.985 | Standards: Surface Impoundments |
| 724.986 | Standards: Containers |
| 724.987 | Standards: Closed-Vent Systems and Control Devices |
| 724.988 | Inspection and Monitoring Requirements |
| 724.989 | Recordkeeping Requirements |
| 724.990 | Reporting Requirements |
| 724.991 | Alternative Control Requirements for Tanks (Repealed) |
| 724.1100 | Applicability |
| 724.1101 | Design and Operating Standards |
| 724.1102 | Closure and Post-Closure Care |
| 724.1200 | Applicability |
| 724.1201 | Design and Operating Standards |
| 724.1202 | Closure and Post-Closure Care |
| 724.Appendix A | Recordkeeping Instructions |
| 724.Appendix B | EPA Report Form and Instructions (Repealed) |
| 724.Appendix D | Cochran’s Approximation to the Behrens-Fisher Student’s T-Test |
| 724.Appendix E | Examples of Potentially Incompatible Waste |
| 724.Appendix I | Groundwater Monitoring List |
| Section 724.103 | Relationship to Interim Status Standards |
| A facility owner or operator that has fully complied with the requirements for interim status | |
| BOARD NOTE: As stated in Section 21(f) of the Illinois Environmental Protection Act [415 ILCS 5/21(f)], the treatment, storage, or disposal of hazardous waste is prohibited, except in accordance with a RCRA permit. 35 Ill. Adm. Code 703, Subpart C provides for the continued operation of an existing facility that meets certain conditions until final administrative disposition of the owner’s or operator’s permit application. | |
| Section 724.114 | Security |
| a) | The owner or operator must prevent the unknowing entry, and minimize the possibility for the unauthorized entry, of persons or livestock onto the active portion of the facility, unless the owner or operator demonstrates the following to the Agency: |
| 1) | That physical contact with the waste, structures or equipment within the active portion of the facility will not injure unknowing or unauthorized persons or livestock that may enter the active portion of a facility; and |
| 2) | That disturbance of the waste or equipment, by the unknowing or unauthorized entry of persons or livestock onto the active portion of a facility, will not cause a violation of the requirements of this Part. |
| b) | Unless the owner or operator has made a successful demonstration under subsections (a)(1) and (a)(2) of this Section, a facility must have the following: |
| 1) | A 24-hour surveillance system (e.g., television monitoring or surveillance by guards or facility personnel) that continuously monitors and controls entry onto the active portion of the facility; or |
| 2) | Physical barriers. |
| A) | An artificial or natural barrier (e.g., a fence in good repair or a fence combined with a cliff), which completely surrounds the active portion of the facility; and |
| B) | A means to control entry, at all times, through the gates or other entrances to the active portion of the facility (e.g., an attendant, television monitors, locked entrance, or controlled roadway access to the facility). |
| c) | Unless the owner or operator has made a successful demonstration under subsections (a)(1) and (a)(2) of this Section, a sign with the legend, “Danger |
| Section 724.154 | Amendment of Contingency Plan |
| a) | The facility permit is revised; |
| b) | The plan fails in an emergency; |
| c) | The facility changes |
| d) | The list of emergency coordinators changes; or |
| e) | The list of emergency equipment changes. |
| Section 724.194 | Concentration Limits |
| a) | The Agency must specify in the facility permit concentration limits in the groundwater for hazardous constituents established under Section 724.193. The following must be true of the concentration of a hazardous constituent: |
| 1) | It must not exceed the background level of that constituent in the groundwater at the time that limit is specified in the permit; or |
| 2) | For any of the constituents listed in Table 1, it must not exceed the respective value given in that Table if the background level of the constituent is below the value given in Table 1; or |
| 3) | It must not exceed an alternative limit established by the Agency under subsection (b) of this Section. |
| TABLE 1 | |
|
Constituent |
Maximum Concentration (mg/ℓ) |
| Arsenic | 0.05 |
| Barium | 1.0 |
| Cadmium | 0.01 |
| Chromium | 0.05 |
| Lead | 0.05 |
| Mercury | 0.002 |
| Selenium | 0.01 |
| Silver | 0.05 |
| Endrin (1,2,3,4,10,10-hexachloro-6,7-epoxy-1,4,4a,5,6,7,8,8a-octahydro-endo,endo-1,4:5,8-dimethanonaphthalene) | 0.0002 |
| Lindane (1,2,3,4,5,6-hexachlorocyclohexane, gamma isomer) | 0.004 |
| Methoxychlor (1,1,1-Trichloro-2,2'-bis-(p-methoxyphenyl)ethane) | 0.1 |
| Toxaphene (Technical chlorinated camphene, 67-69 percent chlorine) | 0.005 |
| 2,4-D (2,4-Dichlorophenoxyacetic acid) | 0.1 |
| 2,4,5-TP (Silvex) (2,4,5-Trichlorophenoxypropionic acid) | 0.01 |
| b) | The Agency must establish an alternative concentration limit for a hazardous constituent if it finds that the constituent will not pose a substantial present or potential hazard to human health or the environment as long as the alternative concentration limit is not exceeded. In establishing alternate concentration limits, the Agency must consider the following factors: |
| 1) | Potential adverse effects on groundwater quality, considering the following: |
| A) | The physical and chemical characteristics of the waste in the regulated unit, including its potential for migration; |
| B) | The hydrogeological characteristics of the facility and surrounding land; |
| C) | The quantity of groundwater and the direction of groundwater flow; |
| D) | The proximity and withdrawal rates of groundwater users; |
| E) | The current and future uses of groundwater in the area; |
| F) | The existing quality of groundwater, including other sources of contamination and their cumulative impact on the groundwater quality; |
| G) | The potential for health risks caused by human exposure to waste constituents; |
| H) | The potential damage to wildlife, crops, vegetation, and physical structures caused by exposure to waste constituents; |
| I) | The persistence and permanence of the potential adverse effects; and |
| 2) | Potential adverse effects on hydraulically-connected surface-water quality, considering the following: |
| A) | The volume and physical and chemical characteristics of the waste in the regulated unit; |
| B) | The hydrogeological characteristics of the facility and surrounding land; |
| C) | The quantity and quality of groundwater and the direction of groundwater flow; |
| D) | The patterns of rainfall in the region; |
| E) | The proximity of the regulated unit to surface waters; |
| F) | The current and future uses of surface waters in the area and any water quality standards established for those surface waters; |
| G) | The existing quality of surface water, including other sources of contamination and the cumulative impact on surface-water quality; |
| H) | The potential for health risks caused by human exposure to waste constituents; |
| I) | The potential damage to wildlife, crops, vegetation, and physical structures caused by exposure to waste constituents; and |
| J) | The persistence and permanence of the potential adverse effects. |
| c) | In making any determination under subsection (b) of this Section about the use of groundwater in the area around the facility, the Agency must consider any identification of underground sources of drinking water and exempted aquifers made under 35 Ill. Adm. Code 704.123. |
| d) | The Agency must make specific written findings in setting any alternate concentration limits under subsection (b) of this Section. |
SUBPART N: LANDFILLS
| ||
| Section 724.416 | Disposal of Small Containers of Hazardous Waste in Overpacked Drums (Lab Packs) |
| Small containers of hazardous waste in overpacked drums (lab packs) may be placed in a landfill if the following requirements are met: | |
| a) | Hazardous waste must be packaged in non-leaking inside containers. The inside containers must be of a design and constructed of a material that will not react dangerously with, be decomposed by, or be ignited by the contained waste. The inside containers must be tightly and securely sealed. The inside containers must be of the size and type specified in the USDOT hazardous materials regulations (49 CFR 173 (Shippers |
| b) | The inside containers must be overpacked in an open head USDOT-specification metal shipping container (49 CFR 178 (Specifications for Packagings) and 179 (Specifications for Tank Cars)) of no more than 416 liter (110 gallon) capacity and surrounded by, at a minimum, a sufficient quantity of sorbent material, determined to be nonbiodegradable in accordance with Section 724.414(e), to completely sorb all of the liquid contents of the inside containers. The metal outer container must be full after packing with inside containers and sorbent material. |
| c) | In accordance with Section 724.117(b), the sorbent material used must not be capable of reacting dangerously with, being decomposed by, or being ignited by the contents of the inside containers, in accordance with Section 724.117(b). |
| d) | Incompatible waste, as defined in 35 Ill. Adm. Code 720.110, must not be placed in the same outside container. |
| e) | Reactive wastes, other than cyanide- or sulfide-bearing waste as defined in 35 Ill. Adm. Code 721.123(a)(5), must be treated or rendered non-reactive prior to packaging in accordance with subsections (a) through (d) of this Section. Cyanide- and sulfide-bearing reactive waste may be packed in accordance with subsections (a) through (d) of this Section without first being treated or rendered non-reactive. |
| f) | Such disposal is in compliance with 35 Ill. Adm. Code 728. Persons who incinerate lab packs according to 35 Ill. Adm. Code 728.142(c)(1) may use fiber drums in place of metal outer containers. Such fiber drums must meet the USDOT specifications in 49 CFR 173.12 (Exceptions for Shipments of Waste Materials), incorporated by reference in 35 Ill. Adm. Code 720.111(b), and be overpacked according to the requirements of subsection (b) of this Section. |
| g) | Pursuant to 35 Ill. Adm. Code 729.312, the use of labpacks for disposal of liquid wastes or wastes containing free liquids allowed under this Section is restricted to labwaste and non-periodic waste, as those terms are defined in that Part. |
| Section 724.440 | Applicability |
| a) | The regulations in this Subpart O apply to owners and operators of hazardous waste incinerators (as defined in 35 Ill. Adm. Code 720.110), except as Section 724.101 provides otherwise. |
| b) | Integration of the MACT standards. |
| 1) | Except as provided by subsections (b)(2) through |
| 2) | The MACT standards of subpart EEE of 40 CFR 63 do not replace the closure requirements of Section 724.451 or the applicable requirements of Subparts A through H, BB, and CC of this Part. |
| 3) | The particulate matter standard of Section 724.443(c) remains in effect for incinerators that elect to comply with the alternative to the particulate matter standard of 40 CFR 63.1206(b)(14) and 63.1219(e) (When and How Must You Comply with the Standards and Operating Requirements?), incorporated by reference in 35 Ill. Adm. Code 720.111(b). |
| 4) | The following requirements remain in effect for startup, shutdown, and malfunction events if the owner or operator elects to comply with 35 Ill. Adm. Code 703.320(a)(1)(A) to minimize emissions of toxic compounds from the following events: |
| A) | Section 724.445(a), requiring that an incinerator operate in accordance with operating requirements specified in the permit; and |
| B) | Section 724.445(c), requiring compliance with the emission standards and operating requirements during startup and shutdown if hazardous waste is in the combustion chamber, except for particular hazardous wastes. |
| c) | After consideration of the waste analysis included with Part B of the permit application, the Agency, in establishing the permit conditions, must exempt the applicant from all requirements of this Subpart O, except Section 724.441 (Waste Analysis) and Section 724.451 (Closure): |
| 1) | If the Agency finds that the waste to be burned is one of the following: |
| A) | It is listed as a hazardous waste in Subpart D of 35 Ill. Adm. Code 721 solely because it is ignitable (Hazard Code I), corrosive (Hazard Code C), or both; |
| B) | It is listed as a hazardous waste in Subpart D of 35 Ill. Adm. Code 721 solely because it is reactive (Hazard Code R) for characteristics other than those listed in Section 721.123(a)(4) and (5), and will not be burned when other hazardous wastes are present in the combustion zone; |
| C) | It is a hazardous waste solely because it possesses the characteristic of ignitability, as determined by the test for characteristics of hazardous wastes pursuant to Subpart C of 35 Ill. Adm. Code 721; or |
| D) | It is a hazardous waste solely because it possesses any of the reactivity characteristics described by 35 Ill. Adm. Code 721.123(a)(1), (a)(2), (a)(3), (a)(6), (a)(7), and (a)(8) and will not be burned when other hazardous wastes are present in the combustion zone; and |
| 2) | If the waste analysis shows that the waste contains none of the hazardous constituents listed in Subpart H of 35 Ill. Adm. Code 721 that would reasonably be expected to be in the waste. |
| d) | If the waste to be burned is one that is described by subsection (b)(1)(A), (b)(1)(B), (b)(1)(C), or (b)(1)(D) of this Section and contains insignificant concentrations of the hazardous constituents listed in Subpart H of 35 Ill. Adm. Code 721, then the Agency may, in establishing permit conditions, exempt the applicant from all requirements of this Subpart O, except Section 724.441 (Waste Analysis) and Section 724.451 (Closure), after consideration of the waste analysis included with Part B of the permit application, unless the Agency finds that the waste will pose a threat to human health or the environment when burned in an incinerator. |
| e) | The owner or operator of an incinerator may conduct trial burns subject only to the requirements of 35 Ill. Adm. Code 703.222 through 703.225 (short-term and incinerator permits). |
| Section 724.982 | Standards: General |
| a) | This Section applies to the management of hazardous waste in tanks, surface impoundments, and containers subject to this Subpart CC. |
| b) | The owner or operator must control air pollutant emissions from each waste management unit in accordance with the standards specified in Sections 724.984 through 724.987, as applicable to the waste management unit, except as provided for in subsection (c) of this Section. |
| c) | A tank, surface impoundment, or container is exempt from standards specified in Sections 724.984 through 724.987, as applicable, provided that all hazardous waste placed in the waste management unit is one of the following: |
| 1) | A tank, surface impoundment, or container for which all hazardous waste entering the unit has an average VO concentration at the point of waste origination of less than 500 parts per million by weight (ppmw). The average VO concentration must be determined by the procedures specified in Section 724.983(a). The owner or operator must review and update, as necessary, this determination at least once every 12 months following the date of the initial determination for the hazardous waste streams entering the unit. |
| 2) | A tank, surface impoundment, or container for which the organic content of all the hazardous waste entering the waste management unit has been reduced by an organic destruction or removal process that achieves any one of the following conditions: |
| A) | The process removes or destroys the organics contained in the hazardous waste to a level such that the average VO concentration of the hazardous waste at the point of waste treatment is less than the exit concentration limit (Ct) established for the process. The average VO concentration of the hazardous waste at the point of waste treatment and the exit concentration limit for the process must be determined using the procedures specified in Section 724.983(b). |
| B) | The process removes or destroys the organics contained in the hazardous waste to a level such that the organic reduction efficiency (R) for the process is equal to or greater than 95 percent, and the average VO concentration of the hazardous waste at the point of waste treatment is less than 100 ppmw. The organic reduction efficiency for the process and the average VO concentration of the hazardous waste at the point of waste treatment must be determined using the procedures specified in Section 724.983(b). |
| C) | The process removes or destroys the organics contained in the hazardous waste to such a level that the actual organic mass removal rate (MR) for the process is equal to or greater than the required organic mass removal rate (RMR) established for the process. The required organic mass removal rate and the actual organic mass removal rate for the process must be determined using the procedures specified in Section 724.983(b). |
| D) | The process is a biological process that destroys or degrades the organics contained in the hazardous waste so that either of the following conditions are met: |
| i) | The organic reduction efficiency (R) for the process is equal to or greater than 95 percent, and the organic biodegradation efficiency (Rbio) for the process is equal to or greater than 95 percent. The organic reduction efficiency and the organic biodegradation efficiency for the process must be determined using the procedures specified in Section 724.983(b). |
| ii) | The total actual organic mass biodegradation rate (MRbio) for all hazardous waste treated by the process is equal to or greater than the required organic mass removal rate (RMR). The required organic mass removal rate and the actual organic mass biodegradation rate for the process must be determined using the procedures specified in Section 724.983(b). |
| E) | The process removes or destroys the organics contained in the hazardous waste and meets all of the following conditions: |
| i) | From the point of waste origination through the point where the hazardous waste enters the treatment process, the hazardous waste is continuously managed in waste management units that use air emission controls in accordance with the standards specified in Sections 724.984 through 724.987, as applicable to the waste management unit. |
| ii) | From the point of waste origination through the point where the hazardous waste enters the treatment process, any transfer of the hazardous waste is accomplished through continuous hard-piping or other closed system transfer that does not allow exposure of the waste to the atmosphere. |
| iii) | The average VO concentration of the hazardous waste at the point of waste treatment is less than the lowest average VO concentration at the point of waste origination, determined for each of the individual hazardous waste streams entering the process or 500 ppmw, whichever value is lower. The average VO concentration of each individual hazardous waste stream at the point of waste origination must be determined using the procedures specified in Section 724.983(a). The average VO concentration of the hazardous waste at the point of waste treatment must be determined using the procedures specified in Section 724.983(b). |
| F) | A process that removes or destroys the organics contained in the hazardous waste to a level such that the organic reduction efficiency (R) for the process is equal to or greater than 95 percent and the owner or operator certifies that the average VO concentration at the point of waste origination for each of the individual waste streams entering the process is less than 10,000 ppmw. The organic reduction efficiency for the process and the average VO concentration of the hazardous waste at the point of waste origination must be determined using the procedures specified in Section 724.983(b) and Section 724.983(a), respectively. |
| G) | A hazardous waste incinerator for which either of the following conditions is true: |
| i) | The owner or operator has been issued a final permit under 35 Ill. Adm. Code 702, 703, and 705 that implements the requirements of Subpart H of 35 Ill. Adm. Code 726; or |
| ii) | The owner or operator has designed and operates the incinerator in accordance with the interim status requirements of Subpart O of 35 Ill. Adm. Code 725. |
| H) | A boiler or industrial furnace for which either of the following conditions is true: |
| i) | The owner or operator has been issued a final permit under 35 Ill. Adm. Code 702, 703, and 705 that implements the requirements of Subpart H of 35 Ill. Adm. Code 726; or |
| ii) | The owner or operator has designed and operates the boiler or industrial furnace in accordance with the interim status requirements of Subpart O of 35 Ill. Adm. Code 725. |
| I) | For the purpose of determining the performance of an organic destruction or removal process in accordance with the conditions in each of subsections (c)(2)(A) through (c)(2)(F) of this Section, the owner or operator must account for VO concentrations determined to be below the limit of detection of the analytical method by using the following VO concentration: |
| i) | If Method 25D (Determination of the Volatile Organic Concentration of Waste Samples) in appendix A to 40 CFR 60 (Test Methods), incorporated by reference in 35 Ill. Adm. Code 720.111(b), is used for the analysis, one-half the blank value determined in Section 4.4 of the method or a value of 25 ppmw, whichever is less. |
| ii) | If any other analytical method is used, one-half the sum of the limits of detection established for each organic constituent in the waste that has a Henry’s law constant value at least 0.1 mole-fraction-in-the-gas-phase/mole-fraction-in-the-liquid-phase (0.1 Y/X) (which can also be expressed as 1.8 ´ 10-6 atmospheres/gram-mole/m3) at 25° C. |
| 3) | A tank or surface impoundment used for biological treatment of hazardous waste in accordance with the requirements of subsection (c)(2)(D) of this Section. |
| 4) | A tank, surface impoundment, or container for which all hazardous waste placed in the unit fulfills either of the following conditions: |
| A) | It meets the numerical concentration limits for organic hazardous constituents, applicable to the hazardous waste, as specified in Table T to 35 Ill. Adm. Code 728; or |
| B) | The organic hazardous constituents in the waste have been treated by the treatment technology established by USEPA for the waste, as set forth in 35 Ill. Adm. Code 728.142(a), or have been removed or destroyed by an equivalent method of treatment approved by the Agency pursuant to 35 Ill. Adm. Code 728.142(b). |
| 5) | A tank used for bulk feed of hazardous waste to a waste incinerator and all of the following conditions are met: |
| A) | The tank is located inside an enclosure vented to a control device that is designed and operated in accordance with all applicable requirements specified under federal subpart FF of 40 CFR 61 (National Emission Standard for Benzene Waste Operations), incorporated by reference in 35 Ill. Adm. Code 720.111(b), for a facility at which the total annual benzene quantity from the facility waste is equal to or greater than 10 megagrams (11 tons) per year; |
| B) | The enclosure and control device serving the tank were installed and began operation prior to November 25, 1996; and |
| C) | The enclosure is designed and operated in accordance with the criteria for a permanent total enclosure as specified in “Procedure T |
| d) | The Agency may at any time perform or request that the owner or operator perform a waste determination for a hazardous waste managed in a tank, surface impoundment, or container that is exempted from using air emission controls under the provisions of this Section, as follows: |
| 1) | The waste determination for average VO concentration of a hazardous waste at the point of waste origination must be performed using direct measurement in accordance with the applicable requirements of Section 724.983(a). The waste determination for a hazardous waste at the point of waste treatment must be performed in accordance with the applicable requirements of Section 724.983(b). |
| 2) | In performing a waste determination pursuant to subsection (d)(1) of this Section, the sample preparation and analysis must be conducted as follows: |
| A) | In accordance with the method used by the owner or operator to perform the waste analysis, except in the case specified in subsection (d)(2)(B) of this Section. |
| B) | If the Agency determines that the method used by the owner or operator was not appropriate for the hazardous waste managed in the tank, surface impoundment, or container, then the Agency may choose an appropriate method. |
| 3) | Where the owner or operator is requested to perform the waste determination, the Agency may elect to have an authorized representative observe the collection of the hazardous waste samples used for the analysis. |
| 4) | Where the results of the waste determination performed or requested by the Agency do not agree with the results of a waste determination performed by the owner or operator using knowledge of the waste, then the results of the waste determination performed in accordance with the requirements of subsection (d)(1) of this Section must be used to establish compliance with the requirements of this Subpart CC. |
| 5) | Where the owner or operator has used an averaging period greater than one hour for determining the average VO concentration of a hazardous waste at the point of waste origination, the Agency may elect to establish compliance with this Subpart CC by performing or requesting that the owner or operator perform a waste determination using direct measurement based on waste samples collected within a one-hour period, as follows: |
| A) | The average VO concentration of the hazardous waste at the point of waste origination must be determined by direct measurement in accordance with the requirements of Section 724.983(a). |
| B) | Results of the waste determination performed or requested by the Agency showing that the average VO concentration of the hazardous waste at the point of waste origination is equal to or greater than 500 ppmw must constitute noncompliance with this Subpart CC, except in a case as provided for in subsection (d)(5)(C) of this Section. |
| C) | Where the average VO concentration of the hazardous waste at the point of waste origination previously has been determined by the owner or operator using an averaging period greater than one hour to be less than 500 ppmw but because of normal operating process variations the VO concentration of the hazardous waste determined by direct measurement for any given one-hour period may be equal to or greater than 500 ppmw, information that was used by the owner or operator to determine the average VO concentration of the hazardous waste (e.g., test results, measurements, calculations, and other documentation) and recorded in the facility records in accordance with the requirements of Section 724.983(a) and Section 724.989 must be considered by the Agency together with the results of the waste determination performed or requested by the Agency in establishing compliance with this Subpart CC. |
| Section 724.989 | Recordkeeping Requirements |
| a) | Each owner or operator of a facility subject to the requirements of this Subpart CC must record and maintain the information specified in subsections (b) through (j) of this Section, as applicable to the facility. Except for air emission control equipment design documentation and information required by subsections (i) and (j) of this Section, records required by this Section must be maintained in the operating record for a minimum of three years. Air emission control equipment design documentation must be maintained in the operating record until the air emission control equipment is replaced or is otherwise no longer in service. Information required by subsections (i) and (j) of this Section must be maintained in the operating record for as long as the waste management unit is not using air emission controls specified in Sections 724.984 through 724.987, in accordance with the conditions specified in Section 724.980(d) or (b)(7), respectively. |
| b) | The owner or operator of a tank using air emission controls in accordance with the requirements of Section 724.984 must prepare and maintain records for the tank that include the following information: |
| 1) | For each tank using air emission controls in accordance with the requirements of Section 724.984, the owner or operator must record the following: |
| A) | A tank identification number (or other unique identification description, as selected by the owner or operator). |
| B) | A record for each inspection required by Section 724.984 that includes the following information: |
| i) | Date inspection was conducted. |
| ii) | For each defect detected during the inspection: the location of the defect, a description of the defect, the date of detection, and corrective action taken to repair the defect. In the event that repair of the defect is delayed in accordance with the requirements of Section 724.984, the owner or operator must also record the reason for the delay and the date that completion of repair of the defect is expected. |
| 2) | In addition to the information required by subsection (b)(1) of this Section, the owner or operator must record the following information, as applicable to the tank: |
| A) | The owner or operator using a fixed roof to comply with the Tank Level 1 control requirements specified in Section 724.984(c) must prepare and maintain records for each determination for the maximum organic vapor pressure of the hazardous waste in the tank performed in accordance with the requirements of Section 724.984(c). The records must include the date and time the samples were collected, the analysis method used, and the analysis results. |
| B) | The owner or operator using an internal floating roof to comply with the Tank Level 2 control requirements specified in Section 724.984(e) must prepare and maintain documentation describing the floating roof design. |
| C) | Owners and operators using an external floating roof to comply with the Tank Level 2 control requirements specified in Section 724.984(f) must prepare and maintain the following records: |
| i) | Documentation describing the floating roof design and the dimensions of the tank. |
| ii) | Records for each seal gap inspection required by Section 724.984(f)(3) describing the results of the seal gap measurements. The records must include the date that the measurements were performed, the raw data obtained for the measurements, and the calculations of the total gap surface area. In the event that the seal gap measurements do not conform to the specifications in Section 724.984(f)(1), the records must include a description of the repairs that were made, the date the repairs were made, and the date the tank was emptied, if necessary. |
| D) | Each owner or operator using an enclosure to comply with the Tank Level 2 control requirements specified in Section 724.984(i) must prepare and maintain the following records: |
| i) | Records for the most recent set of calculations and measurements performed by the owner or operator to verify that the enclosure meets the criteria of a permanent total enclosure as specified in “Procedure T |
| ii) | Records required for the closed-vent system and control device in accordance with the requirements of subsection (e) of this Section. |
| c) | The owner or operator of a surface impoundment using air emission controls in accordance with the requirements of Section 724.985 must prepare and maintain records for the surface impoundment that include the following information: |
| 1) | A surface impoundment identification number (or other unique identification description as selected by the owner or operator). |
| 2) | Documentation describing the floating membrane cover or cover design, as applicable to the surface impoundment, that includes information prepared by the owner or operator or provided by the cover manufacturer or vendor describing the cover design, and certification by the owner or operator that the cover meets the specifications listed in Section 724.985(c). |
| 3) | A record for each inspection required by Section 724.985 that includes the following information: |
| A) | Date inspection was conducted. |
| B) | For each defect detected during the inspection the following information: the location of the defect, a description of the defect, the date of detection, and corrective action taken to repair the defect. In the event that repair of the defect is delayed in accordance with the provisions of Section 724.985(f), the owner or operator must also record the reason for the delay and the date that completion of repair of the defect is expected. |
| 4) | For a surface impoundment equipped with a cover and vented through a closed-vent system to a control device, the owner or operator must prepare and maintain the records specified in subsection (e) of this Section. |
| d) | The owner or operator of containers using Container Level 3 air emission controls in accordance with the requirements of Section 724.986 must prepare and maintain records that include the following information: |
| 1) | Records for the most recent set of calculations and measurements performed by the owner or operator to verify that the enclosure meets the criteria of a permanent total enclosure as specified in “Procedure T |
| 2) | Records required for the closed-vent system and control device in accordance with the requirements of subsection (e) of this Section. |
| e) | The owner or operator using a closed-vent system and control device in accordance with the requirements of Section 724.987 must prepare and maintain records that include the following information: |
| 1) | Documentation for the closed-vent system and control device that includes the following: |
| A) | Certification that is signed and dated by the owner or operator stating that the control device is designed to operate at the performance level documented by a design analysis as specified in subsection (e)(1)(B) of this Section or by performance tests as specified in subsection (e)(1)(C) of this Section when the tank, surface impoundment, or container is or would be operating at capacity or the highest level reasonably expected to occur. |
| B) | If a design analysis is used, then design documentation, as specified in Section 724.935(b)(4). The documentation must include information prepared by the owner or operator or provided by the control device manufacturer or vendor that describes the control device design in accordance with Section 724.935(b)(4)(C) and certification by the owner or operator that the control equipment meets the applicable specifications. |
| C) | If performance tests are used, then a performance test plan as specified in Section 724.935(b)(3) and all test results. |
| D) | Information as required by Section 724.935(c)(1) and Section 724.935(c)(2), as applicable. |
| E) | An owner or operator must record, on a semiannual basis, the information specified in subsections (e)(1)(E)(i) and (e)(1)(E)(ii) of this Section for those planned routine maintenance operations that would require the control device not to meet the requirements of Section 724.987(c)(1)(A), (c)(1)(B), or (c)(1)(C) of this Section, as applicable. |
| i) | A description of the planned routine maintenance that is anticipated to be performed for the control device during the next six-month period. This description must include the type of maintenance necessary, planned frequency of maintenance, and lengths of maintenance periods. |
| ii) | A description of the planned routine maintenance that was performed for the control device during the previous six-month period. This description must include the type of maintenance performed and the total number of hours during those six months that the control device did not meet the requirements of Section 724.987(c)(1)(A), (c)(1)(B), or (c)(1)(C), as applicable, due to planned routine maintenance. |
| F) | An owner or operator must record the information specified in subsections (e)(1)(F)(i) through (e)(1)(F)(iii) of this Section for those unexpected control device system malfunctions that would require the control device not to meet the requirements of Section 724.987 (c)(1)(A), (c)(1)(B), or (c)(1)(C) of this Section, as applicable. |
| i) | The occurrence and duration of each malfunction of the control device system. |
| ii) | The duration of each period during a malfunction when gases, vapors, or fumes are vented from the waste management unit through the closed-vent system to the control device while the control device is not properly functioning. |
| iii) | Actions taken during periods of malfunction to restore a malfunctioning control device to its normal or usual manner of operation. |
| G) | Records of the management of carbon removed from a carbon adsorption system conducted in accordance with Section 724.987(c)(3)(B). |
| f) | The owner or operator of a tank, surface impoundment, or container exempted from standards in accordance with the provisions of Section 724.982(c) must prepare and maintain the following records, as applicable: |
| 1) | For tanks, surface impoundments, or containers exempted under the hazardous waste organic concentration conditions specified in Section 724.982(c)(1) or (c)(2)(A) through (c)(2)(E), the owner or operator must record the information used for each waste determination (e.g., test results, measurements, calculations, and other documentation) in the facility operating log. If analysis results for waste samples are used for the waste determination, then the owner or operator must record the date, time, and location that each waste sample is collected in accordance with the applicable requirements of Section 724.983. |
| 2) | For tanks, surface impoundments, or containers exempted under the provisions of Section 724.982(c)(2)(G) or (c)(2)(H), the owner or operator must record the identification number for the incinerator, boiler, or industrial furnace in which the hazardous waste is treated. |
| g) | An owner or operator designating a cover as “unsafe to inspect and monitor” pursuant to Section 724.984(l) or Section 724.985(g) must record in a log that is kept in the facility operating record the following information: the identification numbers for waste management units with covers that are designated as “unsafe to inspect and monitor,” the explanation for each cover stating why the cover is unsafe to inspect and monitor, and the plan and schedule for inspecting and monitoring each cover. |
| h) | The owner or operator of a facility that is subject to this Subpart CC and to the control device standards in federal subpart VV of 40 CFR 60 (Standards of Performance for Equipment Leaks of VOC in the Synthetic Organic Chemicals Manufacturing Industry) or subpart V of 40 CFR 61 (National Emission Standard for Equipment Leaks (Fugitive Emission Sources)), each incorporated by reference in 35 Ill. Adm. Code 720.111(b), may elect to demonstrate compliance with the applicable Sections of this Subpart CC by documentation either pursuant to this Subpart CC, or pursuant to the provisions of subpart VV of 40 CFR 60 or subpart V of 40 CFR 61, to the extent that the documentation required by 40 CFR 60 or 61 duplicates the documentation required by this Section. |
| i) | For each tank or container not using air emission controls specified in Sections 724.984 through 724.987 in accordance with the conditions specified in Section 724.980(d), the owner or operator must record and maintain the following information: |
| 1) | A list of the individual organic peroxide compounds manufactured at the facility that meet the conditions specified in Section 724.980(d)(1). |
| 2) | A description of how the hazardous waste containing the organic peroxide compounds identified pursuant to subsection (i)(1) of this Section are managed at the facility in tanks and containers. This description must include the following information: |
| A) | For the tanks used at the facility to manage this hazardous waste, sufficient information must be provided to describe the following for each tank: a facility identification number for the tank, the purpose and placement of this tank in the management train of this hazardous waste, and the procedures used to ultimately dispose of the hazardous waste managed in the tanks. |
| B) | For containers used at the facility to manage this hazardous waste, sufficient information must be provided to describe each tank: a facility identification number for the container or group of containers, the purpose and placement of this container or group of containers in the management train of this hazardous waste, and the procedures used to ultimately dispose of the hazardous waste managed in the containers. |
| 3) | An explanation of why managing the hazardous waste containing the organic peroxide compounds identified pursuant to subsection (i)(1) of this Section in the tanks or containers identified pursuant to subsection (i)(2) of this Section would create an undue safety hazard if the air emission controls specified in Sections 724.984 through 724.987 were installed and operated on these waste management units. This explanation must include the following information: |
| A) | For tanks used at the facility to manage this hazardous waste, sufficient information must be provided to explain the following: how use of the required air emission controls on the tanks would affect the tank design features and facility operating procedures currently used to prevent an undue safety hazard during management of this hazardous waste in the tanks; and why installation of safety devices on the required air emission controls, as allowed under this Subpart CC, would not address those situations in which evacuation of tanks equipped with these air emission controls is necessary and consistent with good engineering and safety practices for handling organic peroxides. |
| B) | For containers used at the facility to manage this hazardous waste, sufficient information must be provided to explain the following: how use of the required air emission controls on the tanks would affect the container design features and handling procedures currently used to prevent an undue safety hazard during management of this hazardous waste in the containers; and why installation of safety devices on the required air emission controls, as allowed under this Subpart CC, would not address those situations in which evacuation of containers equipped with these air emission controls is necessary and consistent with good engineering and safety practices for handling organic peroxides. |
| j) | For each hazardous waste management unit not using air emission controls specified in Sections 724.984 through 724.987 in accordance with the requirements of Section 724.980(b)(7), the owner and operator must record and maintain the following information: |
| 1) | The certification that the waste management unit is equipped with and operating air emission controls in accordance with the requirements of an applicable federal Clean Air Act regulation codified under 40 CFR 60, 61, or 63. |
| 2) | An identification of the specific federal requirements codified under 40 CFR 60, 61, or 63 with which the waste management unit is in compliance. |
| Section 724.Appendix I | |
| Groundwater Monitoring List | |
| a) | Common names are those widely used in government regulations, scientific publications and commerce; synonyms exist for many chemicals. |
| b) | “CAS RN” means “Chemical Abstracts Service Registry Number.” Where “total” is entered, all species in the groundwater that contain this element are included. |
| c) | CAS index names are those used in the 9th Cumulative index. |
| d) | PCBs (CAS RN 1336-36-3). This category contains congener chemicals, including constituents Aroclor-1016 (CAS RN 12674-11-2), Aroclor-1221 (CAS RN 11104-28-2), Aroclor-1232 (CAS RN 11141-16-5), Aroclor-1242 (CAS RN 53469-21-9), Aroclor-1248 (CAS RN 12672-29-6), Aroclor-1254 (CAS RN 11097-69-1) and Aroclor-1260 (CAS RN 11096-82-5). |
| e) | PCDDs. This category includes congener chemicals, including tetrachlorodibenzo-p-dioxins (see also 2,3,7,8-TCDD), pentachlorodibenzo-p-dioxins and hexachlorodibenzo-p-dioxins. |
| f) | PCDFs. This category contains congener chemicals, including tetrachlorodibenzofurans, pentachlorodibenzofurans, and hexachlorodibenzofurans. |
| Common Name | CAS RN | Chemical Abstracts Service Index Name |
Acenaphthene
|
83-32-9 | Acenaphthylene, 1,2-dihydro- |
| Acenaphthylene | 208-96-8 | Acenaphthylene |
| Acetone | 67-64-1 | 2-Propanone |
| Acetophenone | 98-86-2 | Ethanone, 1-phenyl- |
| Acetonitrile; Methyl cyanide | 75-05-8 | Acetonitrile |
| 2-Acetylaminofluorene; 2-AAF | 53-96-3 | Acetamide, N-9H-fluoren-2-yl- |
| Acrolein | 107-02-8 | 2-Propenal |
| Acrylonitrile | 107-13-1 | 2-Propenenitrile |
| Aldrin | 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 )- |
| Allyl chloride | 107-05-1 | 1-Propene, 3-chloro- |
| 4-Aminobiphenyl | 92-67-1 | (1,1'-Biphenyl)-4-amine |
| Aniline | 62-53-3 | Benzenamine |
| Anthracene | 120-12-7 | Anthracene |
| Antimony | (Total) | Antimony |
| Aramite | 140-57-8 | Sulfurous acid, 2-chloroethyl 2-(4-(1,1-dimethylethyl)phenoxy)-1-methylethyl ester |
| Arsenic | (Total) | Arsenic |
| Barium | (Total) | Barium |
| Benzene | 71-43-2 | Benzene |
| Benzo(a)anthracene; Benzanthracene | 56-55-3 | Benz(a)anthracene |
| Benzo(b)fluoranthene | 205-99-2 | Benz(e)acephenanthrylene |
| Benzo(k)fluoranthene | 207-08-9 | Benzo(k)fluoranthene |
| Benzo(ghi)perylene | 191-24-2 | Benzo(ghi)perylene |
| Benzo(a)pyrene | 50-32-8 | Benzo(a)pyrene |
| Benzyl alcohol | 100-51-6 | Benzenemethanol |
| Beryllium | (Total) | Beryllium |
| a -BHC | 319-84-6 | Cyclohexane, 1,2,3,4,5,6-hexachloro-, (1 a ,2 a ,3 b ,4 a ,5 b ,6 b )- |
| b -BHC | 319-85-7 | Cyclohexane, 1,2,3,4,5,6-hexachloro-, (1 a ,2 b ,3 a ,4 b ,5 a ,6 b )- |
| d -BHC | 319-86-8 | Cyclohexane, 1,2,3,4,5,6-hexachloro-, (1 a ,2 a ,3 a ,4 b ,5 a ,6 b )- |
| g -BHC; Lindane | 58-89-9 | Cyclohexane, 1,2,3,4,5,6-hexachloro-, (1 a ,2 a ,3 b ,4 a ,5 a ,6 b )- |
| Bis(2-chloroethoxy)methane | 111-91-1 | Ethane, 1,1'-(methylenebis(oxy))bis(2-chloro- |
| Bis(2-chloroethyl) ether | 111-44-4 | Ethane, 1,1'-oxybis(2-chloro- |
| Bis(2-chloro-1-methylethyl) ether; 2,2'-Dichlorodiisopropyl ether | 108-60-1 | Propane, 2,2'-oxybis(1-chloro- |
| Bis(2-ethylhexyl) phthalate | 117-81-7 | 1,2-Benzenedicarboxylic acid, bis(2-ethylhexyl) ester |
| Bromodichloromethane | 75-27-4 | Methane, bromodichloro- |
| Bromoform; Tribromomethane | 75-25-2 | Methane, tribromo- |
| 4-Bromophenyl phenyl ether | 101-55-3 | Benzene, 1-bromo-4-phenoxy- |
| Butyl benzyl phthalate; Benzyl butyl phthalate | 85-68-7 | 1,2-Benzenedicarboxylic acid, butyl phenylmethyl ester |
| Cadmium | Total | Cadmium |
| Carbon disulfide | 75-15-0 | Carbon disulfide |
| Carbon tetrachloride | 56-23-5 | Methane, tetrachloro- |
| Chlordane | 57-74-9 | 4,7-Methano-1H-indene,1,2,4,5,6,7,8,8-octachloro-2,3,3a,4,7,7a-hexahydro- |
| p-Chloroaniline | 106-47-8 | Benzeneamine, 4-chloro- |
| Chlorobenzene | 108-90-7 | Benzene, chloro- |
| Chlorobenzilate | 510-15-6 | Benzeneacetic acid, 4-chloro- a -(4-chlorophenyl)- a -hydroxy-, ethyl ester |
| p-Chloro-m-cresol | 59-50-7 | Phenol, 4-chloro-3-methyl- |
| Chloroethane; Ethyl chloride | 75-00-3 | Ethane, chloro- |
| Chloroform | 67-66-3 | Methane, trichloro- |
| 2-Chloronapthalene | 91-58-7 | Naphthalene, 2-chloro- |
| 2-Chlorophenol | 95-57-8 | Phenol, 2-chloro- |
| 4-Chlorophenyl phenyl ether | 7005-72-3 | Benzene, 1-chloro-4-phenoxy- |
| Chloroprene | 126-99-8 | 1,3-Butadiene, 2-chloro- |
| Chromium | (Total) | Chromium |
| Chrysene | 218-01-9 | Chrysene |
| Cobalt | (Total) | Cobalt |
| Copper | (Total) | Copper |
| m-Cresol | 108-39-4 | Phenol, 3-methyl- |
| o-Cresol | 95-48-7 | Phenol, 2-methyl- |
| p-Cresol | 106-44-5 | Phenol, 4-methyl- |
| Cyanide | 57-12-5 | Cyanide |
| 2,4-D; 2,4-Dichlorophenoxyacetic acid | 94-75-7 | Acetic acid, (2,4-dichlorophenoxy)- |
| 4,4'-DDD | 72-54-8 | Benzene, 1,1'-(2,2-dichloroethylidene)bis(4-chloro- |
| 4,4'-DDE | 72-55-9 | Benzene, 1,1'-(dichloroethylidene)bis(4-chloro- |
| 4,4'-DDT | 50-29-3 | Benzene, 1,1'-(2,2,2-trichloroethylidene)bis(4-chloro- |
| Diallate | 2303-16-4 | Carbamothioic acid, bis(1-methylethyl)-, |
| Dibenz(a,h)anthracene | 53-70-3 | Dibenz(a,h)anthracene |
| Dibenzofuran | 132-64-9 | Dibenzofuran |
| Dibromochloromethane; Chlorodibromomethane | 124-48-1 | Methane, dibromochloro- |
| 1,2-Dibromo-3-chloropropane; DBCP | 96-12-8 | Propane, 1,2-dibromo-3-chloro- |
| 1,2-Dibromoethane; Ethylene dibromide | 106-93-4 | Ethane, 1,2-dibromo- |
| Di-n-butyl phthalate | 84-74-2 | 1,2-Benzenedicarboxylic acid, dibutyl ester |
| o-Dichlorobenzene | 95-50-1 | Benzene, 1,2-dichloro- |
| m-Dichlorobenzene | 541-73-1 | Benzene, 1,3-dichloro- |
| p-Dichlorobenzene | 106-46-7 | Benzene, 1,4-dichloro- |
| 3,3'-Dichlorobenzidine | 91-94-1 | (1,1'-Biphenyl)-4,4'-diamine, 3,3'-dichloro- |
| trans-1,4-Dichloro-2-butene | 110-57-6 | 2-Butene, 1,4-dichloro-, (E)- |
| Dichlorodifluoromethane | 75-71-8 | Methane, dichlorodifluoro- |
| 1,1-Dichloroethane | 75-34-3 | Ethane, 1,1-dichloro- |
| 1,2-Dichloroethane; Ethylene dichloride | 107-06-2 | Ethane, 1,2-dichloro- |
| 1,1-Dichloroethylene; Vinylidene chloride | 75-35-4 | Ethene, 1,1-dichloro- |
| trans-1,2-Dichloroethylene | 156-60-5 | Ethene, 1,2-dichloro-, (E)- |
| 2,4-Dichlorophenol | 120-83-2 | Phenol, 2,4-dichloro- |
| 2,6-Dichlorophenol | 87-65-0 | Phenol, 2,6-dichloro- |
| 1,2-Dichloropropane | 78-87-5 | Propane, 1,2-dichloro- |
| cis-1,3-Dichloropropene | 10061-01-5 | 1-Propene, 1,3-dichloro-, (Z)- |
| trans-1,3-Dichloropropene | 10061-02-6 | 1-Propene, 1,3-dichloro-, (E)- |
| Dieldrin | 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 )- |
| Diethyl phthalate | 84-66-2 | 1,2-Benzenedicarboxylic acid, diethyl ester |
| O,O-Diethyl O-2-pyrazinyl phosphorothioate; Thionazin | 297-97-2 | Phosphorothioic acid, O,O-diethyl O-pyrazinyl ester |
| Dimethoate | 60-51-5 | Phosphorodithioic acid, O,O-dimethyl S-(2-(methylamino)-2-oxoethyl) ester |
| p-(Dimethylamino)azobenzene | 60-11-7 | Benzenamine, N,N-dimethyl-4-(phenylazo)- |
| 7,12-Dimethylbenz(a)anthracene | 57-97-6 | Benz(a)anthracene,7,12-dimethyl- |
| 3,3'-Dimethylbenzidine | 119-93-7 | (1,1'-Biphenyl)-4,4'-diamine, 3,3'-dimethyl- |
| a , a -Dimethylphenethylamine | 122-09-8 | Benzeneethanamine, a , a -dimethyl- |
| 2,4-Dimethylphenol | 105-67-9 | Phenol, 2,4-dimethyl- |
| Dimethyl phthalate | 131-11-3 | 1,2-Benzenedicarboxylic acid, dimethyl ester |
| m-Dinitrobenzene | 99-65-0 | Benzene, 1,3-dinitro- |
| 4,6-Dinitro-o-cresol | 534-52-1 | Phenol, 2-methyl-4,6-dinitro- |
| 2,4-Dinitrophenol | 51-28-5 | Phenol, 2,4-dinitro- |
| 2,4-Dinitrotoluene | 121-14-2 | Benzene, 1-methyl-2,4-dinitro- |
| 2,6-Dinitrotoluene | 606-20-2 | Benzene, 2-methyl-1,3-dinitro- |
| Dinoseb; DNBP; 2-sec-Butyl-4,6-dinitrophenol | 88-85-7 | Phenol, 2-(1-methylpropyl)-4,6-dinitro- |
| Di-n-octyl phthalate | 117-84-0 | 1,2-Benzenedicarboxylic acid, dioctyl ester |
| 1,4-Dioxane | 123-91-1 | 1,4-Dioxane |
| Diphenylamine | 122-39-4 | Benzeneamine, N-phenyl- |
| Disulfoton | 298-04-4 | Phosphorodithioic acid, O,O-diethyl S-(2-(ethylthio)ethyl) ester |
| Endosulfan I | 959-98-8 | 6,9-Methano-2,4,3-benzodioxathiepin,6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide, (3 a ,5a b ,6 a ,9 a ,9a b )- |
| Endosulfan II | 33213-65-9 | 6,9-Methano-2,4,3-benzodioxathiepin,6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide, (3 a ,5a a ,6 b ,9 b ,9a a )- |
| Endosulfan sulfate | 1031-07-8 | 6,9-Methano-2,4,3-benzodioxathiepin,6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-,3,3-dioxide |
| Endrin | 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 )- |
| Endrin aldehyde | 7421-93-4 | 1,2,4-Methanocyclopenta(cd)pentalene-5-carboxaldehyde, 2,2a,3,3,4,7-hexachlorodecahydro-, (1 a ,2 b ,2a b ,4 b ,4a b ,5 b ,6a b ,6b b ,7R)- |
| Ethylbenzene | 100-41-4 | Benzene, ethyl- |
| Ethyl methacrylate | 97-63-2 | 2-Propenoic acid, 2-methyl-, ethyl ester |
| Ethyl methanesulfonate | 62-50-0 | Methanesulfonic acid, ethyl ester |
| Famphur | 52-85-7 | Phosphorothioic acid, O-(4-((dimethylamino)sulfonyl)phenyl)-O,O-dimethyl ester |
| Fluoranthene | 206-44-0 | Fluoranthene |
| Fluorene | 86-73-7 | 9H-Fluorene |
| Heptachlor | 76-44-8 | 4,7-Methano-1H-indene, 1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro- |
| Heptachlor epoxide | 1024-57-3 | 2,5-Methano-2H-indeno(1,2-b)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 )- |
| Hexachlorobenzene | 118-74-1 | Benzene, hexachloro- |
| Hexachlorobutadiene | 87-68-3 | 1,3-Butadiene, 1,1,2,3,4,4-hexachloro- |
| Hexachlorocyclopentadiene | 77-47-4 | 1,3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro- |
| Hexachloroethane | 67-72-1 | Ethane, hexachloro- |
| Hexachlorophene | 70-30-4 | Phenol, 2,2'-methylenebis(3,4,6-trichloro- |
| Hexachloropropene | 1888-71-7 | 1-Propene, 1,1,2,3,3,3-hexachloro- |
| 2-Hexanone | 591-78-6 | 2-Hexanone |
| Indeno(1,2,3-cd)pyrene | 193-39-5 | Indeno(1,2,3-cd)pyrene |
| Isobutyl alcohol | 78-83-1 | 1-Propanol, 2-methyl- |
| Isodrin | 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 )- |
| Isophorone | 78-59-1 | 2-Cyclohexen-1-one, 3,5,5-trimethyl- |
| Isosafrole | 120-58-1 | 1,3-Benzodioxole, 5-(1-propenyl)- |
| Kepone | 143-50-0 | 1,3,4-Metheno-2H-cyclobuta-(c,d)pentalen-2-one, 1,1a,3,3a,4,5,5,5a,5b,6-decachlorooctahydro- |
| Lead | (Total) | Lead |
| Mercury | (Total) | Mercury |
| Methacrylonitrile | 126-96-7 | 2-Propenenitrile, 2-methyl- |
| Methapyrilene | 91-80-5 | 1,2-Ethanediamine, N,N-dimethyl-N'-2-pyridinyl-N'-(2-thienylmethyl)- |
| Methoxychlor | 72-43-5 | Benzene, 1,1'-(2,2,2-trichloroethylidene)bis(4-methoxy- |
| Methyl bromide; Bromomethane | 74-83-9 | Methane, bromo- |
| Methyl chloride; Chloromethane | 74-87-3 | Methane, chloro- |
| 3-Methylcholanthrene | 56-49-5 | Benz(j)aceanthrylene, 1,2-dihydro-3-methyl- |
| Methylene bromide; Dibromomethane | 74-95-3 | Methane, dibromo- |
| Methylene chloride; Dichloromethane | 75-09-2 | Methane, dichloro- |
| Methyl ethyl ketone; MEK | 78-93-3 | 2-Butanone |
| Methyl iodide; Iodomethane | 74-88-4 | Methane, iodo- |
| Methyl methacrylate | 80-62-6 | 2-Propenoic acid, 2-methyl-, methyl ester |
| Methyl methanesulfonate | 66-27-3 | Methanesulfonic acid, methyl ester |
| 2-Methylnaphthalene | 91-57-6 | Naphthylene, 2-methyl- |
| Methyl parathion; Parathion methyl | 298-00-0 | Phosphorothioic acid, O,O-dimethyl O-(4-nitrophenyl) ester |
| 4-Methyl-2-pentanone; Methyl isobutyl ketone | 108-10-1 | 2-Pentanone, 4-methyl- |
| Naphthalene | 91-20-3 | Naphthalene |
| 1,4-Naphthoquinone | 130-15-4 | 1,4-Naphthalenedione |
| 1-Naphthylamine | 134-32-7 | 1-Naphthalenamine |
| 2-Naphthylamine | 91-59-8 | 2-Naphthalenamine |
| Nickel | (Total) | Nickel |
| o-Nitroaniline | 88-74-4 | Benzenamine, 2-nitro- |
| m-Nitroaniline | 99-09-2 | Benzenamine, 3-nitro- |
| p-Nitroaniline | 100-01-6 | Benzenamine, 4-nitro- |
| Nitrobenzene | 98-95-3 | Benzene, nitro- |
| o-Nitrophenol | 88-75-5 | Phenol, 2-nitro- |
| p-Nitrophenol | 100-02-7 | Phenol, 4-nitro- |
| 4-Nitroquinoline 1-oxide | 56-57-5 | Quinoline, 4-nitro-, 1-oxide |
| N-Nitrosodi-n-butylamine | 924-16-3 | 1-Butanamine, N-butyl-N-nitroso- |
| N-Nitrosodiethylamine | 55-18-5 | Ethanamine, N-ethyl-N-nitroso- |
| N-Nitrosodimethylamine | 62-75-9 | Methanamine, N-methyl-N-nitroso- |
| N-Nitrosodiphenylamine | 86-30-6 | Benzenamine, N-nitroso-N-phenyl- |
| N-Nitrosodipropylamine; Di-n-propylnitrosamine | 621-64-7 | 1-Propanamine, N-nitroso-N-propyl- |
| N-Nitrosomethylethylamine | 10595-95-6 | Ethanamine, N-methyl-N-nitroso- |
| N-Nitrosomorpholine | 59-89-2 | Morpholine, 4-nitroso- |
| N-Nitrosopiperidene | 100-75-4 | Piperidene, 1-nitroso- |
| N-Nitrosopyrrolidine | 930-55-2 | Pyrrolidine, 1-nitroso- |
| 5-Nitro-o-toluidine | 99-55-8 | Benzenamine, 2-methyl-5-nitro- |
| Parathion | 56-38-2 | Phosphorothioic acid, O,O-diethyl-O-(4-nitrophenyl) ester |
| Polychlorinated biphenyls; PCBs | See (g) | 1,1'-Biphenyl, chloro derivatives |
| Polychlorinated dibenzo-p-dioxins; PCDDs | See (h) | Dibenzo(b,e)(1,4)dioxin, chloro derivatives |
| Polychlorinated dibenzofurans; PCDFs | See (i) | Bibenzofuran, chloro derivatives |
| Pentachlorobenzene | 608-93-5 | Benzene, pentachloro- |
| Pentachloroethane | 76-01-7 | Ethane, pentachloro- |
| Pentachloronitrobenzene | 82-68-8 | Benzene, pentachloronitro- |
| Pentachlorophenol | 87-86-5 | Phenol, pentachloro- |
| Phenacetin | 62-44-2 | Acetamide, N-(4-ethoxyphenyl) |
| Phenanthrene | 85-01-8 | Phenanthrene |
| Phenol | 108-95-2 | Phenol |
| p-Phenylenediamine | 106-50-3 | 1,4-Benzenediamine |
| Phorate | 298-02-2 | Phosphorodithioic acid, O,O-diethyl S-((ethylthio)methyl) ester |
| 2-Picoline | 109-06-8 | Pyridine, 2-methyl- |
| Pronamide | 23950-58-5 | Benzamide, 3,5-dichloro-N-(1,1-dimethyl-2-propenyl)- |
| Propionitrile; Ethyl cyanide | 107-12-0 | Propanenitrile |
| Pyrene | 129-00-0 | Pyrene |
| Pyridine | 110-86-1 | Pyridine |
| Safrole | 94-59-7 | 1,3-Benzodioxole, 5-(2-propenyl)- |
| Selenium | (Total) | Selenium |
| Silver | (Total) | Silver |
| Silvex; 2,4,5-TP | 93-72-1 | Propanoic acid, 2-(2,4,5-trichlorophenoxy)- |
| Styrene | 100-42-5 | Benzene, ethenyl- |
| Sulfide | 18496-25-8 | Sulfide |
| 2,4,5-T; 2,4,5-Trichlorophenoxyacetic acid | 93-76-5 | Acetic acid, (2,4,5-trichlorophenoxy)- |
| 2,3,7,8-TCDD; 2,3,7,8-Tetrachlorodibenzo-p-dioxin | 1746-01-8 | Dibenzo(b,e)(1,4)dioxin, 2,3,7,8-tetrachloro- |
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | Benzene, 1,2,4,5-tetrachloro- |
| 1,1,1,2-Tetrachloroethane | 630-20-6 | Ethane, 1,1,1,2-tetrachloro- |
| 1,1,2,2,-Tetrachloroethane | 79-34-5 | Ethane, 1,1,2,2-tetrachloro- |
| Tetrachloroethylene; Perchloroethylene; Tetrachloroethene | 127-18-4 | Ethene, tetrachloro- |
| 2,3,4,6-Tetrachlorophenol | 58-90-2 | Phenol, 2,3,4,6-tetrachloro- |
| Tetraethyl dithiopyrophosphate; Sulfotepp | 3689-24-5 | Thiodiphosphoric acid (((HO)2P(S))2O), tetraethyl ester |
| Thallium | (Total) | Thallium |
| Tin | (Total) | Tin |
| Toluene | 108-88-3 | Benzene, methyl- |
| o-Toluidine | 95-53-4 | Benzenamine, 2-methyl- |
| Toxaphene | 8001-35-2 | Toxaphene |
| 1,2,4-Trichlorobenzene | 120-82-1 | Benzene, 1,2,4-trichloro- |
| 1,1,1-Trichloroethane; Methyl chloroform | 71-55-6 | Ethane, 1,1,1-trichloro- |
| 1,1,2-Trichloroethane | 79-00-5 | Ethane, 1,1,2-trichloro- |
| Trichloroethylene; Trichloroethene | 79-01-6 | Ethene, trichloro- |
| Trichlorofluoromethane | 75-69-4 | Methane, trichlorofluoro- |
| 2,4,5-Trichlorophenol | 95-96-4 | Phenol, 2,4,5-trichloro- |
| 2,4,6-Trichlorophenol | 88-06-2 | Phenol, 2,4,6-trichloro- |
| 1,2,3-Trichloropropane | 96-18-4 | Propane, 1,2,3-trichloro- |
| O,O,O-Triethyl phosphorothioate | 126-68-1 | Phosphorothioic acid, O,O,O-triethyl ester |
| sym-Trinitrobenzene | 99-35-4 | Benzene, 1,3,5-trinitro- |
| Vanadium | (Total) | Vanadium |
| Vinyl acetate | 108-05-4 | Acetic acid, ethenyl ester |
| Vinyl chloride | 75-01-4 | Ethene, chloro- |
| Xylene (total) | 1330-20-7 | Benzene, dimethyl- |
| Zinc | (Total) | Zinc |
| 725.101 | Purpose, Scope, and Applicability |
| 725.102 | Electronic Reporting |
| 725.104 | Imminent Hazard Action |
| 725.110 | Applicability |
| 725.111 | USEPA Identification Number |
| 725.112 | Required Notices |
| 725.113 | General Waste Analysis |
| 725.114 | Security |
| 725.115 | General Inspection Requirements |
| 725.116 | Personnel Training |
| 725.117 | General Requirements for Ignitable, Reactive, or Incompatible Wastes |
| 725.118 | Location Standards |
| 725.119 | Construction Quality Assurance Program |
| 725.130 | Applicability |
| 725.131 | Maintenance and Operation of Facility |
| 725.132 | Required Equipment |
| 725.133 | Testing and Maintenance of Equipment |
| 725.134 | Access to Communications or Alarm System |
| 725.135 | Required Aisle Space |
| 725.137 | Arrangements with Local Authorities |
| 725.150 | Applicability |
| 725.151 | Purpose and Implementation of Contingency Plan |
| 725.152 | Content of Contingency Plan |
| 725.153 | Copies of Contingency Plan |
| 725.154 | Amendment of Contingency Plan |
| 725.155 | Emergency Coordinator |
| 725.156 | Emergency Procedures |
| 725.170 | Applicability |
| 725.171 | Use of Manifest System |
| 725.172 | Manifest Discrepancies |
| 725.173 | Operating Record |
| 725.174 | Availability, Retention, and Disposition of Records |
| 725.175 | Annual Report |
| 725.176 | Unmanifested Waste Report |
| 725.177 | Additional Reports |
| 725.190 | Applicability |
| 725.191 | Groundwater Monitoring System |
| 725.192 | Sampling and Analysis |
| 725.193 | Preparation, Evaluation, and Response |
| 725.194 | Recordkeeping and Reporting |
| 725.210 | Applicability |
| 725.211 | Closure Performance Standard |
| 725.212 | Closure Plan; Amendment of Plan |
| 725.213 | Closure; Time Allowed for Closure |
| 725.214 | Disposal or Decontamination of Equipment, Structures, and Soils |
| 725.215 | Certification of Closure |
| 725.216 | Survey Plat |
| 725.217 | Post-Closure Care and Use of Property |
| 725.218 | Post-Closure Care Plan; Amendment of Plan |
| 725.219 | Post-Closure Notices |
| 725.220 | Certification of Completion of Post-Closure Care |
| 725.221 | Alternative Post-Closure Care Requirements |
| 725.240 | Applicability |
| 725.241 | Definitions of Terms as Used in this Subpart H |
| 725.242 | Cost Estimate for Closure |
| 725.243 | Financial Assurance for Closure |
| 725.244 | Cost Estimate for Post-Closure Care |
| 725.245 | Financial Assurance for Post-Closure Monitoring and Maintenance |
| 725.246 | Use of a Mechanism for Financial Assurance of Both Closure and Post-Closure Care |
| 725.247 | Liability Requirements |
| 725.248 | Incapacity of Owners or Operators, Guarantors, or Financial Institutions |
| 725.251 | Promulgation of Forms (Repealed) |
| 725.270 | Applicability |
| 725.271 | Condition of Containers |
| 725.272 | Compatibility of Waste with Containers |
| 725.273 | Management of Containers |
| 725.274 | Inspections |
| 725.276 | Special Requirements for Ignitable or Reactive Wastes |
| 725.277 | Special Requirements for Incompatible Wastes |
| 725.278 | Air Emission Standards |
| 725.290 | Applicability |
| 725.291 | Assessment of Existing Tank System Integrity |
| 725.292 | Design and Installation of New Tank Systems or Components |
| 725.293 | Containment and Detection of Releases |
| 725.294 | General Operating Requirements |
| 725.295 | Inspections |
| 725.296 | Response to Leaks or Spills and Disposition of Tank Systems |
| 725.297 | Closure and Post-Closure Care |
| 725.298 | Special Requirements for Ignitable or Reactive Wastes |
| 725.299 | Special Requirements for Incompatible Wastes |
| 725.300 | Waste Analysis and Trial Tests |
| 725.301 | Generators of 100 to 1,000 Kilograms of Hazardous Waste Per Month |
| 725.302 | Air Emission Standards |
| 725.320 | Applicability |
| 725.321 | Design and Operating Requirements |
| 725.322 | Action Leakage Rate |
| 725.323 | Containment System |
| 725.324 | Response Actions |
| 725.325 | Waste Analysis and Trial Tests |
| 725.326 | Monitoring and Inspections |
| 725.328 | Closure and Post-Closure Care |
| 725.329 | Special Requirements for Ignitable or Reactive Wastes |
| 725.330 | Special Requirements for Incompatible Wastes |
| 725.331 | Air Emission Standards |
| 725.350 | Applicability |
| 725.351 | Protection from Wind |
| 725.352 | Waste Analysis |
| 725.353 | Containment |
| 725.354 | Design and Operating Requirements |
| 725.355 | Action Leakage Rates |
| 725.356 | Special Requirements for Ignitable or Reactive Wastes |
| 725.357 | Special Requirements for Incompatible Wastes |
| 725.358 | Closure and Post-Closure Care |
| 725.359 | Response Actions |
| 725.360 | Monitoring and Inspections |
| 725.370 | Applicability |
| 725.372 | General Operating Requirements |
| 725.373 | Waste Analysis |
| 725.376 | Food Chain Crops |
| 725.378 | Unsaturated Zone (Zone of Aeration) Monitoring |
| 725.379 | Recordkeeping |
| 725.380 | Closure and Post-Closure Care |
| 725.381 | Special Requirements for Ignitable or Reactive Wastes |
| 725.382 | Special Requirements for Incompatible Wastes |
| 725.400 | Applicability |
| 725.401 | Design Requirements |
| 725.402 | Action Leakage Rate |
| 725.403 | Response Actions |
| 725.404 | Monitoring and Inspections |
| 725.409 | Surveying and Recordkeeping |
| 725.410 | Closure and Post-Closure Care |
| 725.412 | Special Requirements for Ignitable or Reactive Wastes |
| 725.413 | Special Requirements for Incompatible Wastes |
| 725.414 | Special Requirements for Liquid Wastes |
| 725.415 | Special Requirements for Containers |
| 725.416 | Disposal of Small Containers of Hazardous Waste in Overpacked Drums (Lab Packs) |
| 725.440 | Applicability |
| 725.441 | Waste Analysis |
| 725.445 | General Operating Requirements |
| 725.447 | Monitoring and Inspections |
| 725.451 | Closure |
| 725.452 | Interim Status Incinerators Burning Particular Hazardous Wastes |
| 725.470 | Other Thermal Treatment |
| 725.473 | General Operating Requirements |
| 725.475 | Waste Analysis |
| 725.477 | Monitoring and Inspections |
| 725.481 | Closure |
| 725.482 | Open Burning; Waste Explosives |
| 725.483 | Interim Status Thermal Treatment Devices Burning Particular Hazardous Wastes |
| 725.500 | Applicability |
| 725.501 | General Operating Requirements |
| 725.502 | Waste Analysis and Trial Tests |
| 725.503 | Inspections |
| 725.504 | Closure |
| 725.505 | Special Requirements for Ignitable or Reactive Wastes |
| 725.506 | Special Requirements for Incompatible Wastes |
| 725.530 | Applicability |
| 725.540 | Applicability |
| 725.541 | Assessment of Existing Drip Pad Integrity |
| 725.542 | Design and Installation of New Drip Pads |
| 725.543 | Design and Operating Requirements |
| 725.544 | Inspections |
| 725.545 | Closure |
| 725.930 | Applicability |
| 725.931 | Definitions |
| 725.932 | Standards: Process Vents |
| 725.933 | Standards: Closed-Vent Systems and Control Devices |
| 725.934 | Test Methods and Procedures |
| 725.935 | Recordkeeping Requirements |
| 725.950 | Applicability |
| 725.951 | Definitions |
| 725.952 | Standards: Pumps in Light Liquid Service |
| 725.953 | Standards: Compressors |
| 725.954 | Standards: Pressure Relief Devices in Gas/Vapor Service |
| 725.955 | Standards: Sampling Connecting Systems |
| 725.956 | Standards: Open-Ended Valves or Lines |
| 725.957 | Standards: Valves in Gas/Vapor or Light Liquid Service |
| 725.958 | Standards: Pumps, Valves, Pressure Relief Devices, Flanges, and Other Connectors |
| 725.959 | Standards: Delay of Repair |
| 725.960 | Standards: Closed-Vent Systems and Control Devices |
| 725.961 | Percent Leakage Alternative for Valves |
| 725.962 | Skip Period Alternative for Valves |
| 725.963 | Test Methods and Procedures |
| 725.964 | Recordkeeping Requirements |
| 725.980 | Applicability |
| 725.981 | Definitions |
| 725.982 | Schedule for Implementation of Air Emission Standards |
| 725.983 | Standards: General |
| 725.984 | Waste Determination Procedures |
| 725.985 | Standards: Tanks |
| 725.986 | Standards: Surface Impoundments |
| 725.987 | Standards: Containers |
| 725.988 | Standards: Closed-Vent Systems and Control Devices |
| 725.989 | Inspection and Monitoring Requirements |
| 725.990 | Recordkeeping Requirements |
| 725.991 | Alternative Tank Emission Control Requirements (Repealed) |
| 725.1100 | Applicability |
| 725.1101 | Design and Operating Standards |
| 725.1102 | Closure and Post-Closure Care |
| 725.1200 | Applicability |
| 725.1201 | Design and Operating Standards |
| 725.1202 | Closure and Post-Closure Care |
| 725.Appendix A | Recordkeeping Instructions |
| 725.Appendix B | EPA Report Form and Instructions (Repealed) |
| 725.Appendix C | USEPA Interim Primary Drinking Water Standards |
| 725.Appendix D | Tests for Significance |
| 725.Appendix E | Examples of Potentially Incompatible Wastes |
| 725.Appendix F | Compounds with Henry’s Law Constant Less Than 0.1 Y/X (at 25°C) |
| Section 725.114 | Security |
| a) | The owner or operator must prevent the unknowing entry and minimize the possibility for the unauthorized entry of persons or livestock onto the active portion of his facility, unless the following are true: |
| 1) | Physical contact with the waste, structures, or equipment of the active portion of the facility will not injure unknowing or unauthorized persons or livestock that may enter the active portion of the facility; and |
| 2) | Disturbance of the waste or equipment by the unknowing or unauthorized entry of persons or livestock onto the active portion of a facility will not cause a violation of the requirements of this Part. |
| b) | Unless exempt under subsections (a)(1) and (a)(2) of this Section, a facility must have the following: |
| 1) | A 24-hour surveillance system (e.g., television monitoring or surveillance by guards or facility personnel) that continuously monitors and controls entry into the active portion of the facility; or |
| 2) | Controlled access, including the following minimum elements: |
| A) | An artificial or natural barrier (e.g., a fence in good repair or a fence combined with a cliff) that completely surrounds the active portion of the facility; and |
| B) | A means to control entry at all times through the gates or other entrances to the active portion of the facility (e.g., an attendant, television monitors, locked entrance, or controlled roadway access to the facility). |
| c) | Unless exempt under subsection (a)(1) or (a)(2) of this Section, a sign with the legend, “Danger |
| Section 725.154 | Amendment of Contingency Plan |
| a) | Applicable regulations are revised; |
| b) | The plan fails in an emergency; |
| c) | The facility changes |
| d) | The list of emergency coordinators changes; or |
| e) | The list of emergency equipment changes. |
| Section 725.176 | Unmanifested Waste Report |
| a) | If a facility accepts for treatment, storage, or disposal any hazardous waste from an off-site source without an accompanying manifest, or without an accompanying shipping paper, as described by 35 Ill. Adm. Code 723.120(e), and if the waste is not excluded from the manifest requirement by 35 Ill. Adm. Code 260 through 265, then the owner or operator must prepare and submit a letter to the Agency within 15 days after receiving the waste. The unmanifested waste report must contain the following information: |
| 1) | The USEPA identification number, name, and address of the facility; |
| 2) | The date the facility received the waste; |
| 3) | The USEPA identification number, name, and address of the generator and the transporter, if available; |
| 4) | A description and the quantity of each unmanifested hazardous waste the facility received; |
| 5) | The method of treatment, storage, or disposal for each hazardous waste; |
| 6) | The certification signed by the owner or operator of the facility or its authorized representative; and |
| 7) | A brief explanation of why the waste was unmanifested, if known. |
| b) | This subsection (b) corresponds with 40 CFR 265.76(b), which USEPA has marked “reserved.” This statement maintains structural consistency with the corresponding federal regulations. |
| Section 725.416 | Disposal of Small Containers of Hazardous Waste in Overpacked Drums (Lab Packs) |
| a) | Hazardous waste must be packaged in non-leaking inside containers. The inside containers must be of a design and constructed of a material that will not react dangerously with, be decomposed by, or be ignited by the waste held therein. Inside containers must be tightly and securely sealed. The inside containers must be of the size and type specified in the USDOT hazardous materials regulations (49 CFR 173 (Shippers |
| b) | The inside containers must be overpacked in an open head USDOT-specification metal shipping container (49 CFR 178 (Specifications for Packagings) and 179 (Specifications for Tank Cars), of no more than 416 liter (110 gallon) capacity and surrounded by, at a minimum, a sufficient quantity of sorbent material, determined to be nonbiodegradable in accordance with 35 Ill. Adm. Code 725.414(f) to completely sorb all of the liquid contents of the inside containers. The metal outer container must be full after packing with inside containers and sorbent material. |
| c) | The sorbent material used must not be capable of reacting dangerously with, being decomposed by, or being ignited by the contents of the inside containers, in accordance with Section 725.117(b). |
| d) | Incompatible wastes, as defined in 35 Ill. Adm. Code 720.110, must not be placed in the same outside container. |
| e) | Reactive waste, other than cyanide- or sulfide-bearing waste, as defined in 35 Ill. Adm. Code 721.123(a)(5), must be treated or rendered non-reactive prior to packaging in accordance with subsections (a) through (d) of this Section. Cyanide- or sulfide-bearing reactive waste may be packaged in accordance with subsections (a) through (d) of this Section without first being treated or rendered non-reactive. |
| f) | Such disposal is in compliance with the requirements of 35 Ill. Adm. Code 728. Persons that incinerate lab packs according to the requirements of 35 Ill. Adm. Code 728.142(c)(1) may use fiber drums in place of metal outer containers. Such fiber drums must meet the USDOT specifications in 49 CFR 173.12 (Exceptions for Shipments of Waste Materials), incorporated by reference in 35 Ill. Adm. Code 720.111(b), and be overpacked according to subsection (b) of this Section. |
| g) | Pursuant to 35 Ill. Adm. Code 729.312, the use of labpacks for disposal of liquid wastes or wastes containing free liquids allowed under this Section is restricted to labwaste and non-periodic waste, as those terms are defined in that Part. |
| Section 725.933 | Standards: Closed-Vent Systems and Control Devices |
| a) | Compliance Required. |
| 1) | Owners or operators of closed-vent systems and control devices used to comply with provisions of this Part must comply with the provisions of this Section. |
| 2) | Implementation Schedule. |
| A) | The owner or operator of an existing facility that cannot install a closed-vent system and control device to comply with the provisions of this Subpart AA on the effective date that the facility becomes subject to the provisions of this Subpart AA must prepare an implementation schedule that includes dates by which the closed-vent system and control device will be installed and in operation. The controls must be installed as soon as possible, but the implementation schedule may allow up to 30 months after the effective date that the facility becomes subject to this Subpart AA for installation and startup. |
| B) | Any unit that begins operation after Dec. 21, 1990, and which is subject to the provisions of this Subpart AA when operation begins, must comply with the rules immediately (i.e., must have control devices installed and operating on startup of the affected unit); the 30-month implementation schedule does not apply. |
| C) | The owner or operator of any facility in existence on the effective date of a statutory or regulatory amendment that renders the facility subject to this Subpart AA must comply with all requirements of this Subpart AA as soon as practicable but no later than 30 months after the effective date of the amendment. When control equipment required by this Subpart AA cannot be installed and begin operation by the effective date of the amendment, the facility owner or operator must prepare an implementation schedule that includes the following information: specific calendar dates for award of contracts or issuance of purchase orders for the control equipment, initiation of on-site installation of the control equipment, completion of the control equipment installation, and performance of any testing to demonstrate that the installed equipment meets the applicable standards of this Subpart AA. The owner or operator must enter the implementation schedule in the operating record or in a permanent, readily available file located at the facility. |
| D) | An owner or operator of a facility or unit that becomes newly subject to the requirements of this Subpart AA after Dec. 8, 1997, due to an action other than those described in subsection (a)(2)(iii) of this Section must comply with all applicable requirements immediately (i.e., the facility or unit must have control devices installed and operating on the date the facility or unit becomes subject to this Subpart AA; the 30-month implementation schedule does not apply). |
| b) | A control device involving vapor recovery (e.g., a condenser or adsorber) must be designed and operated to recover the organic vapors vented to it with an efficiency of 95 weight percent or greater unless the total organic emission limits of Section 725.932(a)(1) for all affected process vents is attained at an efficiency less than 95 weight percent. |
| c) | An enclosed combustion device (e.g., a vapor incinerator, boiler, or process heater) must be designed and operated to reduce the organic emissions vented to it by 95 weight percent or greater; to achieve a total organic compound concentration of 20 ppmv, expressed as the sum of the actual compounds, not carbon equivalents, on a dry basis corrected to three percent oxygen; or to provide a minimum residence time of 0.50 seconds at a minimum temperature of 760 degrees Celsius (° C). If a boiler or process heater is used as the control device, then the vent stream must be introduced into the flame combustion zone of the boiler or process heater. |
| d) | Flares. |
| 1) | A flare must be designed for and operated with no visible emissions as determined by the methods specified in subsection (e)(1) of this Section except for periods not to exceed a total of five minutes during any two consecutive hours. |
| 2) | A flare must be operated with a flame present at all times, as determined by the methods specified in subsection (f)(2)(c) of this Section. |
| 3) | A flare must be used only if the net heating value of the gas being combusted is 11.2 MJ/scm (300 Btu/scf) or greater if the flare is steam-assisted or air-assisted, or if the net heating value of the gas being combusted is 7.45 MJ/scm (200 Btu/scf) or greater if the flare is nonassisted. The net heating value of the gas being combusted must be determined by the methods specified in subsection (e)(2) of this Section. |
| 4) | Exit Velocity. |
| A) | A steam-assisted or nonassisted flare must be designed for and operated with an exit velocity, as determined by the methods specified in subsection (e)(3) of this Section, less than 18.3 m/s (60 ft/s), except as provided in subsections (d)(4)(B) and (d)(4)(C) of this Section. |
| B) | A steam-assisted or nonassisted flare designed for and operated with an exit velocity, as determined by the methods specified in subsection (e)(3) of this Section, equal to or greater than 18.3 m/s (60 ft/s) but less than 122 m/s (400 ft/s) is allowed if the net heating value of the gas being combusted is greater than 37.3 MJ/scm (1,000 Btu/scf). |
| C) | A steam-assisted or nonassisted flare designed for and operated with an exit velocity, as determined by the methods specified in subsection (e)(3) of this Section, less than the velocity, V as determined by the method specified in subsection (e)(4) and less than 122 m/s (400 ft/s) is allowed. |
| 5) | An air-assisted flare must be designed and operated with an exit velocity less than the velocity, V, as determined by the method specified in subsection (e)(5) of this Section. |
| 6) | A flare used to comply with this Section must be steam-assisted, air-assisted, or nonassisted. |
| e) | Compliance determination and equations. |
| 1) | Reference Method 22 (Visual Determination of Fugitive Emissions from Material Sources and Smoke Emissions from Flares) in appendix A to 40 CFR 60 (Test Methods), incorporated by reference in 35 Ill. Adm. Code 720.111(b), must be used to determine the compliance of a flare with the visible emission provisions of this Subpart AA. The observation period is two hours and must be used according to Method 22. |
| 2) | The net heating value of the gas being combusted in a flare must be calculated using the following equation: |
| HT = | the net heating value of the sample in MJ/scm; where the net enthalpy per mole of offgas is based on combustion at 25° C and 760 mm Hg, but the standard temperature for determining the volume corresponding to 1 mole is 20° C |
| K = | 1.74´10-7 (1/ppm)(g mol/scm)(MJ/kcal) where the standard temperature for (g mol/scm) is 20° C |
| S Xi = | the sum of the values of X for each component i, from i=1 to n |
| Ci = | the concentration of sample component i in ppm on a wet basis, as measured for organics by Reference Method 18 (Measurement of Gaseous Organic Compound Emissions by Gas Chromatography) in appendix A to 40 CFR 60 (Test Methods), and for carbon monoxide, by ASTM D 1946-90 (Standard Practice for Analysis of Reformed Gas by Gas Chromatography), each incorporated by reference in 35 Ill. Adm. Code 720.111 |
| 3) | The actual exit velocity of a flare must be determined by dividing the volumetric flow rate (in units of standard temperature and pressure), as determined by Reference Methods 2 (Determination of Stack Gas Velocity and Volumetric Flow Rate (Type S Pitot Tube)), 2A (Direct Measurement of Gas Volume through Pipes and Small Ducts), 2C (Determination of Gas Velocity and Volumetric Flow Rate in Small Stacks or Ducts (Standard Pitot Tube)), or 2D (Measurement of Gas Volume Flow Rates in Small Pipes and Ducts) in appendix A to 40 CFR 60 (Test Methods), incorporated by reference in 35 Ill. Adm. Code 720.111(b), as appropriate, by the unobstructed (free) cross-sectional area of the flare tip. |
| 4) | The maximum allowed velocity in m/s, V for a flare complying with subsection (d)(4)(C) of this Section must be determined by the following equation: |
| log10 = | logarithm to the base 10 |
| HT = | the net heating value as determined in subsection (e)(2) of this Section. |
| 5) | The maximum allowed velocity in m/s, V, for an air-assisted flare must be determined by the following equation: |
| HT = | the net heating value as determined in subsection (e)(2) of this Section. |
| f) | The owner or operator must monitor and inspect each control device required to comply with this Section to ensure proper operation and maintenance of the control device by implementing the following requirements: |
| 1) | Install, calibrate, maintain, and operate according to the manufacturer’s specifications a flow indicator that provides a record of vent stream flow from each affected process vent to the control device at least once every hour. The flow indicator sensor must be installed in the vent stream at the nearest feasible point to the control device inlet but before being combined with other vent streams. |
| 2) | Install, calibrate, maintain, and operate according to the manufacturer’s specifications a device to continuously monitor control device operation, as specified below: |
| A) | For a thermal vapor incinerator, a temperature monitoring device equipped with a continuous recorder. The device must have accuracy of ±1 percent of the temperature being monitored in ° C or |
| B) | For a catalytic vapor incinerator, a temperature monitoring device equipped with a continuous recorder. The device must be capable of monitoring temperature at two locations and have an accuracy of ±1 percent of the temperature being monitored in ° C or |
| C) | For a flare, a heat sensing monitoring device equipped with a continuous recorder that indicates the continuous ignition of the pilot flame. |
| D) | For a boiler or process heater having a design heat input capacity less than 44 MW, a temperature monitoring device equipped with a continuous recorder. The device must have an accuracy of ±1 percent of the temperature being monitored in ° C or |
| E) | For a boiler or process heater having a design heat input capacity greater than or equal to 44 MW, a monitoring device equipped with a continuous recorder to measure parameters that indicate good combustion operating practices are being used. |
| F) | For a condenser, either of the following: |
| i) | A monitoring device equipped with a continuous recorder to measure the concentration level of the organic compounds in the exhaust vent stream from the condenser; or |
| ii) | A temperature monitoring device equipped with a continuous recorder. The device must be capable of monitoring temperature with an accuracy of ±1 percent of the temperature being monitored in degrees Celsius (° C) or ±0.5° C, whichever is greater. The temperature sensor must be installed at a location in the exhaust vent stream from the condenser exit (i.e., product side). |
| G) | For a carbon adsorption system, such as a fixed-bed carbon adsorber that regenerates the carbon bed directly in the control device, either of the following: |
| i) | A monitoring device equipped with a continuous recorder to measure the concentration level of the organic compounds in the exhaust vent stream from the carbon bed; or |
| ii) | A monitoring device equipped with a continuous recorder to measure a parameter that indicates the carbon bed is regenerated on a regular, predetermined time cycle. |
| 3) | Inspect the readings from each monitoring device required by subsections (f)(1) and (f)(2) of this Section at least once each operating day to check control device operation and, if necessary, immediately implement the corrective measures necessary to ensure the control device operates in compliance with the requirements of this Section. |
| g) | An owner or operator using a carbon adsorption system such as a fixed-bed carbon adsorber that regenerates the carbon bed directly onsite in the control device must replace the existing carbon in the control device with fresh carbon at a regular, predetermined time interval that is no longer than the carbon service life established as a requirement of Section 725.935(b)(4)(C)(vi). |
| h) | An owner or operator using a carbon adsorption system, such as a carbon canister, that does not regenerate the carbon bed directly onsite in the control device must replace the existing carbon in the control device with fresh carbon on a regular basis by using one of the following procedures: |
| 1) | Monitor the concentration level of the organic compounds in the exhaust vent stream from the carbon adsorption system on a regular schedule, and replace the existing carbon with fresh carbon immediately when carbon breakthrough is indicated. The monitoring frequency must be daily or at an interval no greater than 20 percent of the time required to consume the total carbon working capacity established as a requirement of Section 725.935(b)(4)(C)(vii), whichever is longer. |
| 2) | Replace the existing carbon with fresh carbon at a regular, predetermined time interval that is less than the design carbon replacement interval established as a requirement of Section 725.935(b)(4)(C)(vii). |
| i) | An owner or operator of an affected facility seeking to comply with the provisions of this Part by using a control device other than a thermal vapor incinerator, catalytic vapor incinerator, flare, boiler, process heater, condenser, or carbon adsorption system is required to develop documentation including sufficient information to describe the control device operation and identify the process parameter or parameters that indicate proper operation and maintenance of the control device. |
| j) | A closed-vent system must meet either of the following design requirements: |
| 1) | A closed-vent system must be designed to operate with no detectable emissions, as indicated by an instrument reading of less than 500 ppmv above background, as determined by the methods specified at Section 725.934(b), and by visual inspections; or |
| 2) | A closed-vent system must be designed to operate at a pressure below atmospheric pressure. The system must be equipped with at least one pressure gauge or other pressure measurement device that can be read from a readily accessible location to verify that negative pressure is being maintained in the closed-vent system when the control device is operating. |
| k) | The owner or operator must monitor and inspect each closed-vent system required to comply with this Section to ensure proper operation and maintenance of the closed-vent system by implementing the following requirements: |
| 1) | Each closed-vent system that is used to comply with subsection (j)(1) of this Section must be inspected and monitored in accordance with the following requirements: |
| A) | An initial leak detection monitoring of the closed-vent system must be conducted by the owner or operator on or before the date that the system becomes subject to this Section. The owner or operator must monitor the closed-vent system components and connections using the procedures specified in Section 725.934(b) to demonstrate that the closed-vent system operates with no detectable emissions, as indicated by an instrument reading of less than 500 ppmv above background. |
| B) | After initial leak detection monitoring required in subsection (k)(1)(A) of this Section, the owner or operator must inspect and monitor the closed-vent system as follows: |
| i) | Closed-vent system joints, seams, or other connections that are permanently or semi-permanently sealed (e.g., a welded joint between two sections of hard piping or a bolted and gasketed ducting flange) must be visually inspected at least once per year to check for defects that could result in air pollutant emissions. The owner or operator must monitor a component or connection using the procedures specified in Section 725.934(b) to demonstrate that it operates with no detectable emissions following any time the component is repaired or replaced (e.g., a section of damaged hard piping is replaced with new hard piping) or the connection is unsealed (e.g., a flange is unbolted). |
| ii) | Closed-vent system components or connections other than those specified in subsection (k)(1)(B)(i) of this Section must be monitored annually and at other times as requested by the Agency, except as provided for in subsection (n) of this Section, using the procedures specified in Section 725.934(b) to demonstrate that the components or connections operate with no detectable emissions. |
| C) | In the event that a defect or leak is detected, the owner or operator must repair the defect or leak in accordance with the requirements of subsection (k)(3) of this Section. |
| D) | The owner or operator must maintain a record of the inspection and monitoring in accordance with the requirements specified in Section 725.935. |
| 2) | Each closed-vent system that is used to comply with subsection (j)(2) of this Section must be inspected and monitored in accordance with the following requirements: |
| A) | The closed-vent system must be visually inspected by the owner or operator to check for defects that could result in air pollutant emissions. Defects include, but are not limited to, visible cracks, holes, or gaps in ductwork or piping or loose connections. |
| B) | The owner or operator must perform an initial inspection of the closed-vent system on or before the date that the system becomes subject to this Section. Thereafter, the owner or operator must perform the inspections at least once every year. |
| C) | In the event that a defect or leak is detected, the owner or operator must repair the defect in accordance with the requirements of subsection (k)(3) of this Section. |
| D) | The owner or operator must maintain a record of the inspection and monitoring in accordance with the requirements specified in Section 725.935. |
| 3) | The owner or operator must repair all detected defects as follows: |
| A) | Detectable emissions, as indicated by visual inspection or by an instrument reading greater than 500 ppmv above background, must be controlled as soon as practicable, but not later than 15 calendar days after the emission is detected, except as provided for in subsection (k)(3)(C) of this Section. |
| B) | A first attempt at repair must be made no later than five calendar days after the emission is detected. |
| C) | Delay of repair of a closed-vent system for which leaks have been detected is allowed if the repair is technically infeasible without a process unit shutdown, or if the owner or operator determines that emissions resulting from immediate repair would be greater than the fugitive emissions likely to result from delay of repair. Repair of such equipment must be completed by the end of the next process unit shutdown. |
| D) | The owner or operator must maintain a record of the defect repair in accordance with the requirements specified in Section 725.935. |
| l) | A closed-vent system or control device used to comply with provisions of this Subpart AA must be operated at all times when emissions may be vented to it. |
| m) | The owner or operator using a carbon adsorption system to control air pollutant emissions must document that all carbon removed that is a hazardous waste and that is removed from the control device is managed in one of the following manners, regardless of the volatile organic concentration of the carbon: |
| 1) | It is regenerated or reactivated in a thermal treatment unit that meets one of the following: |
| A) | The owner or operator of the unit has been issued a final permit under 35 Ill. Adm. Code 702, 703, and 705 that implements the requirements of Subpart X of 35 Ill. Adm. Code 724; or |
| B) | The unit is equipped with and operating air emission controls in accordance with the applicable requirements of Subparts AA and CC of this Part or 35 Ill. Adm. Code 724; or |
| C) | The unit is equipped with and operating air emission controls in accordance with a federal national emission standard for hazardous air pollutants under 40 CFR 61 (National Emission Standards for Hazardous Air Pollutants) or 63 (National Emission Standards for Hazardous Air Pollutants for Source Categories), each incorporated by reference in 35 Ill. Adm. Code 720.111(b). |
| 2) | It is incinerated in a hazardous waste incinerator for which the owner or operator has done either of the following: |
| A) | The owner or operator has been issued a final permit under 35 Ill. Adm. Code 702, 703, and 705 that implements the requirements of Subpart O of 35 Ill. Adm. Code 724; or |
| B) | The owner or operator has designed and operates the incinerator in accordance with the interim status requirements of Subpart O of this Part. |
| 3) | It is burned in a boiler or industrial furnace for which the owner or operator has done either of the following: |
| A) | The owner or operator has been issued a final permit under 35 Ill. Adm. Code 702, 703, and 705 that implements the requirements of Subpart H of 35 Ill. Adm. Code 726; or |
| B) | The owner or operator has designed and operates the boiler or industrial furnace in accordance with the interim status requirements of Subpart H of 35 Ill. Adm. Code 726. |
| n) | Any components of a closed-vent system that are designated, as described in Section 725.935(c)(9), as unsafe to monitor are exempt from the requirements of subsection (k)(1)(B)(ii) of this Section if both of the following conditions are fulfilled: |
| 1) | The owner or operator of the closed-vent system has determined that the components of the closed-vent system are unsafe to monitor because monitoring personnel would be exposed to an immediate danger as a consequence of complying with subsection (k)(1)(B)(ii) of this Section; and |
| 2) | The owner or operator of the closed-vent system adheres to a written plan that requires monitoring the closed-vent system components using the procedure specified in subsection (k)(1)(B)(ii) of this Section as frequently as practicable during safe-to-monitor times. |
| 728.101 | Purpose, Scope, and Applicability |
| 728.102 | Definitions |
| 728.103 | Dilution Prohibited as a Substitute for Treatment |
| 728.104 | Treatment Surface Impoundment Exemption |
| 728.105 | Procedures for Case-by-Case Extensions to an Effective Date |
| 728.106 | Petitions to Allow Land Disposal of a Waste Prohibited Pursuant to Subpart C |
| 728.107 | Testing, Tracking, and Recordkeeping Requirements for Generators, Treaters, and Disposal Facilities |
| 728.108 | Landfill and Surface Impoundment Disposal Restrictions (Repealed) |
| 728.109 | Special Rules for Characteristic Wastes |
| 728.110 | First Third (Repealed) |
| 728.111 | Second Third (Repealed) |
| 728.112 | Third Third (Repealed) |
| 728.113 | Newly Listed Wastes |
| 728.114 | Surface Impoundment Exemptions |
| 728.120 | Waste-Specific Prohibitions: Dyes and Pigments Production Wastes |
| 728.130 | Waste-Specific Prohibitions: Wood Preserving Wastes |
| 728.131 | Waste-Specific Prohibitions: Dioxin-Containing Wastes |
| 728.132 | Waste-Specific Prohibitions: Soils Exhibiting the Toxicity Characteristic for Metals and Containing PCBs |
| 728.133 | Waste-Specific Prohibitions: Chlorinated Aliphatic Wastes |
| 728.134 | Waste-Specific Prohibitions: Toxicity Characteristic Metal Wastes |
| 728.135 | Waste-Specific Prohibitions: Petroleum Refining Wastes |
| 728.136 | Waste-Specific Prohibitions: Inorganic Chemical Wastes |
| 728.137 | Waste-Specific Prohibitions: Ignitable and Corrosive Characteristic Wastes Whose Treatment Standards Were Vacated |
| 728.138 | Waste-Specific Prohibitions: Newly-Identified Organic Toxicity Characteristic Wastes and Newly-Listed Coke By-Product and Chlorotoluene Production Wastes |
| 728.139 | Waste-Specific Prohibitions: Spent Aluminum Potliners and Carbamate Wastes |
| 728.140 | Applicability of Treatment Standards |
| 728.141 | Treatment Standards Expressed as Concentrations in Waste Extract |
| 728.142 | Treatment Standards Expressed as Specified Technologies |
| 728.143 | Treatment Standards Expressed as Waste Concentrations |
| 728.144 | Adjustment of Treatment Standard |
| 728.145 | Treatment Standards for Hazardous Debris |
| 728.146 | Alternative Treatment Standards Based on HTMR |
| 728.148 | Universal Treatment Standards |
| 728.150 | Prohibitions on Storage of Restricted Wastes |
| 728.Appendix A | Toxicity Characteristic Leaching Procedure (TCLP) (Repealed) |
| 728.Appendix B | Treatment Standards (As concentrations in the Treatment Residual Extract) (Repealed) |
| 728.Appendix C | List of Halogenated Organic Compounds Regulated under Section 728.132 |
| 728.Appendix D | Wastes Excluded from Lab Packs |
| 728.Appendix E | Organic Lab Packs (Repealed) |
| 728.Appendix F | Technologies to Achieve Deactivation of Characteristics |
| 728.Appendix G | Federal Effective Dates |
| 728.Appendix H | National Capacity LDR Variances for UIC Wastes |
| 728.Appendix I | EP Toxicity Test Method and Structural Integrity Test |
| 728.Appendix J | Recordkeeping, Notification, and Certification Requirements (Repealed) |
| 728.Appendix K | Metal-Bearing Wastes Prohibited from Dilution in a Combustion Unit According to Section 728.103(c) |
| 728.Table A | Constituent Concentrations in Waste Extract (CCWE) |
| 728.Table B | Constituent Concentrations in Wastes (CCW) |
| 728.Table C | Technology Codes and Description of Technology-Based Standards |
| 728.Table D | Technology-Based Standards by RCRA Waste Code |
| 728.Table E | Standards for Radioactive Mixed Waste |
| 728.Table F | Alternative Treatment Standards for Hazardous Debris |
| 728.Table G | Alternative Treatment Standards Based on HTMR |
| 728.Table H | Wastes Excluded from CCW Treatment Standards |
| 728.Table I | Generator Paperwork Requirements |
| 728.Table T | Treatment Standards for Hazardous Wastes |
| 728.Table U | Universal Treatment Standards (UTS) |
| Section 728.102 | Definitions |
