Section 721.101  Purpose and Scope

 

a)         This Part identifies those solid wastes that are subject to regulation as hazardous wastes under 35 Ill. Adm. Code 702, 703, and 722 through 728, and that are subject to the notification requirements of Section 3010 of  RCRA (42 USC 6930).  In this Part:

 

1)         Subpart A defines the terms "solid waste" and "hazardous waste", identifies those wastes that are excluded from regulation under 35 Ill. Adm. Code 702, 703, and 722 through 728, and establishes special management requirements for hazardous waste that is recycled.

 

2)         Subpart B specifies the criteria used to identify characteristics of hazardous waste and to list hazardous wastes.

 

3)         Subpart C identifies characteristics of hazardous wastes.

 

4)         Subpart D lists particular hazardous wastes.

 

b)         Limitations on Definition of Solid Waste

 

1)         The definition of solid waste contained in this Part applies only to wastes that also are hazardous for  the regulations implementing Subtitle C of RCRA.  For example, it does not apply to materials (like non-hazardous scrap, paper, textiles, or rubber) that are not otherwise hazardous wastes and that are recycled.

 

2)         This Part identifies only some of the materials that are solid wastes and hazardous wastes under Sections 1004(5), 1004(27) and 7003 of RCRA. A material that is not defined as a solid waste in this Part, or is not a hazardous waste identified or listed in this Part, is still a hazardous waste under those Sections if, in the case of Section 7003 of RCRA, the statutory elements are established.

 

c)         For Sections 721.102 and 721.106, the following definitions apply:

 

1)         A "spent material" is any material that has been used and because of contamination can no longer serve the purpose for which it was produced without processing.

 

2)         "Sludge" has the same meaning used in 35 Ill. Adm. Code 720.110.

 

3)         A "by-product" is a material that is not one of the primary products of a production process and is not solely or separately produced by the production process.  Examples are process residues like slags or distillation column bottoms.  The term does not include a co-product that is produced for the general public's use and is ordinarily used in the form it is produced by the process.

 

4)         A material is "reclaimed" if it is processed to recover a usable product, or if it is regenerated.  Examples are recovering lead values from spent batteries and regenerating spent solvents.  In addition, for Section 721.104(a)(23) and (a)(24) smelting, melting, and refining furnaces are considered to be solely engaged in metals reclamation if the metal recovery from the hazardous secondary materials meets the same requirements as those specified for metals recovery from hazardous waste in 35 Ill. Adm. Code 726.200(d)(1) through (d)(3), and if the residuals meet the requirements specified in 35 Ill. Adm. Code 726.212.

 

5)         A material is "used or reused" if:

 

A)        It is employed as an ingredient (including use as an intermediate) in an industrial process to make a product (for example, distillation bottoms from one process used as feedstock in another process).  However, a material will not meet this condition if distinct components of the material are recovered as separate end products (as when metals are recovered from metal-containing secondary materials); or

 

B)        It is employed in a particular function or application as an effective substitute for a commercial product (for example, spent pickle liquor used as phosphorus precipitant and sludge conditioner in wastewater treatment).

 

6)         "Scrap metal" is bits and pieces of metal parts (e.g., bars, turnings, rods, sheets, or wire) or metal pieces that may be combined with bolts or soldering (e.g., radiators, scrap automobiles, or railroad box cars) that when worn or superfluous can be recycled.

 

7)         A material is "recycled" if it is used, reused, or reclaimed.

 

8)         A material is "accumulated speculatively" if it is accumulated before being recycled.  A material is not accumulated speculatively, however, if the person accumulating it can show that the material is potentially recyclable and has a feasible means of being recycled; and that, during the calendar year (commencing on January 1), the amount of material that is recycled, or transferred to a different site for recycling, equals at least 75 percent by weight or volume of the amount of that material accumulated at the beginning of the period.  Materials must be placed in a storage unit with a label indicating the first date that the material began to be accumulated.  If placing a label on the storage unit is not practicable, the accumulation period must be documented through an inventory log or other appropriate method.  In calculating the percentage of turnover, the 75 percent requirement is to be applied to each material of the same type (e.g., slags from a single smelting process) that is recycled in the same way (i.e., from which the same material is recovered or that is used in the same way).  Materials accumulating in units that would be exempt from regulation under Section 721.104(c) are not to be included in making the calculation.  Materials that are already defined as solid wastes also are not to be included in making the calculation. Materials are no longer in this category once they are removed from accumulation for recycling, however.

 

BOARD NOTE:  Various segments of this Part and 35 Ill. Adm. Code 720 use the verbal phrase "accumulated speculatively" and the noun phrase "speculative accumulation".  Some of those segments rely on this subsection (c)(8) definition of "speculatively accumulated" for defining "speculative accumulation".  The Board infers that USEPA intends that the verb phrase define the noun phrase:  material that is accumulated speculatively is the subject of speculative accumulation.

 

9)         "Excluded scrap metal" is processed scrap metal, unprocessed home scrap metal, and unprocessed prompt scrap metal.

 

10)         "Processed scrap metal" is scrap metal that has been manually or physically altered to either separate it into distinct materials to enhance economic value or to improve the handling of materials.  Processed scrap metal includes scrap metal that has been baled, shredded, sheared, chopped, crushed, flattened, cut, melted, or separated by metal type (i.e., sorted) and fines, drosses, and related materials that have been agglomerated. (Note:  shredded circuit boards being sent for recycling are not considered processed scrap metal.  They are covered under the exclusion from the definition of solid waste for shredded circuit boards being recycled (Section 721.104(a)(14))).

 

11)         "Home scrap metal" is scrap metal as generated by steel mills, foundries, and refineries, like turnings, cuttings, punchings, and borings.

 

12)         "Prompt scrap metal" is scrap metal as generated by the metal working/fabrication industries, and it includes scrap metal like turnings, cuttings, punchings, and borings.  Prompt scrap metal is also known as industrial or new scrap metal.

 

d)         The Agency has inspection authority under Section 3007 of RCRA and Section 4 of the Act.

 

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

 

BOARD NOTE:  Subsection (e) is derived from 40 CFR 3, 271.10(b), 271.11(b), and 271.12(h) (2017).

 

(Source:  Amended at 48 Ill. Reg. 16813, effective November 7, 2024)

 

Section 721.102  Definition of Solid Waste

 

a)         Solid Waste

 

1)         A solid waste is any discarded material that is not excluded pursuant to Section 721.104(a) or that is not excluded pursuant to 35 Ill. Adm. Code 720.130 and 720.131 or 35 Ill. Adm. Code 720.130 and 720.134.

 

2)         Discarded Material

 

A)        A discarded material is any material that is described as follows:

 

i)          It is abandoned, as described in subsection (b);

 

ii)         It is recycled, as described in subsection (c);

 

iii)        It is considered inherently waste-like, as described in subsection (d); or

 

iv)        It is a military munition identified as a solid waste in 35 Ill. Adm. Code 726.302.

 

B)        This subsection (a)(2)(B) corresponds with 40 CFR 261.2(a)(2)(ii), which USEPA has removed and marked "reserved".  This statement maintains structural consistency with the corresponding federal regulations.

 

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;

 

3)         It is accumulated, stored, or treated (but not recycled) before or in lieu of being abandoned by being disposed of, burned, or incinerated; or

 

4)         Sham recycled, as explained in subsection (g).

 

c)         A material is a solid waste if it is recycled − or accumulated, stored, or treated before recycling − as specified in subsections (c)(1) through (c)(4), if one of the following occurs with regard to the material:

 

1)         The material is used in a manner constituting disposal.

 

A)        A material that is noted with a "yes" in column 1 of the table in Appendix Z 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 is a solid waste when one of the following occurs:

 

i)          It is burned to recover energy;

 

ii)         It is used to produce a fuel or is otherwise contained in fuels (in which case the fuel itself remains a solid waste);

 

iii)        It is contained in fuels (in which case the fuel itself remains a solid waste).

 

B)        However, a commercial chemical product that is listed in Section 721.133 is not a solid waste if it is itself a fuel.

 

3)         Reclaimed.  A material noted with a "No" in column 3 of the table in Appendix Z is not a solid waste when reclaimed (except as provided under Section 721.104(a)(17)).  A material  noted with a "Yes" in column 3 of Appendix Z is a solid waste when reclaimed, unless it meets the requirements of Section 721.104(a)(17), (a)(23), (a)(24), or (a)(27).

 

4)         Accumulated Speculatively.  A material noted with "yes" in column 4 of the table in Appendix Z 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)         USEPA 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, 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; 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 and these constituents are not ordinarily found in raw materials or products for which the material substitutes (or are found in raw materials or products in smaller concentrations) and is not used or reused during the recycling process; and

 

B)        The material may pose a substantial hazard to human health and the environment when recycled.

 

e)         Materials That Are Not Solid Waste When Recycled

 

1)         A material is not a solid waste when it can be shown to be recycled by fulfilling one of the following conditions:

 

A)        It is used or reused as an ingredient in an industrial process to make a product, provided the material is not being reclaimed; or

 

B)        It is used or reused as effective substitutes for commercial products; or

 

C)        It is returned to the original process from which it is generated, without first being reclaimed or land disposed.  The material must be returned as a substitute for feedstock materials.  In cases where the original process to which the material is returned is a secondary process, the material must be managed in such a manner that there is no placement on the land. In cases where the material is generated and reclaimed within the primary mineral processing industry, the conditions of the exclusion found at Section 721.104(a)(17) apply rather than this provision.

 

2)         The following materials are solid wastes, even if the recycling involves use, reuse, or return to the original process (described in subsections (e)(1)(A) through (e)(1)(C)):

 

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).

 

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.

 

g)         Sham Recycling.  A hazardous secondary material found to be sham recycled is considered discarded and a solid waste.  Sham recycling is recycling that is not legitimate recycling, as defined in 35 Ill. Adm. Code 720.143.

 

(Source:  Amended at 42 Ill. Reg. 21673, effective November 19, 2018)

 

Section 721.103  Definition of Hazardous Waste

 

a)         A solid waste, as defined in Section 721.102, is a hazardous waste if the following is true of the waste:

 

1)         It is not excluded from regulation as a hazardous waste pursuant to Section 721.104(b); and

 

2)         It meets any of the following criteria:

 

A)        It exhibits any of the characteristics of hazardous waste identified in Subpart C.  However, any mixture of a waste from the extraction, beneficiation, and processing of ores and minerals excluded pursuant to Section 721.104(b)(7) and any other solid waste exhibiting a characteristic of hazardous waste pursuant to Subpart C is a hazardous waste only if it exhibits a characteristic that would not have been exhibited by the excluded waste alone if such mixture had not occurred, or if the mixture continues to exhibit any of the characteristics exhibited by the non-excluded wastes prior to mixture.  Further, for the purposes of applying the toxicity characteristic to such mixtures, the mixture is also a hazardous waste if it exceeds the maximum concentration for any contaminant listed in Section 721.124 that would not have been exceeded by the excluded waste alone if the mixture had not occurred or if it continues to exceed the maximum concentration for any contaminant exceeded by the nonexempt waste prior to mixture.

 

B)        It is listed in Subpart D and has not been excluded from the lists in Subpart D pursuant to 35 Ill. Adm. Code 720.120 and 720.122.

 

C)        This subsection (a)(2)(B) corresponds with 40 CFR 261.3(a)(2)(iii), which USEPA removed and marked as "reserved" at 66 Fed. Reg. 27266 (May 16, 2001).  This statement maintains structural consistency with the federal regulations.

 

D)        It is a mixture of solid waste and one or more hazardous wastes listed in Subpart D and has not been excluded from this subsection (a)(2) pursuant to 35 Ill. Adm. Code 720.120 and 720.122 or subsection (g) or (h); however, the following mixtures of solid wastes and hazardous wastes listed in Subpart D are not hazardous wastes (except by application of subsection (a)(2)(A) or (a)(2)(B)) if the generator demonstrates that the mixture consists of wastewater the discharge of which is subject to regulation under either 35 Ill. Adm. Code 309 or 310 (including wastewater at facilities that have eliminated the discharge of wastewater) and the following is true of the waste:

 

i)          It is one or more of the following solvents listed in Section 721.131:  benzene, carbon tetrachloride, tetrachloroethylene, trichloroethylene or the scrubber waters derived from the combustion of these spent solvents, provided that the maximum total weekly usage of these solvents (other than the amounts that can be demonstrated not to be discharged to wastewater) divided by the average weekly flow of wastewater into the headworks of the facility's wastewater treatment or pretreatment system does not exceed 1 part per million, or the total measured concentration of these solvents entering the headworks of the facility's wastewater treatment system (at a facility that is subject to regulation under the federal Clean Air Act new source performance standards or national emission standards for hazardous air pollutants of 40 CFR 60, 61, or 63 or at a facility that is subject to an enforceable limit in a federal operating permit that minimizes fugitive emissions) does not exceed 1 part per million on an average weekly basis.  Any facility that uses benzene as a solvent and claims this exemption must use an aerated biological wastewater treatment system and must use only lined surface impoundments or tanks prior to secondary clarification in the wastewater treatment system.  A facility that chooses to measure concentration levels must file a copy of its sampling and analysis plan with the Agency.  A facility must file a copy of a revised sampling and analysis plan only if the initial plan is rendered inaccurate by changes in the facility's operations.  The sampling and analysis plan must include the monitoring point location (headworks), the sampling frequency and methodology, and a list of constituents to be monitored.  A facility is eligible for the direct monitoring option once it receives confirmation that the sampling and analysis plan has been received by the Agency.  The Agency must reject the sampling and analysis plan if it determines that the sampling and analysis plan fails to include the information required by this subsection (a)(2)(D)(i) or that the plan parameters would not enable the facility to calculate the weekly average concentration of these chemicals accurately.  If the Agency rejects the sampling and analysis plan, or if the Agency determines that the facility is not following the sampling and analysis plan, the Agency must notify the facility to cease the use of the direct monitoring option until such time as the bases for rejection are corrected;

 

ii)         It is one or more of the following spent solvents listed in Section 721.131:  methylene chloride, 1,1,1-trichloroethane, chlorobenzene, o-dichlorobenzene, cresols, cresylic acid, nitrobenzene, toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, spent chlorofluorocarbon solvents, 2-ethoxyethanol, or the scrubber waters derived-from the combustion of these spent solvents, provided that the maximum total weekly usage of these solvents (other than the amounts that can be demonstrated not to be discharged to wastewater) divided by the average weekly flow of wastewater into the headworks of the facility's wastewater treatment or pretreatment system does not exceed 25 parts per million, or the total measured concentration of these solvents entering the headworks of the facility's wastewater treatment system (at a facility that is subject to regulation under the federal Clean Air Act new source performance standards or national emission standards for hazardous air pollutants of 40 CFR 60, 61, or 63 or at a facility that is subject to an enforceable limit in a federal operating permit that minimizes fugitive emissions) does not exceed 25 parts per million on an average weekly basis.  A facility that chooses to measure concentration levels must file a copy of its sampling and analysis plan with the Agency.  A facility must file a copy of a revised sampling and analysis plan only if the initial plan is rendered inaccurate by changes in the facility's operations.  The sampling and analysis plan must include the monitoring point location (headworks), the sampling frequency and methodology, and a list of constituents to be monitored.  A facility is eligible for the direct monitoring option once it receives confirmation that the sampling and analysis plan has been received by the Agency.  The Agency must reject the sampling and analysis plan if it determines that the sampling and analysis plan fails to include the information required by this subsection (a)(2)(D)(ii) or that the plan parameters would not enable the facility to calculate the weekly average concentration of these chemicals accurately.  If the Agency rejects the sampling and analysis plan, or if the Agency determines that the facility is not following the sampling and analysis plan, the Agency must notify the facility to cease the use of the direct monitoring option until such time as the bases for rejection are corrected;

 

iii)        It is one of the following wastes listed in Section 721.132, provided that the wastes are discharged to the refinery oil recovery sewer before primary oil/water/solids separation:  heat exchanger bundle cleaning sludge from the petroleum refining industry (USEPA hazardous waste number K050), crude oil storage tank sediment from petroleum refining operations (USEPA hazardous waste number K169), clarified slurry oil tank sediment or in-line filter/separation solids from petroleum refining operations (USEPA hazardous waste number K170), spent hydrotreating catalyst (USEPA hazardous waste number K171), and spent hydrorefining catalyst (USEPA hazardous waste number K172);

 

iv)        It is a discarded hazardous waste, commercial chemical product or chemical intermediate listed in Section 721.121, 721.132, or 721.133 arising from de minimis losses of these materials.  For purposes of this subsection (a)(2)(D)(iv), "de minimis" losses are inadvertent releases to a wastewater treatment system, including those from normal material handling operations (e.g., spills from the unloading or transfer of materials from bins or other containers, leaks from pipes, valves, or other devices used to transfer materials); minor leaks of process equipment, storage tanks, or containers; leaks from well-maintained pump packings and seals; sample purgings; relief device discharges; discharges from safety showers and rinsing and cleaning of personal safety equipment; and rinsate from empty containers or from containers that are rendered empty by that rinsing.  Any manufacturing facility that claims an exemption for de minimis quantities of a waste listed in Section 721.131 or 721.132, or any nonmanufacturing facility that claims an exemption for de minimis quantities of wastes listed in Subpart D, must either have eliminated the discharge of wastewaters or have included in its federal Clean Water Act (33 USC 1251 et seq.) permit application or wastewater pretreatment submission to the Agency or the wastewater pretreatment Control Authority pursuant to 35 Ill. Adm. Code 307 of the constituents for which each waste was listed (in Appendix G); and the constituents in Table T to 35 Ill. Adm. Code 728 for which each waste has a treatment standard (i.e., land disposal restriction constituents).  A facility is eligible to claim the exemption once the Agency or Control Authority has been notified of possible de minimis releases via the Clean Water Act permit application or the wastewater pretreatment submission.  A copy of the Clean Water Act permit application or the wastewater pretreatment submission must be placed in the facility's on-site files;

 

v)         It is wastewater resulting from laboratory operations containing toxic (T) wastes listed in Subpart D, provided that the annualized average flow of laboratory wastewater does not exceed one percent of total wastewater flow into the headworks of the facility's wastewater treatment or pretreatment system or provided that the wastes' combined annualized average concentration does not exceed one part per million in the headworks of the facility's wastewater treatment or pretreatment facility.  Toxic (T) wastes used in laboratories that are demonstrated not to be discharged to wastewater are not to be included in this calculation;

 

vi)        It is one or more of the following wastes listed in Section 721.132:  wastewaters from the production of carbamates and carbamoyl oximes (USEPA hazardous waste number K157), provided that the maximum weekly usage of formaldehyde, methyl chloride, methylene chloride, and triethylamine (including all amounts that cannot be demonstrated to be reacted in the process, destroyed through treatment, or recovered, i.e., what is discharged or volatilized) divided by the average weekly flow of process wastewater prior to any dilutions into the headworks of the facility's wastewater treatment system does not exceed a total of 5 parts per million by weight, or the total measured concentration of these chemicals entering the headworks of the facility's wastewater treatment system (at a facility that is subject to regulation under the federal Clean Air Act new source performance standards or national emission standards for hazardous air pollutants of 40 CFR 60, 61, or 63 or at a facility that is subject to an enforceable limit in a federal operating permit that minimizes fugitive emissions) does not exceed 5 parts per million on an average weekly basis.  A facility that chooses to measure concentration levels must file a copy of its sampling and analysis plan with the Agency.  A facility must file a copy of a revised sampling and analysis plan only if the initial plan is rendered inaccurate by changes in the facility's operations.  The sampling and analysis plan must include the monitoring point location (headworks), the sampling frequency and methodology, and a list of constituents to be monitored.  A facility is eligible for the direct monitoring option once it receives confirmation that the sampling and analysis plan has been received by the Agency.  The Agency must reject the sampling and analysis plan if it determines that the sampling and analysis plan fails to include the information required by this subsection (a)(2)(D)(vi) or that the plan parameters would not enable the facility to calculate the weekly average concentration of these chemicals accurately.  If the Agency rejects the sampling and analysis plan, or if the Agency determines that the facility is not following the sampling and analysis plan, the Agency must notify the facility to cease the use of the direct monitoring option until such time as the bases for rejection are corrected; or

 

vii)       It is wastewater derived from the treatment of one or more of the following wastes listed in Section 721.132:  organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes (USEPA hazardous waste number K156), provided that the maximum concentration of formaldehyde, methyl chloride, methylene chloride, and triethylamine prior to any dilutions into the headworks of the facility's wastewater treatment system does not exceed a total of 5 milligrams per liter, or the total measured concentration of these chemicals entering the headworks of the facility's wastewater treatment system (at a facility that is subject to regulation under the federal Clean Air Act new source performance standards or national emission standards for hazardous air pollutants of 40 CFR 60, 61, or 63 or at a facility that is subject to an enforceable limit in a federal operating permit that minimizes fugitive emissions)  does not exceed 5 milligrams per liter on an average weekly basis.  A facility that chooses to measure concentration levels must file a copy of its sampling and analysis plan with the Agency.  A facility must file a copy of a revised sampling and analysis plan only if the initial plan is rendered inaccurate by changes in the facility's operations.  The sampling and analysis plan must include the monitoring point location (headworks), the sampling frequency and methodology, and a list of constituents to be monitored.  A facility is eligible for the direct monitoring option once it receives confirmation that the sampling and analysis plan has been received by the Agency.  The Agency must reject the sampling and analysis plan if it determines that the sampling and analysis plan fails to include the information required by this subsection (a)(2)(D)(vii) or that the plan parameters would not enable the facility to calculate the weekly average concentration of these chemicals accurately.  If the Agency rejects the sampling and analysis plan, or if the Agency determines that the facility is not following the sampling and analysis plan, the Agency must notify the facility to cease the use of the direct monitoring option until such time as the bases for rejection are corrected.

 

E)        Rebuttable presumption for used oil.  Used oil containing more than 1,000 ppm total halogens is presumed to be a hazardous waste because it has been mixed with halogenated hazardous waste listed in Subpart D.  Persons may rebut this presumption by demonstrating that the used oil does not contain hazardous waste (for example, to show that the used oil does not contain significant concentrations of halogenated hazardous constituents listed in Appendix H).

 

i)          The rebuttable presumption does not apply to a metalworking oil or fluid containing chlorinated paraffins if it is processed through a tolling arrangement, as described in 35 Ill. Adm. Code 739.124(c), to reclaim metalworking oils or fluids.  The presumption does apply to a metalworking oil or fluid if such an oil or fluid is recycled in any other manner, or disposed of.

 

ii)         The rebuttable presumption does not apply to a used oil contaminated with chlorofluorocarbons (CFCs) removed from refrigeration units where the CFCs are destined for reclamation.  The rebuttable presumption does apply to a used oil contaminated with CFCs that have been mixed with used oil from a source other than a refrigeration unit.

 

b)         A solid waste that is not excluded from regulation pursuant to subsection (a)(1) becomes a hazardous waste when any of the following events occur:

 

1)         In the case of a waste listed in Subpart D, when the waste first meets the listing description set forth in Subpart D.

 

2)         In the case of a mixture of solid waste and one or more listed hazardous wastes, when a hazardous waste listed in Subpart D is first added to the solid waste.

 

3)         In the case of any other waste (including a waste mixture), when the waste exhibits any of the characteristics identified in Subpart C.

 

c)         Unless and until it meets the criteria of subsection (e), a hazardous waste will remain a hazardous waste.

 

            BOARD NOTE: This subsection (c) corresponds with 40 CFR 261.3(c)(1) (2017). The Board has codified 40 CFR 261.3(c)(2) at subsection (e).

 

d)         Any solid waste described in subsection (e) is not a hazardous waste if it meets the following criteria:

 

1)         In the case of any solid waste, it does not exhibit any of the characteristics of hazardous waste identified in Subpart C.  (However, wastes that exhibit a characteristic at the point of generation may still be subject to 35 Ill. Adm. Code 728, even if they no longer exhibit a characteristic at the point of land disposal.)

 

2)         In the case of a waste that is a listed waste pursuant to Subpart D , a waste that contains a waste listed pursuant to Subpart D, or a waste that is derived from a waste listed in Subpart D, it also has been excluded from subsection (e) pursuant to 35 Ill. Adm. Code 720.120 and 720.122.

 

e)         Specific Inclusions and Exclusions

 

1)         Except as otherwise provided in subsection (e)(2), (g), or (h), any solid waste generated from the treatment, storage, or disposal of a hazardous waste, including any sludge, spill residue, ash, emission control dust, or leachate (but not including precipitation run-off), is a hazardous waste.  (However, materials that are reclaimed from solid wastes and that are used beneficially are not solid wastes and hence are not hazardous wastes under this provision unless the reclaimed material is burned for energy recovery or used in a manner constituting disposal.)

 

2)         The following solid wastes are not hazardous even though they are generated from the treatment, storage, or disposal of a hazardous waste, unless they exhibit one or more of the characteristics of hazardous waste:

 

A)        Waste pickle liquor sludge generated by lime stabilization of spent pickle liquor from the iron and steel industry (SIC Codes 331 and 332).

 

B)        Wastes from burning any of the materials exempted from regulation by Section 721.106(a)(3)(C) and (a)(3)(D).

 

C)        Nonwastewater residues, such as slag, resulting from high temperature metal recovery (HTMR) processing of K061, K062, or F006 waste in the units identified in this subsection (e)(2) that are disposed of in non-hazardous waste units, provided that these residues meet the generic exclusion levels identified in the tables in this subsection (e)(2)(C) for all constituents and the residues exhibit no characteristics of hazardous waste.  The types of units identified are rotary kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors, rotary hearth furnace/electric furnace combinations, or the following types of industrial furnaces (as defined in 35 Ill. Adm. Code 720.110): blast furnaces; smelting, melting, and refining furnaces (including pyrometallurgical devices such as cupolas, reverberator furnaces, sintering machines, roasters, and foundry furnaces); and other furnaces designated by the Agency pursuant to that definition.

 

i)          Testing requirements must be incorporated in a facility's waste analysis plan or a generator's self-implementing waste analysis plan; at a minimum, composite samples of residues must be collected and analyzed quarterly and when the process or operation generating the waste changes.

 

ii)         Persons claiming this exclusion in an enforcement action will have the burden of proving by clear and convincing evidence that the material meets all of the exclusion requirements.  The generic exclusion levels are the following:

 

Generic exclusion levels for K061 and K062 nonwastewater HTMR residues:
Constituent	Maximum for any single composite sample (mg/ℓ)
Antimony	0.10
Arsenic	0.50
Barium	7.6
Beryllium	0.010
Cadmium	0.050
Chromium (total)	0.33
Lead	0.15
Mercury	0.009
Nickel	1.0
Selenium	0.16
Silver	0.30
Thallium	0.020
Vanadium	1.26
Zinc	70

 

Generic exclusion levels for F006 nonwastewater HTMR residues:
Constituent	Maximum for any single composite sample (mg/ℓ)
Antimony	0.10
Arsenic	0.50
Barium	7.6
Beryllium	0.010
Cadmium	0.050
Chromium (total)	0.33
Cyanide (total) (mg/kg)	1.8
Lead	0.15
Mercury	0.009
Nickel	1.0
Selenium	0.16
Silver	0.30
Thallium	0.020
Zinc	70

 

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

 

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

 

D)        Biological treatment sludge from the treatment of one of the following wastes listed in Section 721.132:  organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes (USEPA hazardous waste number K156) and wastewaters from the production of carbamates and carbamoyl oximes (USEPA hazardous waste number K157).

 

E)        Catalyst inert support media separated from one of the following wastes listed in Section 721.132: spent hydrotreating catalyst (USEPA hazardous waste number K171) and spent hydrorefining catalyst (USEPA hazardous waste number K172).

 

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

 

f)         Notwithstanding subsections (a) through (e) and provided the debris, as defined in 35 Ill. Adm. Code 728.102, does not exhibit a characteristic identified at Subpart C, the following materials are not subject to  regulation under 35 Ill. Adm. Code 702, 703, 720, 721 to 726, or 728:

 

1)         Hazardous debris as defined in 35 Ill. Adm. Code 728.102 that has been treated using one of the required extraction or destruction technologies specified in Table F to 35 Ill. Adm. Code 728; persons claiming this exclusion in an enforcement action will have the burden of proving by clear and convincing evidence that the material meets all of the exclusion requirements; or

 

2)         Debris, as defined in 35 Ill. Adm. Code 728.102, that the Agency, considering the extent of contamination, has determined is no longer contaminated with hazardous waste.

 

g)         Exclusion of certain wastes listed in Subpart D solely because they exhibit a characteristic of ignitability, corrosivity, or reactivity.

 

1)         A hazardous waste that is listed in Subpart D solely because it exhibits one or more characteristics of ignitability, as defined under Section 721.121; corrosivity, as defined under Section 721.122; or reactivity, as defined under Section 721.123 is not a hazardous waste if the waste no longer exhibits any characteristic of hazardous waste identified in Subpart C.

 

2)         The exclusion described in subsection (g)(1) also pertains to the following:

 

A)        Any mixture of a solid waste and a hazardous waste listed in Subpart D solely because it exhibits the characteristics of ignitability, corrosivity, or reactivity, as regulated under subsection (a)(2)(D); and

 

B)        Any solid waste generated from treating, storing, or disposing of a hazardous waste listed in Subpart D solely because it exhibits the characteristics of ignitability, corrosivity, or reactivity, as regulated under subsection (e)(1).

 

3)         Wastes excluded pursuant to this subsection (g) are subject to 35 Ill. Adm. Code 728 (as applicable), even if they no longer exhibit a characteristic at the point of land disposal.

 

4)         Any mixture of a solid waste excluded from regulation in Section 721.104(b)(7) and a hazardous waste listed in Subpart D solely because the listed hazardous waste exhibits one or more of the characteristics of ignitability, corrosivity, or reactivity, as regulated under subsection (a)(2)(D), is not a hazardous waste if the mixture no longer exhibits any characteristic of hazardous waste identified in Subpart C for which USEPA listed the hazardous waste listed in Subpart D.

 

h)         Eligible Radioactive Mixed Waste

 

1)         Hazardous waste containing radioactive waste is no longer a hazardous waste when it meets the eligibility criteria and conditions of Subpart N of 35 Ill. Adm. Code 726 (i.e., it is "eligible radioactive mixed waste").

 

2)         The exemption described in subsection (h)(1) also pertains to the following:

 

A)        Any mixture of a solid waste and an eligible radioactive mixed waste; and

 

B)        Any solid waste generated from treating, storing, or disposing of an eligible radioactive mixed waste.

 

3)         Waste exempted pursuant to this subsection (h) must meet the eligibility criteria and specified conditions in 35 Ill. Adm. Code 726.325 and 726.330 (for storage and treatment) and in 35 Ill. Adm. Code 726.410 and 726.415 (for transportation and disposal).  Waste that fails to satisfy these eligibility criteria and conditions is regulated as hazardous waste.

 

(Source:  Amended at 42 Ill. Reg. 21673, effective November 19, 2018)

 

Section 721.104  Exclusions

 

a)         Materials That Are Not Solid Wastes.  The following materials are not solid wastes for this Part:

 

1)         Sewage.

 

A)        Domestic sewage (untreated sanitary wastes that pass through a sewer system); and

 

B)        Any mixture of domestic sewage and other waste that passes through a sewer system to publicly-owned treatment works for treatment, except as prohibited by 35 Ill. Adm. Code 726.605 and 40 CFR 403.5(b), incorporated by reference in 35 Ill. Adm. Code 720.111.

 

2)         Industrial wastewater discharges that are point source discharges with NPDES permits issued by the Agency under Section 12(f) of the  Act and 35 Ill. Adm. Code 309.

 

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

 

3)         Irrigation return flows.

 

4)         Source, by-product, or special nuclear material, as defined by Section 11 of the Atomic Energy Act of 1954, as amended (42 USC 2014), incorporated by reference in 35 Ill. Adm. Code 720.111(b).

 

5)         Materials subjected to in-situ mining techniques that are not removed from the ground as part of the extraction process.

 

6)         Pulping liquors (i.e., black liquors) that are reclaimed in a pulping liquor recovery furnace and then reused in the pulping process, unless it is accumulated speculatively, as defined in Section 721.101(c).

 

7)         Spent sulfuric acid used to produce virgin sulfuric acid, provided it is not accumulated speculatively, as defined in Section 721.101(c).

 

8)         Secondary materials that are reclaimed and returned to the original process or processes in which they were generated, if they are reused in the production process, provided that the following is true:

 

A)        Only tank storage is involved, and the entire process through completing reclamation is closed by being entirely connected with pipes or other comparable enclosed means of conveyance;

 

B)        Reclamation does not involve controlled flame combustion (like that occurring in boilers, industrial furnaces, or incinerators);

 

C)        The secondary materials are never accumulated in tanks for over 12 months without being reclaimed; and

 

D)        The reclaimed material is not used to produce a fuel or used to produce products that are used in a manner constituting disposal.

 

9)         Wood preserving wastes.

 

A)        Spent wood preserving solutions that have been used and that are reclaimed and reused for their original intended purpose;

 

B)        Wastewaters from the wood preserving process that have been reclaimed and that are reused to treat wood; and

 

C)        Prior to reuse, the wood preserving wastewaters and spent wood preserving solutions described in subsections (a)(9)(A) and (a)(9)(B), so long as they meet the following conditions:

 

i)          The wood preserving wastewaters and spent wood preserving solutions are reused on-site at water-borne plants in the production process for their original intended purpose;

 

ii)         Prior to reuse, the wastewaters and spent wood preserving solutions are managed to prevent release to either land or groundwater or both;

 

iii)        Any unit used to manage wastewaters or spent wood preserving solutions prior to reuse can be visually or otherwise determined to prevent such releases;

 

iv)        Any drip pad used to manage the wastewaters or spent wood preserving solutions prior to reuse complies with the standards in Subpart W of 35 Ill. Adm. Code 725, regardless of whether the plant generates a total of less than 100 kg/month of hazardous waste; and

 

v)         Prior to operating under this exclusion, the plant owner or operator prepares a one-time notification to the Agency stating that the plant intends to claim the exclusion, giving the date on which the plant intends to begin operating under the exclusion, and containing the following language:  "I have read the applicable regulation establishing an exclusion for wood preserving wastewaters and spent wood preserving solutions and understand it requires me to comply at all times with the conditions set out in the regulation."  The plant must maintain a copy of that document in its on-site records until closure of the facility.  The exclusion applies only so long as the plant meets the conditions under subsection (a)(9)(C).  If the plant does not comply with any condition, it may apply to the Agency for reinstatement of the exclusion.  The Agency must reinstate the exclusion in writing if it finds that the plant has returned to complying 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, grant the reinstatement with conditions, or terminate a reinstatement before the Board under Section 40 of the Act.

 

10)       USEPA hazardous waste numbers K060, K087, K141, K142, K143, K144, K145, K147, and K148, and any wastes from the coke by-products processes that are hazardous only because they exhibit the toxicity characteristic specified in Section 721.124, when subsequent to generation these materials are recycled to coke ovens, to the tar recovery process as a feedstock to produce coal tar, or are mixed with coal tar prior to the tar's sale or refining.  This exclusion is conditioned on there being no land disposal of the waste from the point it is generated to the point it is recycled to coke ovens, to tar recovery, to the tar refining processes, or prior to when it is mixed with coal.

 

11)       Nonwastewater splash condenser dross residue from the treatment of USEPA hazardous waste number K061 in high temperature metals recovery units, provided it is shipped in drums (if shipped) and not land disposed before recovery.

 

12)       Certain oil-bearing hazardous secondary materials and recovered oil, as follows:

 

A)        Oil-bearing hazardous secondary materials (i.e., sludges, by-products, or spent materials) that are generated at a petroleum refinery (standard industrial classification (SIC) code 2911) and are inserted into the petroleum refining process (SIC code 2911: including, distillation, catalytic cracking, fractionation, or thermal cracking units (i.e., cokers)), unless the material is placed on the land, or speculatively accumulated before being so recycled.  Materials inserted into thermal cracking units are excluded under this subsection (a)(12), if the coke product also does not exhibit a characteristic of hazardous waste.  Oil-bearing hazardous secondary materials may be inserted into the same petroleum refinery where they are generated or sent directly to another petroleum refinery and still be excluded under this provision.  Except as provided in subsection (a)(12)(B), oil-bearing hazardous secondary materials generated elsewhere in the petroleum industry (i.e., from sources other than petroleum refineries) are not excluded under this Section.  Residuals generated from processing or recycling materials excluded under this subsection (a)(12)(A), if the materials as generated would have otherwise met a listing under Subpart D, are designated as USEPA hazardous waste number F037 listed wastes when disposed of or intended for disposal.

 

B)        Recovered oil that is recycled in the same manner and with the same conditions as described in subsection (a)(12)(A).  Recovered oil is oil that has been reclaimed from secondary materials (including wastewater) generated from normal petroleum industry practices, including refining, exploration and production, bulk storage, and transportation incident (SIC codes 1311, 1321, 1381, 1382, 1389, 2911, 4612, 4613, 4922, 4923, 4789, 5171, and 5172).  Recovered oil does not include oil-bearing hazardous wastes listed in Subpart D; however, oil recovered from such wastes may be considered recovered oil.  Recovered oil does not include used oil, as defined in 35 Ill. Adm. Code 739.100.

 

13)       Excluded scrap metal (processed scrap metal, unprocessed home scrap metal, and unprocessed prompt scrap metal) being recycled.

 

14)       Shredded circuit boards being recycled if they meet the following conditions:

 

A)        The circuit boards are stored in containers sufficient to prevent a release to the environment prior to recovery; and

 

B)        The circuit boards are free of mercury switches, mercury relays, nickel-cadmium batteries, and lithium batteries.

 

15)       Condensates derived from the overhead gases from kraft mill steam strippers that are used to comply with federal Clean Air Act regulation 40 CFR 63.446(e).  The exemption applies only to combustion at the mill generating the condensates.

 

16)       This subsection (a)(16) corresponds with 40 CFR 261.4(a)(16), marked "reserved" by USEPA.  This statement maintains structural consistency with the federal regulations.

 

17)       Spent materials (as defined in Section 721.101) (other than hazardous wastes listed in Subpart D) generated within the primary mineral processing industry from which minerals, acids, cyanide, water, or other values are recovered by mineral processing or by beneficiation, if:

 

A)        The spent material is legitimately recycled to recover minerals, acids, cyanide, water, or other values;

 

B)        The spent material is not accumulated speculatively;

 

C)        Except as provided in subsection (a)(17)(D), the spent material is stored in tanks, containers, or buildings that meet the following minimum integrity standards:  a building must be an engineered structure with a floor, walls, and a roof that are made of non-earthen materials providing structural support (except that smelter buildings may have partially earthen floors if the spent material is stored on the non-earthen portion), and have a roof suitable for diverting rainwater away from the foundation; a tank must be free standing, not be a surface impoundment (as defined in 35 Ill. Adm. Code 720.110), and be manufactured of a material suitable for containment of its contents; a container must be free standing and be manufactured of a material suitable for containment of its contents.  If a tank or container contains any particulate that may be subject to wind dispersal, the owner or operator must operate the unit in a manner that controls fugitive dust.  A tank, container, or building must be designed, constructed, and operated to prevent significant releases to the environment of these materials.

 

D)        The Agency must allow by permit in writing that solid mineral processing spent materials only may be placed on pads, rather than in tanks, containers, or buildings if the facility owner or operator can demonstrate the following:  the solid mineral processing secondary materials do not contain any free liquid; the pads are designed, constructed, and operated to prevent significant releases of the spent material into the environment; and the pads provide the same degree of containment afforded by the non-RCRA tanks, containers, and buildings eligible for exclusion.

 

i)          The Agency must also consider whether storage on pads poses the potential for significant releases via groundwater, surface water, and air exposure pathways.  Factors to be considered for assessing the groundwater, surface water, and air exposure pathways must include the following:  the volume and physical and chemical properties of the spent material, including its potential for migration off the pad; the potential for human or environmental exposure to hazardous constituents migrating from the pad via each exposure pathway; and the possibility and extent of harm to human and environmental receptors via each exposure pathway.

 

ii)         Pads must meet the following minimum standards:  they must be designed of non-earthen material that is compatible with the chemical nature of the mineral processing spent material; they must be capable of withstanding physical stresses associated with placement and removal; they must have run-on and run-off controls; they must be operated in a manner that controls fugitive dust; and they must have integrity assurance through inspections and maintenance programs.

 

iii)        Before making a determination under this subsection (a)(17)(D), the Agency must provide notice and the opportunity for comment to all persons potentially interested in the determination.  This can be accomplished by placing notice of this action in major local newspapers, or broadcasting notice over local radio stations.

 

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

 

E)        The owner or operator provides a notice to the Agency, providing the following information:  the types of materials to be recycled, the type and location of the storage units and recycling processes, and the annual quantities expected to be placed in land-based units.  This notification must be updated when there is a change in the type of materials recycled or the location of the recycling process.

 

F)         For subsection (b)(7), mineral processing spent materials must be the result of mineral processing and may not include any listed hazardous wastes.  Listed hazardous wastes and characteristic hazardous wastes generated by non-mineral processing industries are not eligible for the conditional exclusion from the definition of solid waste.

 

18)       Petrochemical recovered oil from an associated organic chemical manufacturing facility, if the oil is to be inserted into the petroleum refining process (SIC code 2911) along with normal petroleum refinery process streams, if:

 

A)        The oil is hazardous only because it exhibits the characteristic of ignitability (as defined in Section 721.121) or toxicity for benzene (Section 721.124, USEPA hazardous waste number D018); and

 

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 the:  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, if that the following conditions are met:

 

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:

 

i)          Submit a one-time notice to the Agency that contains the name, address, and USEPA identification number of the generator or intermediate handler facility, that provides a brief description of the secondary material that will be subject to the exclusion, and that identifies when the manufacturer intends to begin managing excluded zinc-bearing hazardous secondary materials under the conditions specified in this subsection (a)(20).

 

ii)         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 meet the conditions of subsection (a)(20)(F).

 

iii)        With each off-site shipment of excluded hazardous secondary materials, provide written notice to the receiving facility that the material is subject to the conditions of this subsection (a)(20).

 

iv)        Maintain records at the generator's or intermediate handler's facility, for at least three years, of all shipments of excluded hazardous secondary materials.  For each shipment these records must, at a minimum, contain the information specified in subsection (a)(20)(G).

 

C)        A manufacturer of zinc fertilizers or zinc fertilizer ingredients made from excluded hazardous secondary materials must:

 

i)          Store excluded hazardous secondary materials in compliance with the storage requirements for generators and intermediate handlers, as specified in subsection (a)(20)(B)(ii).

 

ii)         Submit a one-time notification to the Agency that, at a minimum, specifies the name, address, and USEPA identification number of the manufacturing facility and that identifies when the manufacturer intends to begin managing excluded zinc-bearing hazardous secondary materials under the conditions specified in this subsection (a)(20).

 

iii)        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)        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 submitting the one-time notice described in subsection (a)(20)(B)(i), and that afterward will be used only to store hazardous secondary materials excluded under this subsection (a)(20), are not subject to the closure requirements of 35 Ill. Adm. Code 724 and 725.

 

F)         Storage areas where containers are stored outdoors under subsection (a)(20)(B)(ii), must:

 

i)          Have containment structures or systems sufficiently impervious to contain leaks, spills, and accumulated precipitation;

 

ii)         Provide for effective drainage and removal of leaks, spills, and accumulated precipitation; and

 

iii)        Prevent run-on into the containment system.

 

BOARD NOTE:  Subsections (a)(20)(F)(i) through (a)(20)(F)(iii) are derived from 40 CFR 261.4(a)(20)(ii)(B)(1) through (a)(20)(ii)(B)(3).  The Board added the preamble to these federal paragraphs as subsection (a)(20)(F) to comport with Illinois Administrative Code codification requirements.

 

G)        Required records of shipments of excluded hazardous secondary materials under subsection (a)(20)(B)(iv) must, at a minimum, contain the following information:

 

i)          The name of the transporter and date of the shipment;

 

ii)         The name and address of the facility that received the excluded material, along with documentation confirming receipt of the shipment; and

 

iii)        The type and quantity of excluded secondary material in each shipment.

 

BOARD NOTE:  Subsections (a)(20)(G)(i) through (a)(20)(G)(iii) are derived from 40 CFR 261.4(a)(20)(ii)(D)(1) through (a)(20)(ii)(D)(3).  The Board added the preamble to these federal paragraphs as subsection (a)(20)(G) to comport with Illinois Administrative Code codification requirements.

 

21)       Zinc fertilizers made from hazardous wastes or hazardous secondary materials that are excluded under subsection (a)(20), if:

 

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 at least once every six months, and for dioxins at least 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 a constituent of concern is not 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 at least three years, records of all sampling and analyses performed for determining compliance with subsection (a)(21)(B).  The 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 if they comply with Section 721.140.

 

C)        Used, broken CRTs, as defined in 35 Ill. Adm. Code 720.110, are not solid waste if they comply with the requirements of Section 721.139.

 

D)        Glass removed from CRTs is not a solid waste if it complies with the requirements of Section 721.139(c).

 

23)       Hazardous Secondary Materials Reclaimed under the Control of the Generator.  Hazardous secondary material generated and legitimately reclaimed within the United States or its territories and under the control of the generator, if the material complies with subsections (a)(23)(A) and (a)(23)(B):

 

A)        Excluded Hazardous Secondary Materials

 

i)          The hazardous secondary material is generated and reclaimed at the generating facility.  (For this subsection (a)(23)(A)(i), "generating facility" means all contiguous property owned, leased, or otherwise controlled by the hazardous secondary material generator.);

 

ii)         The hazardous secondary material is generated and reclaimed at different facilities, if the reclaiming facility is controlled by the generator or if both the generating facility and the reclaiming facility are controlled by a person as defined in 35 Ill. Adm. Code 720.110, and if the generator provides one of the following certifications:

 

"On behalf of [insert generator facility name], I certify that this facility will send the indicated hazardous secondary material to [insert reclaimer facility name], which is controlled by [insert generator facility name] and that [insert name of either facility] has acknowledged full responsibility for the safe management of the hazardous secondary material."

 

or

 

"On behalf of [insert generator facility name], I certify that this facility will send the indicated hazardous secondary material to [insert reclaimer facility name], that both facilities are under common control, and that [insert name of either facility] has acknowledged full responsibility for the safe management of the hazardous secondary material."

 

For subsection (a)(23)(A)(ii), "control" means the power to direct the policies of the facility, whether by the ownership of stock, voting rights, or otherwise, except that contractors who operate facilities on behalf of a different person, as defined in 35 Ill. Adm. Code 720.110, cannot be deemed to "control" such facilities.  The generating and receiving facilities must both maintain at their facilities, for no less than three years, records of hazardous secondary materials sent or received under this exclusion.  In both cases, the records must contain the name of the transporter, the date of the shipment, and the type and quantity of the hazardous secondary material shipped or received under the exclusion.  These requirements may be satisfied by routine business records (e.g., financial records, bills of lading, copies of USDOT shipping papers, or electronic confirmations); or

 

iii)        The hazardous secondary material is generated under a written contract between a tolling contractor and a toll manufacturer and is reclaimed by the tolling contractor, if the tolling contractor certifies as follows:

 

"On behalf of [insert tolling contractor name], I certify that [insert tolling contractor name] has a written contract with [insert toll manufacturer name] to manufacture [insert name of product or intermediate] which is made from specified unused materials, and that [insert tolling contractor name] will reclaim the hazardous secondary materials generated during this manufacture.  On behalf of [insert tolling contractor name], I also certify that [insert tolling contractor name] retains ownership of, and responsibility for, the hazardous secondary materials that are generated during the course of the manufacture, including any releases of hazardous secondary materials that occur during the manufacturing process."

 

The tolling contractor must maintain at its facility, for at least three years, records of hazardous secondary materials received under its written contract with the tolling manufacturer, and the tolling manufacturer must maintain at its facility, for no less than three years, records of hazardous secondary materials shipped under its written contract with the tolling contractor.  In both cases, the records must contain the name of the transporter, the date of the shipment, and the type and quantity of the hazardous secondary material shipped or received under the written contract.  These requirements may be satisfied by routine business records (e.g., financial records, bills of lading, copies of USDOT shipping papers, or electronic confirmations).  For this subsection (a)(23)(A)(ii), "tolling contractor" means a person who arranges for producing a product or intermediate made from specified unused materials through a written contract with a toll manufacturer.  "Toll manufacturer" means a person who produces a product or intermediate made from specified unused materials under a written contract with a tolling contractor.

 

B)        Management of Hazardous Secondary Materials

 

i)          The hazardous secondary material is contained, as defined in 35 Ill. Adm. Code 720.110.  A hazardous secondary material released to the environment is discarded material and a solid waste unless it is immediately recovered for reclamation.  Hazardous secondary material managed in a unit with leaks or other continuing or intermittent unpermitted releases is discarded material and a solid waste;

 

ii)         The hazardous secondary material is not speculatively accumulated, as defined in Section 721.101(c)(8);

 

iii)        Notice is provided, as required by 35 Ill. Adm. Code 720.142;

 

iv)        The hazardous secondary material is not otherwise subject to material-specific management conditions under subsection (a) when reclaimed, and it is not a spent lead acid battery (see 35 Ill. Adm. Code 726.180 and 733.102);

 

v)         Persons performing the recycling of hazardous secondary materials under this exclusion must maintain documentation of their legitimacy determination on-site.  Documentation must be a written description of how the recycling meets all three  factors in 35 Ill. Adm. Code 720.143(a) and how the factor in 35 Ill. Adm. Code 720.143(b) was considered.  Documentation must be maintained for three years after the recycling operation has ceased; and

 

vi)        The emergency preparedness and response requirements found in Subpart M are met.

 

24)       Hazardous Secondary Materials Transferred for Off-Site Reclamation.  Hazardous secondary material that is generated and then transferred to another person for reclamation is not a solid waste if the management of the material meets the conditions of subsections (a)(24)(A) through (a)(24)(G):

 

A)        The hazardous secondary material must not be speculatively accumulated, as defined in Section 721.101(c)(8).

 

B)        No person or facility other than the hazardous secondary material generator, the transporter, an intermediate facility, or a reclaimer manages the material; the hazardous secondary material must not be stored for more than ten days at a transfer facility, as defined in Section 721.110; and the hazardous secondary material must be packaged according to applicable USDOT regulations codified as 49 CFR 173, 178, and 179, incorporated by reference in 35 Ill. Adm. Code 720.111, while in transport.

 

C)        The hazardous secondary material must not otherwise be subject to material-specific management conditions under other provisions of this subsection (a) when reclaimed, and the hazardous secondary material must not be a spent lead-acid battery (see 35 Ill. Adm. Code 726.180 and 733.102).

 

D)        Reclaiming the hazardous secondary material must be legitimate, as determined under 35 Ill. Adm. Code 720.143.

 

E)        The hazardous secondary material generator must meet each of the following conditions:

 

i)          The hazardous secondary material must be contained as defined in 35 Ill. Adm. Code 720.110.  A hazardous secondary material released to the environment is discarded and a solid waste unless it is immediately recovered for recycling.  Hazardous secondary material managed in a unit that leaks or that otherwise continuously releases hazardous secondary material is discarded material and a solid waste.

 

ii)         Prior to arranging for transport of hazardous secondary materials to a reclamation facility where the hazardous secondary material is managed in a unit that is not subject to a RCRA permit or interim status standards, the hazardous secondary material generator must make reasonable efforts to ensure that each reclaimer intends to properly and legitimately reclaim the hazardous secondary material and not discard it, and that each reclaimer will manage the hazardous secondary material in a manner that is protective of human health and the environment.  If the hazardous secondary material will pass through an intermediate facility where the hazardous secondary materials is managed at that facility in a unit that is not subject to a RCRA permit or interim status standards, the hazardous secondary material generator must make contractual arrangements with the intermediate facility to ensure that the hazardous secondary material is sent to the reclamation facility identified by the hazardous secondary material generator, and the hazardous secondary material generator must perform reasonable efforts to ensure that the intermediate facility will manage the hazardous secondary material in a manner that is protective of human health and the environment.  Reasonable efforts must be repeated at a minimum of every three years for the hazardous secondary material generator to claim the exclusion and to send the hazardous secondary materials to each reclaimer and any intermediate facility.  In making these reasonable efforts, the generator may use any credible evidence available, including information gathered by the hazardous secondary material generator, provided by the reclaimer or intermediate facility, or provided by a third party.  The hazardous secondary material generator must affirmatively answer the questions in subsection (a)(24)(H) for each reclamation facility and any intermediate facility.

 

BOARD NOTE:  The Board moved the required generator inquiries of 40 CFR 261.4(a)(24)(v)(B)(1) through (a)(24)(v)(B)(5) to subsection (a)(24)(H) to comply with codification requirements.

 

iii)        The hazardous secondary material generator must maintain for a minimum of three years documentation and certification that reasonable efforts were made for each reclamation facility and, if applicable, intermediate facility where the facility manages the hazardous secondary materials in a unit that is not subject to a RCRA permit or interim status standards prior to transferring hazardous secondary material.  Documentation and certification must be made available upon request by USEPA or the Agency within 72 hours, or within a longer period as specified by USEPA or the Agency.  The certification statement must include the printed name and official title of an authorized representative of the hazardous secondary material generator company, the authorized representative's signature, and the date signed.  The certification statement must also incorporate the following language:

 

"I hereby certify in good faith and to the best of my knowledge that, prior to arranging for transport of excluded hazardous secondary materials to [insert name(s) of reclamation facility and any intermediate facility], reasonable efforts were made in compliance with 35 Ill. Adm. Code 721.104(a)(24)(E)(ii) to ensure that the hazardous secondary materials would be recycled legitimately, and otherwise managed in a manner that is protective of human health and the environment, and that such efforts were based on current and accurate information."

 

BOARD NOTE:  The Board combined the documentation, certification, and records retention requirements of corresponding 40 CFR 261.4(a)(24)(v)(C)(1) through (a)(24)(v)(C)(3) into subsection (a)(24)(E)(iii) to comply with codification requirements.

 

iv)        The hazardous secondary material generator must maintain certain records at the generating facility for a minimum of three years that document every off-site shipment of hazardous secondary materials.  The documentation for each shipment must, at a minimum, include the following information about the shipment:  the name of the transporter and date of the shipment; the name and address of each reclaimer and intermediate facility to which the hazardous secondary material was sent; and the type and quantity of hazardous secondary material in the shipment.

 

BOARD NOTE:  The Board combined and moved the shipping documentation and records retention requirements of corresponding 40 CFR 261.4(a)(24)(v)(C) and (a)(24)(v)(C)(1) through (a)(24)(v)(C)(3) to this single subsection (a)(24)(E)(iv).  This combination allowed complying with codification requirements relating to the maximum permissible indent level.

 

v)         The hazardous secondary material generator must maintain at the generating facility, for a minimum of three years, for every off-site shipment of hazardous secondary materials, confirmations of receipt from each reclaimer and intermediate facility to which its hazardous secondary materials were sent.  Each confirmation of receipt must include the name and address of the reclaimer (or intermediate facility), the type and quantity of the hazardous secondary materials received, and the date on which the facility received the hazardous secondary materials.  The generator may meet this requirement using routine business records (e.g., financial records, bills of lading, copies of USDOT shipping papers, or electronic confirmations of receipt).

 

vi)        The hazardous secondary material generator must comply with the emergency preparedness and response conditions in Subpart M.

 

BOARD NOTE:  The Board intends that "RCRA permit" in subsections (a)(24)(E)(ii) and (a)(24)(E)(iii) include a permit issued by USEPA or a sister state under section 3005 of RCRA (42 USC 6925).

 

F)         The reclaimer of hazardous secondary material or any intermediate facility, as defined in 35 Ill. Adm. Code 720.110, that manages material that is excluded from regulation under this subsection (a)(24) must meet the following conditions:

 

i)          The owner or operator of a reclamation or intermediate facility must maintain at its facility for a minimum of three years records of every shipment of hazardous secondary material that the facility received and, if applicable, for every shipment of hazardous secondary material that the facility received and subsequently sent off-site from the facility for further reclamation.  For each shipment, these records must, at a minimum, contain the following information:  the name of the transporter and date of the shipment; the name and address of the hazardous secondary material generator and, if applicable, the name and address of the reclaimer or intermediate facility from which the facility received the hazardous secondary materials; the type and quantity of hazardous secondary material in the shipment; and, for hazardous secondary materials that the facility subsequently transferred off-site for further reclamation after receiving it, the name and address of the (subsequent) reclaimer and any intermediate facility to which the facility sent the hazardous secondary material.

 

BOARD NOTE:  The Board combined the provisions from 40 CFR 261.4(a)(24)(vi)(A) and (a)(24)(vi)(A)(1) through (a)(24)(vi)(A)(3) that enumerate the required information into this single subsection (a)(24)(F)(i).  This combination allowed complying with codification requirements relating to the maximum permissible indent level.

 

ii)         The intermediate facility must send the hazardous secondary material to the reclaimers designated by the generator of the hazardous secondary materials.

 

iii)        The reclaimer or intermediate facility that receives a shipment of hazardous secondary material must send a confirmation of receipt to the hazardous secondary material generator for each off-site shipment of hazardous secondary materials.  A confirmation of receipt must include the name and address of the reclaimer (or intermediate facility), the type and quantity of the hazardous secondary materials received, and the date on which the facility received the hazardous secondary materials.  The reclaimer or intermediate facility may meet this requirement using routine business records (e.g., financial records, bills of lading, copies of USDOT shipping papers, or electronic confirmations of receipt).

 

iv)        The reclaimer or intermediate facility must manage the hazardous secondary material in a manner that is at least as protective of human health and the environment as that employed for analogous raw material, and the material must be contained.  An "analogous raw material" is a raw material for which the hazardous secondary material substitutes and that serves the same function and has similar physical and chemical properties as the hazardous secondary material.

 

v)         A reclaimer of hazardous secondary materials must manage any residuals that are generated from its reclamation processes in a manner that is protective of human health and the environment.  If any residuals of the reclamation process exhibit a characteristic of hazardous waste, as defined in Subpart C, or if the residuals themselves are specifically listed as hazardous waste in Subpart D, those residuals are hazardous waste.  The reclaimer and any subsequent persons must manage that hazardous waste in compliance with the applicable requirements of 35 Ill. Adm. Code:  Subtitle G or similar regulations authorized by USEPA as equivalent to 40 CFR 260 through 272.

 

vi)        The reclaimer and intermediate facility must have financial assurance that complies with Subpart H.

 

G)        In addition, any person claiming the exclusion for recycled hazardous secondary material under this subsection (a)(24) must provide notification as required by 35 Ill. Adm. Code 720.142.

 

H)        For the reasonable inquiries required by subsection (a)(24)(E)(ii), the hazardous secondary material generator must affirmatively answer the following questions for each reclamation facility and any intermediate facility:

 

i)          Does the available information indicate that the reclamation process is legitimate under 35 Ill. Adm. Code 720.143?  In answering this question, the hazardous secondary material generator can rely on its existing knowledge of the physical and chemical properties of the hazardous secondary material, as well as information from other sources (e.g., the reclamation facility, audit reports, etc.) about the reclamation process.

 

ii)         Does the publicly available information indicate that the reclamation facility and any intermediate facility that is used by the hazardous secondary material generator notified the appropriate authorities of hazardous secondary materials reclamation activities under 35 Ill. Adm. Code 720.142, and have they notified the appropriate authorities that the financial assurance condition is satisfied per subsection (a)(24)(F)(vi)?  In answering these questions, the hazardous secondary material generator can rely on the available information documenting the reclamation facility's and any intermediate facility's complying with the notification requirements per 35 Ill. Adm. Code 720.142, including the requirement in 35 Ill. Adm. Code 720.142(a)(5) to notify USEPA or the Agency whether the reclaimer or intermediate facility has financial assurance.

 

iii)        Does publicly available information indicate that the reclamation facility or any intermediate facility that is used by the hazardous secondary material generator has not had any formal enforcement actions taken against the facility in the previous three years for violations of the RCRA hazardous waste regulations and has not been classified as a significant noncomplier with RCRA Subtitle C?  In answering this question, the hazardous secondary material generator can rely on the publicly available information from USEPA or the state.  If the reclamation facility or any intermediate facility that is used by the hazardous secondary material generator has had a formal enforcement action taken against the facility in the previous three years for violations of the RCRA hazardous waste regulations and has been classified as a significant non-complier with RCRA Subtitle C, does the hazardous secondary material generator have credible evidence that the facility will manage the hazardous secondary materials properly?  In answering this question, the hazardous secondary material generator can obtain additional information from USEPA, the state, or the facility itself that the facility has addressed the violations, taken remedial steps to address the violations and prevent future violations, or that the violations are not relevant to the proper management of the hazardous secondary materials.

 

iv)        Does the available information indicate that the reclamation facility and any intermediate facility that is used by the hazardous secondary material generator have the equipment and trained personnel to safely recycle the hazardous secondary material?  In answering this question, the generator may rely on a description by the reclamation facility or by an independent third party of the equipment and trained personnel to be used to recycle the generator's hazardous secondary material.

 

v)         If residuals are generated from reclaiming the excluded hazardous secondary materials, does the reclamation facility have the permits required (if any) to manage the residuals?  If not, does the reclamation facility have a contract with an appropriately permitted facility to dispose of the residuals?  If not, does the hazardous secondary material generator have credible evidence that the residuals will be managed in a manner that is protective of human health and the environment?  In answering these questions, the hazardous secondary material generator can rely on publicly available information from USEPA or the state, or information provided by the facility itself.

 

BOARD NOTE:  The Board moved the required generator inquiries into a reclamation or intermediate facility of 40 CFR 261.4(a)(24)(v)(B) and (a)(24)(v)(B)(1) through (a)(24)(v)(B)(5) to this subsection (a)(24)(H) to comply with codification requirements.

 

25)       Hazardous secondary material that is exported from the United States and reclaimed at a reclamation facility located in a foreign country is not a solid waste, provided that the hazardous secondary material generator complies with the applicable requirements of subsections (a)(24)(A) through (a)(24)(E) and (a)(24)(H) (excepting subsection (a)(24)(H)(ii) for foreign reclaimers and foreign intermediate facilities), and that the hazardous secondary material generator also complies with the following requirements:

 

A)        The generator must notify USEPA of an intended export before the hazardous secondary material is scheduled to leave the United States.  The generator must submit a complete notification at least 60 days before the initial shipment is intended to be shipped off-site.  This notification may cover export activities extending over a 12-month or lesser period.  The notification must be in writing, signed by the hazardous secondary material generator, and include the following information:

 

i)          The name, mailing address, telephone number and USEPA identification number (if applicable) of the hazardous secondary material generator;

 

ii)         A description of the hazardous secondary material and the USEPA hazardous waste number that would apply if the hazardous secondary material were managed as hazardous waste and the USDOT proper shipping name, hazard class and identification number (UN or NA) for each hazardous secondary material as identified in the hazardous materials table in 49 CFR 172.101, incorporated by reference in 35 Ill. Adm. Code 720.111;

 

iii)        The estimated frequency or rate at which the hazardous secondary material is to be exported and the period over which the hazardous secondary material is to be exported;

 

iv)        The estimated total quantity of hazardous secondary material;

 

v)         All points of entry to and departure from each foreign country through which the hazardous secondary material will pass;

 

vi)        A description of the means by which each shipment of the hazardous secondary material will be transported (e.g., mode of transportation vehicle (air, highway, rail, water, etc.), types of container (drums, boxes, tanks, etc.), etc.);

 

vii)       A description of how the hazardous secondary material will be reclaimed in the country of import;

 

viii)      The name and address of the reclaimer, any intermediate facility, and any alternate reclaimer and intermediate facilities; and

 

ix)        The name of any countries of transit through which the hazardous secondary material will be sent and a description of the approximate length of time it will remain in such countries and the nature of its handling while there (for this Section, the terms "USEPA Acknowledgement of Consent", "country of import", and "country of transit" are used as defined in 35 Ill. Adm. Code 722.181 with the exception that the terms in this Section refer to hazardous secondary materials, rather than hazardous waste).

 

B)        The generator must submit notifications electronically using USEPA's Waste Import Export Tracking System (WIETS).

 

C)        Except for changes to the telephone number required in subsection (a)(25)(A)(i) and decreases in the quantity of hazardous secondary material indicated under subsection (a)(25)(A)(iv), when the conditions specified on the original notification change (including any exceedance of the estimate of the quantity of hazardous secondary material specified in the original notification), the hazardous secondary material generator must provide USEPA with a written renotification of the change.  The shipment must not occur until consent of the country of import to the changes (except for changes to subsection (a)(25)(A)(ix) and in the ports of entry to and departure from countries of transit under subsection (a)(25)(A)(v)) has been obtained and the hazardous secondary material generator receives from USEPA a USEPA Acknowledgment of Consent reflecting the country of import's consent to the changes.

 

D)        Upon request by USEPA, the hazardous secondary material generator must furnish to USEPA any additional information that a country of import requests to respond to a notification.

 

E)        USEPA will provide a complete notification to the country of import and any countries of transit. A notification is complete when USEPA receives a notification that USEPA determines complies with subsection (a)(25)(A). When a claim of confidentiality is asserted with respect to any notification information required by subsection (a)(25)(A), USEPA may find the notification not complete until any such claim is resolved in compliance with 35 Ill. Adm. Code 720.102.

 

F)         The export of hazardous secondary material under this subsection (a)(25) is prohibited unless the hazardous secondary material generator receives from USEPA an USEPA Acknowledgment of Consent documenting the consent of the country of import to the receipt of hazardous secondary material.  When the country of import objects to receipt of the hazardous secondary material or withdraws a prior consent, USEPA will notify the hazardous secondary material generator in writing.  USEPA will also notify the hazardous secondary material generator of any responses from countries of transit.

 

G)        For exports to OECD member countries, the receiving country may respond to the notification using tacit consent.  If no objection has been lodged by any country of import or countries of transit to a notification provided under subsection (a)(25)(A) within 30 days after the date of issuance of the acknowledgement of receipt of notification by the competent authority of the country of import, the transboundary movement may commence.  In such cases, USEPA will send a USEPA Acknowledgment of Consent to inform the hazardous secondary material generator that the country of import and any relevant countries of transit have not objected to the shipment and are thus presumed to have consented tacitly.  Tacit consent expires one calendar year after the close of the 30-day period; renotification and renewal of all consents is required for exports after that date.

 

H)        A copy of the USEPA Acknowledgment of Consent must accompany the shipment.  The shipment must conform to the terms of the USEPA Acknowledgment of Consent.

 

I)         If the shipment cannot be delivered for any reason to the reclaimer, intermediate facility or the alternate reclaimer or alternate intermediate facility, the hazardous secondary material generator must re-notify USEPA of a change in the conditions of the original notification to allow shipment to a new reclaimer in compliance with subsection (a)(25)(C) and obtain another USEPA Acknowledgment of Consent.

 

J)         Hazardous secondary material generators must keep a copy of each notification of intent to export and each USEPA Acknowledgment of Consent for a period of three years following receipt of the USEPA Acknowledgment of Consent. They may meet this recordkeeping requirement by retaining electronically submitted notifications or electronically generated Acknowledgements in their account on USEPA's WIETS, provided that such copies are readily available for viewing and production if requested by any USEPA or Agency inspector.  No hazardous secondary material generator may be held liable for the inability to produce a notification or Acknowledgement for inspection under this Section if it can demonstrate that the inability to produce such copies is due exclusively to technical difficulty with USEPA's WIETS for which the hazardous secondary material generator bears no responsibility.

 

K)        Hazardous secondary material generators must file with USEPA, no later than March 1 of each year, a report summarizing the types, quantities, frequency, and ultimate destination of all hazardous secondary materials exported during the previous calendar year.  Annual reports must be submitted electronically using USEPA's WIETS.  Such reports must include the following information:

 

i)          Name, mailing and site address, and USEPA identification number (if applicable) of the hazardous secondary material generator;

 

ii)         The calendar year covered by the report;

 

iii)        The name and site address of each reclaimer and intermediate facility;

 

iv)        By reclaimer and intermediate facility, for each hazardous secondary material exported, a description of the hazardous secondary material and the USEPA hazardous waste number that would apply if the hazardous secondary material were managed as hazardous waste; the USDOT hazard class, incorporated by reference in 35 Ill. Adm. Code 720.111; the name and USEPA identification number (if applicable) for each transporter used, the consent number(s) under which the hazardous secondary material was shipped and for each consent number(s) the total amount of hazardous secondary material shipped, and the number of shipments during the calender year covered by the report; and

 

v)         A certification signed by the hazardous secondary material generator that states as follows:

 

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

 

L)        Any person claiming an exclusion under this subsection (a)(25) must provide notification as required by 35 Ill. Adm. Code 720.142.

 

26)       Solvent-contaminated wipes that are sent for cleaning and reuse are not solid wastes from the point of generation if the following conditions are met:

 

A)        The solvent-contaminated wipes, when accumulated, stored, and transported, are contained in non-leaking, closed containers that are labeled "Excluded Solvent-Contaminated Wipes".  The containers must be able to contain free liquids, should free liquids occur.  During accumulation, a container is considered closed when there is complete contact between the fitted lid and the rim, except when it is necessary to add or remove solvent-contaminated wipes.  When the container is full, when the solvent-contaminated wipes are no longer being accumulated, or when the container is being transported, the container must be sealed with all lids properly and securely affixed to the container and all openings tightly bound or closed sufficiently to prevent leaks and emissions;

 

B)        The solvent-contaminated wipes may be accumulated by the generator for up to 180 days from the start date of accumulation for each container prior to being sent for cleaning;

 

C)        At the point of being sent for cleaning on-site or at the point of being transported off-site for cleaning, the solvent-contaminated wipes must contain no free liquids, as defined in 35 Ill. Adm. Code 720.110;

 

D)        Free liquids removed from the solvent-contaminated wipes or from the container holding the wipes must be managed according to the applicable regulations found in this Part and 35 Ill. Adm. Code 720, 722 through 728, and 733;

 

E)        Generators must maintain at their site the following documentation:

 

i)          The name and address of the laundry or dry cleaner that is receiving the solvent-contaminated wipes;

 

ii)         The documentation that the 180-day accumulation time limit in 35 Ill. Adm. Code 721.104(a)(26)(B) is being met; and

 

iii)        A description of the process the generator is using to ensure that the solvent-contaminated wipes contain no free liquids at the point of being laundered or dry cleaned on-site or at the point of being transported off-site for laundering or dry cleaning; and

 

F)         The solvent-contaminated wipes are sent to a laundry or dry cleaner whose discharge, if any, is regulated under sections 301 and 402 or section 307 of the federal Clean Water Act (33 USC 1311 and 1341 or 33 USC 1317) or equivalent Illinois or sister-state requirements approved by USEPA under 33 USC 1311 through 1346 and 1370.

 

27)       Hazardous secondary material that is generated and then transferred to another person for remanufacturing is not a solid waste, provided that the following conditions are met:

 

BOARD NOTE:  The North American Industrial Classification System (NAICS) codes used in this subsection (a)(27) are defined in the NAICS Manual, available from the Office of Management and Budget and incorporated by reference in 35 Ill. Adm. Code 720.111.

 

A)        The hazardous secondary material consists of one or more of the following spent solvents:  toluene, xylenes, ethylbenzene, 1,2,4-trimethylbenzene, chlorobenzene, n-hexane, cyclohexane, methyl tert-butyl ether, acetonitrile, chloroform, chloromethane, dichloromethane, methyl isobutyl ketone, N,N-dimethylformamide, tetrahydrofuran, n-butyl alcohol, ethanol, or methanol.

 

B)        The hazardous secondary material originated from using one or more of the solvents listed in subsection (a)(27)(A) in a commercial grade for reacting, extracting, purifying, or blending chemicals (or for rinsing out the process lines associated with these functions) in the pharmaceutical manufacturing (NAICS 325412), basic organic chemical manufacturing (NAICS 325199), plastics and resins manufacturing (NAICS 325211), or the paints and coatings manufacturing sectors (NAICS 325510).

 

C)        The hazardous secondary material generator sends the hazardous secondary material spent solvents listed in subsection (a)(27)(A) to a remanufacturer in the pharmaceutical manufacturing (NAICS 325412), basic organic chemical manufacturing (NAICS 325199), plastics and resins manufacturing (NAICS 325211), or the paints and coatings manufacturing sectors (NAICS 325510).

 

D)        After remanufacturing one or more of the solvents listed in subsection (a)(27)(A), the use of the remanufactured solvent must be limited to reacting, extracting, purifying, or blending chemicals (or for rinsing out the process lines associated with these functions) in the pharmaceutical manufacturing (NAICS 325412), basic organic chemical manufacturing (NAICS 325199), plastics and resins manufacturing (NAICS 325211), and the paints and coatings manufacturing sectors (NAICS 325510) or to using them as ingredients in a product.  These allowed uses correspond to chemical functional uses enumerated in 40 CFR 711.15(b)(4)(i)(C) (Reporting Information to EPA), incorporated by reference in 35 Ill. Adm. Code 720.111, including Industrial Function Category Codes U015 (solvents consumed in a reaction to produce other chemicals) and U030 (solvents that become part of the mixture).

 

BOARD NOTE:  The Board observes that the citation to Toxic Substances Control Act function categories and use of the word "including" to preface specific example Industrial Function Category Codes does not expand the range of permissible uses beyond the express limitations recited in the first segment of this subsection (a)(27)(D) and subsection (a)(27)(E).

 

E)        After remanufacturing one or more of the solvents listed in subsection (a)(27)(i), the use of the remanufactured solvent does not involve cleaning or degreasing oil, grease, or similar material from textiles, glassware, metal surfaces, or other articles.  (These disallowed continuing uses correspond to chemical functional uses in Industrial Function Category Code U029 (solvents (for cleaning and degreasing)) in 40 CFR 711.15(b)(4)(i)(C), incorporated by reference in 35 Ill. Adm. Code 720.111.

 

F)         Both the hazardous secondary material generator and the remanufacturer must meet the following requirements:

 

i)          The generator and remanufacturer must notify USEPA Region 5 and the Agency, and update the notification every two years per 35 Ill. Adm. Code 720.142;

 

ii)         The generator and remanufacturer must develop and maintain an up-to-date remanufacturing plan that identifies the information enumerated in subsection (a)(27)(G);

 

BOARD NOTE:  The Board moved corresponding 40 CFR 261.4(a)(27)(vi)(B)(1) through (a)(27)(vi)(B)(1) to appear as subsections (a)(27)(G)(i) through (a)(27)(G)(v) to comport with codification requirements.

 

iii)        The generator and remanufacturer must maintain records of shipments and confirmations of receipts for a period of three years from the dates of the shipments;

 

iv)        The generator and remanufacturer must, prior to remanufacturing, store the hazardous spent solvents in tanks or containers that meet technical standards found in Subparts I and J, with the tanks and containers being labeled or otherwise having an immediately available record of the material being stored;

 

v)         The generator and remanufacturer must, during remanufacturing, and during storage of the hazardous secondary materials prior to remanufacturing, the remanufacturer certifies that the remanufacturing equipment, vents, and tanks are equipped with and are operating air emission controls complying with the applicable Clean Air Act regulations of 40 CFR 60, 61 and 63, incorporated by reference in 35 Ill. Adm. Code 720.111; or, absent such Clean Air Act standards for the particular operation or piece of equipment covered by the remanufacturing exclusion, are complying with the appropriate standards in Subparts AA (vents), BB (equipment) and CC (tank storage); and

 

vi)        The generator and remanufacturer must meet the requirements prohibiting speculative accumulation in Section 721.101(c)(8).

 

G)        The following information items are required elements for a remanufacturing plan.

 

i)          The name, address and USEPA ID number of the generators and the remanufacturers;

 

ii)         The types and estimated annual volumes of spent solvents to be remanufactured;

 

iii)        The processes and industry sectors that generate the spent solvents;

 

iv)        The specific uses and industry sectors for the remanufactured solvents; and

 

v)         A certification from the remanufacturer stating as follows: 

"On behalf of [insert remanufacturer facility name], I certify that this facility is a remanufacturer under pharmaceutical manufacturing (NAICS 325412), basic organic chemical manufacturing (NAICS 325199), plastics and resins manufacturing (NAICS 325211), and/or the paints and coatings manufacturing sectors (NAICS 325510), and will accept the spent solvent(s) solely for remanufacturing into commercial-grade solvent(s) that will be used for reacting, extracting, purifying, or blending chemicals (or for rinsing out the process lines associated with these functions) or for use as product ingredient(s).  I also certify that the remanufacturing equipment, vents, and tanks are equipped with and are operating air emission controls complying with the appropriate Clean Air Act regulations under 40 CFR 60, 61 or 63, or, absent such Clean Air Act standards for the particular operation or piece of equipment covered by the remanufacturing exclusion, comply with the appropriate standards in Subparts AA (vents), BB (equipment) and CC (tank storage)."

 

BOARD NOTE:  Subsections (a)(27)(G)(i) through (a)(27)(G)(v) correspond with 40 CFR 261.4(a)(27)(vi)(B)(1) through (a)(27)(vi)(B)(1), moved to this subsection (a)(27)(G) to comport with codification requirements.

 

b)         Solid Wastes That Are Not Hazardous Wastes.  The following solid wastes are not hazardous wastes:

 

1)         Household waste, including household waste that has been collected, transported, stored, treated, disposed of, recovered (e.g., refuse-derived fuel), or reused. "Household waste" means any waste material (including garbage, trash, and sanitary wastes in septic tanks) derived from households (including single and multiple residences, hotels, and motels, bunkhouses, ranger stations, crew quarters, campgrounds, picnic grounds, and day-use recreation areas).  A resource recovery facility managing municipal solid waste must not be deemed to be treating, storing, disposing of, or otherwise managing hazardous wastes for regulation under this Part, if the following describe the facility:

 

A)        The facility receives and burns only the following waste:

 

i)          Household waste (from single and multiple dwellings, hotels, motels, and other residential sources); or

 

ii)         Solid waste from commercial or industrial sources that does not contain hazardous waste; and

 

B)        The facility does not accept hazardous waste and the owner or operator of such facility has established contractual requirements or other appropriate notification or inspection procedures to assure that hazardous wastes are not received at or burned in such facility.

 

BOARD NOTE: The U.S. Supreme Court determined, in City of Chicago v. Environmental Defense Fund, Inc., 511  U.S. 328, 114 S. Ct. 1588, 128 L. Ed. 2d 302 (1994), that this exclusion and RCRA section 3001(i) (42 USC 6921(i)) do not exclude the ash from facilities covered by this subsection (b)(1) from regulation as a hazardous waste.  At 59 Fed. Reg. 29372 (June 7, 1994), USEPA granted facilities managing ash from such facilities that is determined a hazardous waste under Subpart C until December 7, 1994 to file a RCRA Part A permit application under 35 Ill. Adm. Code 703.181.  At 60 Fed. Reg. 6666 (Feb. 3, 1995), USEPA stated that it interpreted that the point at which ash becomes subject to RCRA Subtitle C regulation is when that material leaves the combustion building (including connected air pollution control equipment).

 

2)         Solid wastes generated by any of the following that are returned to the soil as fertilizers:

 

A)        The growing and harvesting of agricultural crops; or

 

B)        The raising of animals, including animal manures.

 

3)         Mining overburden returned to the mine site.

 

4)         Coal and Fossil Fuel Combustion Waste

 

A)        Fly ash waste, bottom ash waste, slag waste, and flue gas emission control waste generated primarily from combusting coal or other fossil fuels, except as provided in 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste.

 

B)        The following wastes generated primarily from processes that support combusting coal or other fossil fuels that are co-disposed with the wastes in subsection (b)(4)(A), except as provided by 35 Ill. Adm. Code 726.112 for facilities that burn or process hazardous waste:

 

i)          Coal Pile Run-Off.  For this subsection (b)(4), "coal pile run-off" means any precipitation that drains off coal piles.

 

ii)         Boiler Cleaning Solutions.  For this subsection (b)(4), "boiler cleaning solutions" means water solutions and chemical solutions used to clean the fire-side and waterside of the boiler.

 

iii)        Boiler Blowdown.  For this subsection (b)(4), "boiler blowdown" means water purged from boilers used to generate steam.

 

iv)        Process Water Treatment and Demineralizer Regeneration Wastes.  For this subsection (b)(4), "process water treatment and demineralizer regeneration wastes" means sludges, rinses, and spent resins generated from processes to remove dissolved gases, suspended solids, and dissolved chemical salts from combustion system process water.

 

v)         Cooling Tower Blowdown.  For this subsection (b)(4), "cooling tower blowdown" means water purged from a closed cycle cooling system.  Closed cycle cooling systems include cooling towers, cooling ponds, or spray canals.

 

vi)        Air Heater and Precipitator Washes.  For this subsection (b)(4), "air heater and precipitator washes" means wastes from cleaning air preheaters and electrostatic precipitators.

 

vii)       Effluents from Floor and Yard Drains and Sumps.  For this subsection (b)(4), "effluents from floor and yard drains and sumps" means wastewaters, such as wash water, collected by or from floor drains, equipment drains, and sumps located inside the power plant building; and wastewaters, such as rain run-off, collected by yard drains and sumps located outside the power plant building.

 

viii)      Wastewater Treatment Sludges.  For this subsection (b)(4), "wastewater treatment sludges" refers to sludges generated from the treatment of wastewaters specified in subsections (b)(4)(B)(i) through (b)(4)(B)(vi).

 

5)         Drilling fluids, produced waters, and other wastes associated with the exploring, developing, or producing crude oil, natural gas, or geothermal energy.

 

6)         Chromium Wastes

 

A)        Wastes that fail the test for the toxicity characteristic (Section 721.124 and Appendix B) because chromium is present or that are listed in Subpart D due to the presence of chromium, that do not fail the test for the toxicity characteristic for any other constituent or that are not listed due to the presence of any other constituent, and that do not fail the test for any other characteristic, if the waste generator shows the following:

 

i)          The chromium in the waste is exclusively (or nearly exclusively) trivalent chromium;

 

ii)         The waste is generated from an industrial process that uses trivalent chromium exclusively (or nearly exclusively) and the process does not generate hexavalent chromium; and

 

iii)        The waste is typically and frequently managed in non-oxidizing environments.

 

B)        The following are specific wastes that meet the standard in subsection (b)(6)(A) (so long as they do not fail the test for the toxicity characteristic for any other constituent and do not exhibit any other characteristic):

 

i)          Chrome (blue) trimmings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling;

 

ii)         Chrome (blue) shavings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling;

 

iii)        Buffing dust generated by the following subcategories of the leather tanning and finishing industry:  hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue;

 

iv)        Sewer screenings generated by the following subcategories of the leather tanning and finishing industry:  hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling;

 

v)         Wastewater treatment sludges generated by the following subcategories of the leather tanning and finishing industry:  hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling;

 

vi)        Wastewater treatment sludges generated by the following subcategories of the leather tanning and finishing industry:  hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, and through-the-blue;

 

vii)       Waste scrap leather from the leather tanning industry, the shoe manufacturing industry, and other leather product manufacturing industries; and

 

viii)      Wastewater treatment sludges from producing titanium dioxide pigment using chromium-bearing ores by the chloride process.

 

7)         Solid waste from extracting, beneficiating, 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 this subsection (b)(7), beneficiating ores and minerals is restricted to the following activities:  crushing; grinding; washing; dissolution; crystallization; filtration; sorting; sizing; drying; sintering; pelletizing; briquetting; calcining to remove water or carbon dioxide; roasting; autoclaving or chlorination in preparation for leaching (except if the roasting (or autoclaving or chlorination) and leaching sequence produces a final or intermediate product that does not undergo further beneficiation or processing); gravity concentration; magnetic separation; electrostatic separation; floatation; ion exchange; solvent extraction; electrowinning; precipitation; amalgamation; and heap, dump, vat tank, and in situ leaching.

 

B)        For the 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 met:

 

i)          The owner or operator processes at least 50 percent by weight normal beneficiation raw materials or normal mineral processing raw materials; and

 

ii)         The owner or operator legitimately reclaims the secondary mineral processing materials.

 

8)         Cement kiln dust waste, except as provided by 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste.

 

9)         Solid waste that consists of discarded arsenical-treated wood or wood products that fails the test for the toxicity characteristic for USEPA hazardous waste numbers D004 through D017 and that is not a hazardous waste for any other reason if the waste is generated by persons that utilize the arsenical-treated wood and wood products for these materials' intended end use.

 

10)       Petroleum-contaminated media and debris that fail the test for the toxicity characteristic of Section 721.124 (USEPA hazardous waste numbers D018 through D043 only) and that are subject to corrective action regulations under 35 Ill. Adm. Code 731.

 

11)       This subsection (b)(11) corresponds with 40 CFR 261.4(b)(11), which expired by its own terms on January 25, 1993.  This statement maintains structural parity with USEPA regulations.

 

12)       Used chlorofluorocarbon refrigerants from totally enclosed heat transfer equipment, including mobile air conditioning systems, mobile refrigeration, and commercial and industrial air conditioning and refrigeration systems, that use chlorofluorocarbons as the heat transfer fluid in a refrigeration cycle, provided the refrigerant is reclaimed for further use.

 

13)       Non-terne plated used oil filters that are not mixed with wastes listed in Subpart D, if these oil filters have been gravity hot-drained using one of the following methods:

 

A)        Puncturing the filter anti-drain back valve or the filter dome end and hot-draining;

 

B)        Hot-draining and crushing;

 

C)        Dismantling and hot-draining; or

 

D)        Any other equivalent hot-draining method that will remove used oil.

 

14)       Used oil re-refining distillation bottoms that are used as feedstock to manufacture asphalt products.

 

15)       Leachate or gas condensate collected from landfills where certain solid wastes have been disposed of, under the following circumstances:

 

A)        The following conditions must be met:

 

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) were disposed of prior to the effective date of the listing (as provided 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 (33 USC 1317(b) or 1342).

 

B)        Leachate or gas condensate derived from K169, K170, K171, K172, K176, K177, K178, or K181 waste will no longer be exempt if it is stored or managed in a surface impoundment prior to discharge. There is one exception:  if the surface impoundment is used to temporarily store leachate or gas condensate in response to an emergency situation (e.g., shutdown of wastewater treatment system), provided the impoundment has a double liner, and provided the leachate or gas condensate is removed from the impoundment and continues to be managed complying with the conditions of this subsection (b)(15) after the emergency ends.

 

16)       This subsection (b)(16) corresponds with 40 CFR 261.4(b)(16), which USEPA has marked "reserved".  This statement maintains structural parity with USEPA regulations.

 

17)       This subsection (b)(17) corresponds with 40 CFR 261.4(b)(17), which pertains exclusively to waste generated by a specific facility outside Illinois.  This statement maintains structural parity with USEPA regulations.

 

18)       Solvent-contaminated wipes, except for wipes that are hazardous waste due to the presence of trichloroethylene, that are sent for disposal are not hazardous wastes from the point of generation if the following conditions are met:

 

A)        The solvent-contaminated wipes, when accumulated, stored, and transported, are contained in non-leaking, closed containers that are labeled "Excluded Solvent-Contaminated Wipes".  The containers must be able to contain free liquids, should free liquids occur.  During accumulation, a container is considered closed when there is complete contact between the fitted lid and the rim, except when it is necessary to add or remove solvent-contaminated wipes.  When the container is full, when the solvent-contaminated wipes are no longer being accumulated, or when the container is being transported, the container must be sealed with all lids properly and securely affixed to the container and all openings tightly bound or closed sufficiently to prevent leaks and emissions;

 

B)        The solvent-contaminated wipes may be accumulated by the generator for up to 180 days from the start date of accumulation for each container prior to being sent for disposal;

 

C)        At the point of being transported for disposal, the solvent-contaminated wipes must contain no free liquids, as defined in 35 Ill. Adm. Code 720.110;

 

D)        Free liquids removed from the solvent-contaminated wipes or from the container holding the wipes must be managed according to the applicable regulations found in this Part and 35 Ill. Adm. Code 720, 722 through 728, and 733;

 

E)        Generators must maintain at their site the following documentation:

 

i)          The name and address of the landfill or combustor that is receiving the solvent-contaminated wipes;

 

ii)         The documentation that the 180-day accumulation time limit in 35 Ill. Adm. Code 721.104(b)(18)(B) is being met; and

 

iii)        A description of the process the generator is using to ensure that the solvent-contaminated wipes contain no free liquids at the point of being transported for disposal; and

 

F)         The solvent-contaminated wipes are sent for disposal at one of the following facilities:

 

i)          A municipal solid waste landfill regulated under RCRA Subtitle D regulations:  35 Ill. Adm. Code 810 through 815, including the landfill design criteria of 35 Ill. Adm. Code 811.303 through 811.309, 811.315 through 811.317, and Subpart E of 35 Ill. Adm. Code 811 or 35 Ill. Adm. Code 814.302 and 814.402; 40 CFR 258, including the landfill design criteria of 40 CFR 258.40; or equivalent regulations of a sister state that USEPA has approved under 42 USC 6943 and 6947; or

 

ii)         A hazardous waste landfill regulated under RCRA Subtitle C regulations:  35 Ill. Adm. Code 724 or 725; 40 CFR 264 or 265; or equivalent regulations of a sister state that USEPA has approved under 42 USC 6926; or

 

iii)        A municipal waste combustor or other combustion facility regulated under section 129 of the Clean Air Act (42 USC 7429) or equivalent Illinois or sister-state regulations approved by USEPA under 42 USC 7429; or

 

iv)        A hazardous waste combustor, boiler, or industrial furnace regulated under RCRA Subtitle C regulations:  35 Ill. Adm. Code 724 or 725 or Subpart H of 35 Ill. Adm. Code 726; 40 CFR 264 or 265 or subpart H of 40 CFR 266; or equivalent regulations of a sister state that USEPA has approved under 42 USC 6926.

 

c)         Hazardous wastes that are exempted from certain regulations. A hazardous waste that is generated in a product or raw material storage tank, a product or raw material transport vehicle or vessel, a product or raw material pipeline, or in a manufacturing process unit, or an associated non-waste-treatment manufacturing unit, is not subject to regulation under 35 Ill. Adm. Code 702, 703, and 722 through 728 or to the notification requirements of section 3010 of RCRA (42 USC 6930) until it exits the unit in which it was generated, unless the unit is a surface impoundment, or unless the hazardous waste remains in the unit more than 90 days after the unit ceases to be operated for manufacturing or for storage or transporting product or raw materials.

 

d)         Samples

 

1)         Except as provided in subsections (d)(2) and (d)(4), a sample of solid waste or a sample of water, soil, or air that is collected solely for 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 meets one of the following conditions:

 

A)        The sample is being transported to a laboratory for testing;

 

B)        The sample is being transported back to the sample collector after testing;

 

C)        The sample is being stored by the sample collector before transport to a laboratory for testing;

 

D)        The sample is being stored in a laboratory before testing;

 

E)        The sample is being stored in a laboratory for testing but before it is returned to the sample collector; or

 

F)         The sample is being stored temporarily in the laboratory after testing for a specific purpose (for example, until conclusion of a court case or enforcement action if further testing of the sample may be necessary).

 

2)         To qualify for the exemption in subsection (d)(1)(A) or (d)(1)(B), a sample collector shipping samples to a laboratory and a laboratory returning samples to a sample collector must do the following:

 

A)        Comply with USDOT, U.S. Postal Service (USPS), or any other applicable shipping requirements; or

 

B)        Comply with the following requirements if the sample collector determines that USDOT, USPS, or other shipping requirements do not apply to the shipment of the sample:

 

i)          Assure that the following information accompanies the sample:  The sample collector's name, mailing address, and telephone number; the laboratory's name, mailing address, and telephone number; the quantity of the sample; the date of the shipment; and a description of the sample; and

 

ii)         Package the sample so that it does not leak, spill, or vaporize from its packaging.

 

3)         This exemption does not apply if the laboratory determines that the waste is hazardous, but the laboratory is no longer meeting any of the conditions stated in subsection (d)(1).

 

4)         To qualify for the exemption in subsections (d)(1)(A) and (d)(1)(B), the mass of a sample that will be exported to a foreign laboratory or that will be imported to a U.S. laboratory from a foreign source must additionally not exceed 25 kg.

 

e)         Treatability Study Samples

 

1)         Except as provided in subsections (e)(2) and (e)(4), a person that generates or collects samples for conducting treatability studies, as defined in 35 Ill. Adm. Code 720.110, are not subject to any requirement of 35 Ill. Adm. Code 721 through 723 or to the notification requirements of section 3010 of RCRA (42 USC 6930).  Nor are such samples included in the quantity determinations of 35 Ill. Adm. Code 722.114 and 722.116 when:

 

A)        The sample is being collected and prepared for transportation by the generator or sample collector;

 

B)        The sample is being accumulated or stored by the generator or sample collector prior to transportation to a laboratory or testing facility; or

 

C)        The sample is being transported to the laboratory or testing facility for conducting a treatability study.

 

2)         The exemption in subsection (e)(1) is applicable to samples of hazardous waste being collected and shipped for conducting treatability studies provided that the following conditions are met:

 

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 subsection (e)(2)(C)(i) or (e)(2)(C)(ii) are met.

 

i)          Transporting each sample shipment complies with USDOT, USPS, or any other applicable shipping requirements; or

 

ii)         If the USDOT, USPS, or other shipping requirements do not apply to the shipment of the sample, the following information must accompany the sample:  The name, mailing address, and telephone number of the originator of the sample; the name, address, and telephone number of the facility that will perform the treatability study; the quantity of the sample; the date of the shipment; and, a description of the sample, including its USEPA hazardous waste number;

 

D)        The sample is shipped to a laboratory or testing facility that is exempt under subsection (f), or has an appropriate RCRA permit or interim status;

 

E)        The generator or sample collector maintains the following records for a period ending three years after completing the treatability study:

 

i)          Copies of the shipping documents;

 

ii)         A copy of the contract with the facility conducting the treatability study; and

 

iii)        Documentation showing the following:  The amount of waste shipped under this exemption; the name, address, and USEPA identification number of the laboratory or testing facility that received the waste; the date the shipment was made; and whether or not unused samples and residues were returned to the generator; and

 

F)         The generator reports the information required in subsection (e)(2)(E)(iii) in its report under 35 Ill. Adm. Code 722.141.

 

3)         The Agency may grant requests on a case-by-case basis for up to an additional two years for treatability studies involving bioremediation.  The Agency may grant requests, on a case-by-case basis, for quantity limits in excess of those specified in subsections (e)(2)(A), (e)(2)(B), and (f)(4), for up to an additional 5,000 kg of media contaminated with non-acute hazardous waste, 500 kg of non-acute hazardous waste, 2,500 kg of media contaminated with acute hazardous waste, and 1 kg of acute hazardous waste under the circumstances in either subsection (e)(3)(A) or (e)(3)(B), subject to the limitations of subsection (e)(3)(C):

 

A)        In response to requests for authorization to ship, store, and conduct further treatability studies on additional quantities in advance of commencing treatability studies. Factors to be considered in reviewing such requests include  the nature of the technology, the type of process (e.g., batch versus continuous), the size of the unit undergoing testing (particularly in relation to scale-up considerations), the time or quantity of material required to reach steady-state operating conditions, or test design considerations, such as mass balance calculations.

 

B)        In response to requests for authorization to ship, store, and conduct treatability studies on additional quantities after initiating or completing 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 evaluating an ongoing treatability study to determine final specifications for treatment.

 

C)        The additional quantities and timeframes allowed in subsections (e)(3)(A) and (e)(3)(B) are subject to all the provisions in subsections (e)(1) and (e)(2)(B) through (e)(2)(F).  The generator or sample collector must apply to the Agency and provide in writing the following information:

 

i)          The reason why the generator or sample collector requires additional time or quantity of sample for the treatability study evaluation and the additional time or quantity needed;

 

ii)         Documentation accounting for all samples of hazardous waste from the waste stream that have been sent for or undergone treatability studies, including the date each previous sample from the waste stream was shipped, the quantity of each previous shipment, the laboratory or testing facility to which it was shipped, what treatability study processes were conducted on each sample shipped, and the available results of each treatability study;

 

iii)        A description of the technical modifications or change in specifications that will be evaluated and the expected results;

 

iv)        If such further study is being required due to equipment or mechanical failure, the applicant must include information regarding the reason for the failure or breakdown and also include what procedures or equipment improvements have been made to protect against further breakdowns; and

 

v)         Such other information as the Agency determines is necessary.

 

4)         To qualify for the exemption in subsection (e)(1)(A), the mass of a sample that will be exported to a foreign laboratory or testing facility, or that will be imported to a U.S. laboratory or testing facility from a foreign source must additionally not exceed 25 kg.

 

5)         Final Agency determinations under this subsection (e) may be appealed to the Board.

 

f)         Samples undergoing treatability studies at laboratories or testing facilities.  Samples undergoing treatability studies and the laboratory or testing facility conducting such treatability studies (to the extent such facilities are not otherwise subject to RCRA requirements) are not subject to any requirement of this Part, or of 35 Ill. Adm. Code 702, 703, 722 through 726, and 728 or to the notification requirements of section 3010 of RCRA (42 USC 6930), provided that the owner or operator complies with subsections (f)(1) through (f)(11).  A mobile treatment unit may qualify as a testing facility subject to subsections (f)(1) through (f)(11). Where a group of mobile treatment units are located at the same site, the limitations specified in subsections (f)(1) through (f)(11) apply to the entire group of mobile treatment units collectively as if the group were one mobile treatment unit.

 

1)         No less than 45 days before conducting treatability studies, the facility notifies the Agency in writing that it intends to conduct treatability studies under this subsection (f).

 

2)         The laboratory or testing facility conducting the treatability study has a USEPA identification number.

 

3)         No more than a total of 10,000 kg of "as received" media contaminated with non-acute hazardous waste, 2,500 kg of media contaminated with acute hazardous waste, or 250 kg of other "as received" hazardous waste is subject to initiating 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 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 completing each study that show complying with the treatment rate limits and the storage time and quantity limits.  The following specific information must be included for each treatability study conducted:

 

A)        The name, address, and USEPA identification number of the generator or sample collector of each waste sample;

 

B)        The date the shipment was received;

 

C)        The quantity of waste accepted;

 

D)        The quantity of "as received" waste in storage each day;

 

E)        The date the treatment study was initiated and the amount of "as received" waste introduced to treatment each day;

 

F)         The date the treatability study was concluded;

 

G)        The date any unused sample or residues generated from the treatability study were returned to the generator or sample collector or, if sent to a designated facility, the name of the facility and the USEPA identification number.

 

8)         The facility keeps, on-site, a copy of the treatability study contract and all shipping papers associated with the transport of treatability study samples to and from the facility for a period ending three years from the completion date of each treatability study.

 

9)         The facility prepares and submits a report to the Agency, by March 15 of each year, that includes the following information for the previous calendar year:

 

A)        The name, address, and USEPA identification number of the facility conducting the treatability studies;

 

B)        The types (by process) of treatability studies conducted;

 

C)        The names and addresses of persons for whom studies have been conducted (including their USEPA identification numbers);

 

D)        The total quantity of waste in storage each day;

 

E)        The quantity and types of waste subjected to treatability studies;

 

F)         When each treatability study was conducted; and

 

G)        The final disposition of residues and unused sample from each treatability study.

 

10)       The facility determines whether any unused sample or residues generated by the treatability study are hazardous waste under Section 721.103 and, if so, are subject to 35 Ill. Adm. Code 702, 703, and 721 through 728, unless the residues and unused samples are returned to the sample originator under the exemption of subsection (e).

 

11)       The facility notifies the Agency by letter when the facility is no longer planning to conduct any treatability studies at the site.

 

g)         Dredged Material That Is Not a Hazardous Waste.  Dredged material that is subject to 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 this subsection (g), the following definitions apply:

 

"Dredged material" has the meaning ascribed it in 40 CFR 232.2 (Definitions), incorporated by reference in 35 Ill. Adm. Code 720.111(b).

 

"Permit" means any of the following:

 

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

 

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

 

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

 

h)         Carbon Dioxide Stream Injected for Geologic Sequestration.  Carbon dioxide streams that are captured and transported for injecting into an underground injection well subject to the requirements for Class VI carbon sequestration injection wells, including the requirements in 35 Ill. Adm. Code 704 and 730, are not a hazardous waste, if the following conditions are met:

 

1)         Transporting the carbon dioxide stream must comply with U.S. Department of Transportation requirements, including the pipeline safety laws (chapter 601 of subtitle VIII of 49 USC, incorporated by reference in 35 Ill. Adm. Code 720.111) and regulations (49 CFR 190 through 199, incorporated by reference in 35 Ill. Adm. Code 720.111) of the U.S. Department of Transportation, and pipeline safety regulations adopted and administered by a state authority under a certification under 49 USC 60105, incorporated by reference in 35 Ill. Adm. Code 720.111, and 49 CFR 171 through 180, incorporated by reference in 35 Ill. Adm. Code 720.111, as applicable;

 

BOARD NOTE:  The parenthetical language relating to pipeline transportation does not preclude transportation by air, water, highway, or rail that complies with U.S. Department of Transportation regulations at 49 CFR 171 through 180.  For this reason, the Board has added citations of those regulations.

 

2)         Injecting the carbon dioxide stream must comply with the applicable requirements for Class VI carbon sequestration injection wells, including the applicable requirements in 35 Ill. Adm. Code 704 and 730;

 

3)         No hazardous wastes may be mixed with, or otherwise co-injected with, the carbon dioxide stream; and

 

4)         Required Certifications

 

A)        Any generator of a carbon dioxide stream, that claims that a carbon dioxide stream is excluded under this subsection (h), must have an authorized representative (as defined in 35 Ill. Adm. Code 720.110) sign a certification statement worded as follows:

 

"I certify under penalty of law that the carbon dioxide stream that I am claiming to be excluded under 35 Ill. Adm. Code 721.104(h) has not been mixed with hazardous wastes, and I have transported the carbon dioxide stream complying with (or have contracted with a pipeline operator or transporter to transport the carbon dioxide stream complying with) U.S. Department of Transportation requirements, including the pipeline safety laws (49 USC 60101 et seq.) and regulations (49 CFR Parts 190 through 199) of the U.S. Department of Transportation, and the pipeline safety regulations adopted and administered by a state authority pursuant to a certification under 49 USC 60105, as applicable, for injection into a well subject to the requirements for the Class VI Underground Injection Control Program of the federal Safe Drinking Water Act (42 USC 300f et seq.)."

 

B)        Any Class VI carbon sequestration injection well owner or operator, who claims that a carbon dioxide stream is excluded under this subsection (h), must have an authorized representative (as defined in 35 Ill. Adm. Code 720.110) sign a certification statement worded as follows:

 

"I certify under penalty of law that the carbon dioxide stream that I am claiming to be excluded under 35 Ill. Adm. Code 721.104(h) has not been mixed with, or otherwise co-injected with, hazardous waste at the UIC Class VI permitted facility, and that injecting the carbon dioxide stream complies with the applicable requirements for UIC Class VI wells, including the applicable requirements in 35 Ill. Adm. Code 704 and 730."

 

C)        The signed certification statement must be kept on-site, for no less than three years, and must be made available within 72 hours after a written request from the Agency or USEPA, or their designee.  The signed certification statement must be renewed every year that the exclusion is claimed, by having an authorized representative (as defined in 35 Ill. Adm. Code 720.110) annually prepare and sign a new copy of the certification statement within one year after the date of the previous statement.  The signed certification statement must also be readily accessible on the facility's publicly available website (if such website exists) as a public notification with the title of "Carbon Dioxide Stream Certification" at the time the exclusion is claimed.

 

i)          This subsection corresponds with 40 CFR 261.4(i), which USEPA marked "Reserved".  This statement maintains structural consistency with the federal regulation.

 

j)          Airbag Waste

 

1)         At the airbag waste handler or during transport to an airbag waste collection facility or designated facility, airbag waste is not subject to regulation under 35 Ill. Adm. Code 702, 703, and 722 through 728 and is not subject to the notification requirements of section 3010 of RCRA provided that the airbag waste handler or transporter meets the following conditions:

 

A)        The airbag waste handler or transporter accumulates the airbag waste in a quantity of no more than 250 airbag modules or airbag inflators for no longer than 180 days;

 

B)        The airbag waste handler or transporter packages the airbag waste in a container designed to address the risk posed by the airbag waste and labeled "Airbag Waste – Do Not Reuse";

 

C)        The airbag waste handler or transporter sends the airbag waste directly to either of the following facilities:

 

i)          An airbag waste collection facility in the United States that is under the control of a vehicle manufacturer or its authorized representative or that is under the control of a person authorized to administer a remedy program in response to a vehicle safety recall under 49 USC 30120; or

 

ii)         A designated facility, as defined in 35 Ill. Adm. Code 720.110;

 

D)        The transport of the airbag waste complies with all applicable USDOT regulations in 49 CFR 171 through 180 during transit; and

 

E)        The airbag waste handler maintains at the handler facility, for at least three years, records of each off-site shipment of airbag waste and each confirmation of receipt from the receiving facility.  For each shipment, these records must, at a minimum, contain the name of the transporter, the date of the shipment, the name and address of the receiving facility, and the type and quantity of airbag waste (i.e., airbag modules or airbag inflators) in the shipment.  A confirmation of receipt must include the name and address of the receiving facility, the type and quantity of the airbag waste (i.e., airbag modules and airbag inflators) received, and the date when the airbag waste collection facility received the airbag waste.  The airbag waste handler must make shipping records and confirmations of receipt available for inspection and may meet this requirement using routine business records (e.g., electronic or paper financial records, bills of lading, copies of USDOT shipping papers, electronic confirmations of receipt, etc.).

 

2)         Once the airbag waste arrives at an airbag waste collection facility or designated facility, it becomes subject to all applicable hazardous waste regulations.  The facility receiving airbag waste is considered the hazardous waste generator for the hazardous waste regulations and must comply with 35 Ill. Adm. Code 722.

 

3)         Reuse in vehicles of defective airbag modules or defective airbag inflators that are subject to a recall under 49 USC 30120 is considered sham recycling and prohibited under 35 Ill. Adm. Code 721.102(g).

 

BOARD NOTE:  This precludes any possibility that reuse qualifies for recycling-based exclusion from the definition of solid waste.  Federal law prohibits selling defective recalled motor vehicle equipment if it may reasonably be used for its original purpose.  (See 42 USC 30120(j).)

 

(Source:  Amended at 48 Ill. Reg. 16813, effective November 7, 2024)

 

Section 721.105  Special Requirements for Hazardous Waste Generated by Small Quantity Generators (Repealed)

 

(Source:  Repealed at 42 Ill. Reg. 21673, effective November 19, 2018)

 

Section 721.106  Requirements for Recyclable Materials

 

a)         Recyclable Materials

 

1)         Hazardous wastes that are recycled are subject to the requirements for generators, transporters, and storage facilities of subsections (b) and (c), except for the materials listed in subsections (a)(2) and (a)(3).  Hazardous wastes that are recycled will be known as "recyclable materials".

 

2)         The following recyclable materials are not subject to this Section but are regulated under Subparts C through H of 35 Ill. Adm. Code 726 and all applicable provisions in 35 Ill. Adm. Code 702, 703, and 728.

 

A)        Recyclable materials used in a manner constituting disposal (see Subpart C of 35 Ill. Adm. Code 726);

 

B)        Hazardous wastes burned (as defined in 35 Ill. Adm. Code 726.200(a)) in boilers and industrial furnaces that are not regulated under Subpart O of 35 Ill. Adm. Code 724 or Subpart O (see Subpart H of 35 Ill. Adm. Code 726);

 

C)        Recyclable materials from which precious metals are reclaimed (see Subpart F of 35 Ill. Adm. Code 726); and

 

D)        Spent lead-acid batteries that are being reclaimed (see Subpart G of 35 Ill. Adm. Code 726).

 

3)         The following recyclable materials are not subject to regulation under 35 Ill. Adm. Code 722 through 728, or 702 and 703 and are not subject to the notification requirements of section 3010 of RCRA (42 USC 6930):

 

A)        Industrial ethyl alcohol that is reclaimed except that exports and imports of these recyclable material must comply with 40 CFR 262, subpart H.

 

B)        Scrap metal that is not excluded under Section 721.104(a)(13);

 

C)        Fuels produced from the refining of oil-bearing hazardous wastes along with normal process streams at a petroleum refining facility if these wastes result from normal petroleum refining, production, and transportation practices (this exemption does not apply to fuels produced from oil recovered from oil-bearing hazardous waste if the recovered oil is already excluded under Section 721.104(a)(12));

 

D)        Petroleum Refining Wastes

 

i)          Hazardous waste fuel produced from oil-bearing hazardous wastes from petroleum refining, production, or transportation practices or produced from oil reclaimed from the hazardous wastes, if these hazardous wastes are reintroduced into a process that does not use distillation or does not produce products from crude oil, so long as the resulting fuel meets the used oil specification under 35 Ill. Adm. Code 739.111 and so long as no other hazardous wastes are used to produce the hazardous waste fuel;

 

ii)         Hazardous waste fuel produced from oil-bearing hazardous waste from petroleum refining production, and transportation practices, if the hazardous wastes are reintroduced into a refining process after a point at which contaminants are removed, so long as the fuel meets the used oil fuel specification under 35 Ill. Adm. Code 739.111; and

 

iii)        Oil reclaimed from oil-bearing hazardous wastes from petroleum refining, production, and transportation practices, which reclaimed oil is burned as a fuel without reintroduction to a refining process, so long as the reclaimed oil meets the used oil fuel specification under 35 Ill. Adm. Code 739.111.

 

4)         Used oil that is recycled and is also a hazardous waste solely because it exhibits a hazardous characteristic is not subject to 35 Ill. Adm. Code 720 through 728, but it is regulated under 35 Ill. Adm. Code 739.  Used oil that is recycled includes any used oil that is reused for any purpose following its original use (including the purpose for which the oil was originally used).  This term includes oil that is re-refined, reclaimed, burned for energy recovery, or reprocessed.

 

5)         Hazardous waste that is exported or imported for recovery is subject to Subpart H of 35 Ill. Adm. Code 722.

 

b)         Generators and transporters of recyclable materials are subject to the applicable requirements of 35 Ill. Adm. Code 722 and 723 and the notification requirements under section 3010 of RCRA (42 USC 6930), except as provided in subsection (a).

 

c)         Storage and Recycling

 

1)         Owners or operators of facilities that store recyclable materials before they are recycled are regulated under all applicable provisions of Subparts A through L, AA through DD of 35 Ill. Adm. Code 724 and 725 and 35 Ill. Adm. Code 702, 703, 705, 726, 727, and 728; and the notification requirement under section 3010 of RCRA (42 USC 6930), except as provided in subsection (a).  (The recycling process itself is exempt from regulation, except as provided in subsection (d).)

 

2)         Owners or operators of facilities that recycle recyclable materials without storing them before they are recycled are subject to the following requirements, except as provided in subsection (a):

 

A)        Notification requirements under section 3010 of RCRA (42 USC 6930);

 

B)        35 Ill. Adm. Code 725.171 and 725.172 (dealing with the use of the manifest and manifest discrepancies);

 

C)        Subsection (d); and

 

D)        35 Ill. Adm. Code 725.175 (annual reporting requirements).

 

d)         Owners or operators of facilities required to have a RCRA permit under 35 Ill. Adm. Code 703 with hazardous waste management units that recycle hazardous wastes are subject to Subparts AA and BB of 35 Ill. Adm. Code 724 or 725 or 35 Ill. Adm. Code 267.

 

(Source:  Amended at 48 Ill. Reg. 16813, effective November 7, 2024)

 

Section 721.107  Residues of Hazardous Waste in Empty Containers

 

a)         Applicability of rules.

 

1)         Any hazardous waste remaining in either an empty container or an inner liner removed from an empty container, as defined in subsection (b), is not subject to regulation under 35 Ill. Adm. Code 702, 703, or 721 through 728, or to the notification requirements of Section 3010 of the Resource Conservation and Recovery Act.

 

2)         Any hazardous waste in either a container that is not empty or an inner liner that is removed from a container that is not empty, as defined in subsection (b), is subject to regulations under 35 Ill. Adm. Code 702, 703, and 721 through 728 and to the notification requirements of Section 3010 of the Resource Conservation and Recovery Act.

 

b)         Definition of "empty":

 

1)         A container or an inner liner removed from a container that has held any hazardous waste, except a waste that is a compressed gas or that is identified as an acute hazardous waste listed in Section 721.131 or 721.133(e), is empty if the conditions of subsections (b)(1)(A) and (b)(1)(B) exist, subject to the limitations of subsection (b)(1)(C):

 

A)        All wastes have been removed that can be removed using the practices commonly employed to remove materials from that type of container, e.g., pouring, pumping, and aspirating, and

 

B)        No more than 2.5 centimeters (one inch) of residue remain on the bottom of the container or inner liner, or

 

C)        Weight Limits

 

i)          No more than three percent by weight of the total capacity of the container remains in the container or inner liner if the container is less than or equal to 119 gallons (450 liters) in size; or

 

ii)         No more than 0.3 percent by weight of the total capacity of the container remains in the container or inner liner if the container is greater than 119 gallons (450 liters) in size.

 

2)         A container that has held a hazardous waste that is a compressed gas is empty when the pressure in the container approaches ambient atmospheric pressure.

 

3)         A container or an inner liner removed from a container that has held an acute hazardous waste listed in Section 721.131 or 721.133(e) is empty if any of the following occurs:

 

A)        The container or inner liner has been triple rinsed using a solvent capable of removing the commercial chemical product or manufacturing chemical intermediate;

 

B)        The container or inner liner has been cleaned by another method that has been shown in the scientific literature, or by tests conducted by the generator, to achieve equivalent removal; or

 

C)        In the case of a container, the inner liner that prevented contact of the commercial chemical product or manufacturing chemical intermediate with the container has been removed.

 

c)         A container that held hazardous waste pharmaceuticals is determined empty under 35 Ill. Adm. Code 726.607, in lieu of under this Section, except as provided by 35 Ill. Adm. Code 726.607(c) and (d).

 

(Source:  Amended at 44 Ill. Reg. 15142, effective September 3, 2020)

 

Section 721.108  PCB Wastes Regulated under TSCA

 

Polychlorinatedbiphenyl-(PCB-)containing dielectric fluid and electric equipment containing such fluid are exempt from regulation under 35 Ill. Adm. Code 702, 703, and 721 through 728, and from the notification requirements of Section 3010 of RCRA (42 USC 6930) if the following conditions are fulfilled with regard to the fluid:

 

a)         The fluid is authorized for use and regulated pursuant to federal 40 CFR 761; and

 

b)         The fluid is hazardous only because it fails the test for toxicity characteristic (hazardous waste numbers D018 through D043 only).

 

(Source:  Amended at 42 Ill. Reg. 21673, effective November 19, 2018)

 

Section 721.109  Requirements for Universal Waste

 

The wastes listed in this Section are exempt from regulation under 35 Ill. Adm. Code 702, 703, 722 through 726, and 728, except as specified in 35 Ill. Adm. Code 733, and are therefore not fully regulated as hazardous waste.  The following wastes are subject to regulation under 35 Ill. Adm. Code 733:

 

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

 

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

 

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

 

d)         Lamps, as described in 35 Ill. Adm. Code 733.105; and

 

e)         Aerosol cans, as described in 35 Ill. Adm. Code 733.106.

 

(Source:  Amended at 44 Ill. Reg. 15142, effective September 3, 2020)

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

 

Section 721.110  Criteria for Identifying the Characteristics of Hazardous Waste

 

a)         USEPA stated in corresponding federal 40 CFR 261.10 that it identifies and defines a characteristic of hazardous waste in Subpart C only upon determining the following:

 

1)         That a solid waste that exhibits the characteristic may do either of the following:

 

A)        It could cause, or significantly contribute to, an increase in mortality or an increase in serious irreversible, or incapacitating reversible, illness; or

 

B)        It could pose a substantial present or potential hazard to human health or the environment when it is improperly treated, stored, transported, disposed of or otherwise managed; and

 

2)         That the characteristic can be as follows:

 

A)        It can be measured by an available standardized test method that is reasonable within the capability of generators of solid waste or private sector laboratories that are available to serve generators of solid waste; or

 

B)        It can reasonably be detected by generators of solid waste through their knowledge of their waste.

 

b)         Delisting procedures are contained in 35 Ill. Adm. Code 720.122.

 

(Source:  Amended at 42 Ill. Reg. 21673, effective November 19, 2018)

 

Section 721.111  Criteria for Listing Hazardous Waste

 

a)         USEPA stated in corresponding federal 40 CFR 261.11 that it lists a solid waste as a hazardous waste only upon determining that the solid waste meets one of the following criteria:

 

1)         The solid waste exhibits any of the characteristics of hazardous waste identified in Subpart C; or

 

2)         Acute hazardous waste.  The solid waste has been found to be fatal to humans in low doses or, in the absence of data on human toxicity, it has been shown in studies to have an oral LD 50 toxicity (rat) of less than 50 mg/kg, an inhalation LC 50 toxicity (rat) of less than 2 mg/ℓ, or a dermal LD 50 toxicity (rabbit) of less than 200 mg/kg or is otherwise capable of causing or significantly contributing to an increase in serious irreversible or incapacitating reversible, illness.

 

BOARD NOTE:  Waste listed under subsection (a)(2) are designated Acute Hazardous Waste.

 

3)         Toxic Waste.  The solid waste contains any of the toxic constituents listed in Appendix H and, after considering the following factors, USEPA concludes that the waste is capable of posing a substantial present or potential hazard to human health or the environment when improperly treated, stored, transported, or disposed of, or otherwise managed:

 

BOARD NOTE:  Substances are listed in Appendix H only if they have been shown in scientific studies to have toxic, carcinogenic, mutagenic, or teratogenic effects on humans or other life forms.

 

A)        The nature of the toxicity presented by the constituent;

 

B)        The concentration of the constituent in the waste;

 

C)        The potential of the constituent or any toxic degradation product of the constituent to migrate from the waste into the environment under the types of improper management considered in subsection (a)(3)(G);

 

D)        The persistence of the constituent or any toxic degradation product of the constituent;

 

E)        The potential for the constituent or any toxic degradation product of the constituent to degrade into nonharmful constituents and the rate of degradation;

 

F)         The degree to which the constituent or any degradation product of the constituent bioaccumulates in ecosystems;

 

G)        The plausible types of improper management to which the waste could be subjected;

 

H)        The quantities of the waste generated at individual generator sites or on a regional or national basis;

 

I)         The nature and severity of the human health and environmental damage that has occurred because of the improper management of the wastes containing the constituent;

 

J)         Action taken by other governmental agencies or regulatory programs based on the health or environmental hazard posed by the waste or waste constituent; and

 

K)        Other factors as may be appropriate.

 

BOARD NOTE:  Wastes listed under subsection (a)(3) are designated toxic wastes.

 

b)         USEPA stated in corresponding federal 40 CFR 261.11(b) that it may list classes or types of solid waste as hazardous waste if USEPA has reason to believe that individual wastes, within the class or type of waste, typically or frequently are hazardous under the definition of hazardous waste found in section 1004(5) of RCRA (42 USC 6904(5)).

 

(Source:  Amended at 48 Ill. Reg. 16813, effective November 7, 2024)

SUBPART C: CHARACTERISTICS OF HAZARDOUS WASTE

 

Section 721.120  General

 

a)         A solid waste, as defined in Section 721.102, that is not excluded from regulation as a hazardous waste under Section 721.104(b), is a hazardous waste if it exhibits any of the characteristics identified in this Subpart C.

 

BOARD NOTE:  35 Ill. Adm. Code 722.111 states the generator's responsibility to determine whether the generator's waste exhibits one or more characteristics identified in this Subpart C.

 

b)         A hazardous waste that is identified by a characteristic in this Subpart C is assigned every USEPA hazardous waste number that is applicable as specified in this Subpart C. This number must be used in complying with the notification requirements of Section 3010 of RCRA (42 U.S.C. 6930) and all applicable recordkeeping and reporting requirements under 35 Ill. Adm. Code 702, 703, and 722 through 728.

 

c)         For this Subpart C, a sample obtained using any of the applicable sampling methods specified in Appendix A is a representative sample within the meaning of 35 Ill. Adm. Code 720.

 

BOARD NOTE:  Since the Appendix A sampling methods are not being formally adopted, a person who desires to employ an alternative sampling method is not required to demonstrate the equivalency of the person's method under the procedures set forth in 35 Ill. Adm. Code 720.121.

 

(Source:  Amended at 48 Ill. Reg. 9827, effective June 20, 2024)

 

Section 721.121  Characteristic of Ignitability

 

a)         A solid waste exhibits the characteristic of ignitability if a representative sample of the waste has any of the following properties:

 

1)         It is a liquid, other than a solution containing less than 24 percent alcohol by volume, and at least 50 percent water by weight, that has a flash point less than 60°C (140°F), as determined by one of the following ASTM standards:  D 93-79, D 93-80, D 3278-78, D 8174-18, or D 8175-18, each incorporated by reference in 35 Ill. Adm. Code 720.111(a), as specified in SW-846 Test Methods 1010B or 1020C, each incorporated by reference in 35 Ill. Adm. Code 720.111(a).

 

2)         It is not a liquid and is capable, under standard temperature and pressure, of causing fire through friction, absorbing moisture, or spontaneous chemical changes and, when ignited, burns so vigorously and persistently that it creates a hazard.

 

3)         It is an ignitable compressed gas.

 

A)        The term "compressed gas" designates any material or mixture having in the container an absolute pressure exceeding 40 p.s.i. at 70 °F or, regardless of the pressure at 70 °F, having an absolute pressure exceeding 104 p.s.i. at 130 °F.  Alternatively, the term "compressed gas" designates any liquid flammable material having a vapor pressure exceeding 40 p.s.i. absolute at 100 °F, as determined by ASTM D 323.

 

B)        A compressed gas is characterized as ignitable if any one of the following occurs:

 

i)          Either a mixture of 13 percent or less (by volume) with air forms a flammable mixture or the flammable range with air is wider than 12 percent regardless of the lower limit.  These limits must be determined at atmospheric temperature and pressure.  The method of sampling and test procedure must be ASTM E 681-85, incorporated by reference in 35 Ill. Adm. Code 720.111, or other equivalent methods approved by the Associate Administrator, Pipeline and Hazardous Materials Safety Administration, U.S. Department of Transportation.

 

ii)         It is determined to be flammable or extremely flammable using 49 CFR 173.115(l), incorporated by reference in 35 Ill. Adm. Code 720.111.

 

4)         It is an oxidizer, as defined in 49 CFR 173.127 (Class 5, Division 5.1 Definition and Assignment of Packaging Groups), incorporated by reference in 35 Ill. Adm. Code 720.111(b).

 

A)        An organic compound containing the bivalent -O-O- structure and which may be considered a derivative of hydrogen peroxide where one or more of the hydrogen atoms have been replaced by organic radicals must be classed as an organic peroxide unless:

 

i)          The material is a Division 1.1, 1.2, or 1.3 explosive, as defined in 40 CFR § 261.23(a)(8), in which case it must be classed as an explosive;

 

ii)         Offering the material for transportation is forbidden under 49 CFR 172.101 and 49 CFR 173.21;

 

iii)        The predominant hazard of the material containing an organic peroxide is other than that of an organic peroxide; or

 

iv)        According to data on file with the Pipeline and Hazardous Materials Safety Administration in the U.S. Department of Transportation, it has been determined that the material does not present a hazard in transportation.

 

b)         A solid waste that exhibits the characteristic of ignitability has the USEPA hazardous waste number of D001.

 

(Source:  Amended at 48 Ill. Reg. 9827, effective June 20, 2024)

 

Section 721.122  Characteristic of Corrosivity

 

a)         A solid waste exhibits the characteristic of corrosivity if a representative sample of the waste has either of the following properties:

 

1)         It is aqueous and has a pH less than or equal to 2 or greater than or equal to 12.5, as determined by a pH meter using Method 9040C (pH Electrometric Measurement) in "Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods", USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

 

2)         It is a liquid and corrodes steel (SAE 1020) at a rate greater than 6.35 mm (0.250 inch) per year at a test temperature of  55 °C (130 °F), as determined by Method 1110A (Corrosivity Toward Steel) in "Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods", USEPA publication number EPA-530/SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111(a).

 

BOARD NOTE:  The corrosivity characteristic determination currently does not apply to non-liquid wastes, as discussed by USEPA at 45 Fed. Reg. 33109, May 19, 1980 and at 55 Fed. Reg. 22549, June 1, 1990.

 

b)         A solid waste that exhibits the characteristic of corrosivity has the USEPA hazardous waste number of D002.

 

(Source:  Amended at 44 Ill. Reg. 15142, effective September 3, 2020)

 

Section 721.123  Characteristic of Reactivity

 

a)         A solid waste exhibits the characteristic of reactivity if a representative sample of the waste has any of the following properties:

 

1)         It is normally unstable and readily undergoes violent change without detonating.

 

2)         It reacts violently with water.

 

3)         It forms potentially explosive mixtures with water.

 

4)         When mixed with water, it generates toxic gases, vapors, or fumes in a quantity sufficient to present a danger to human health or the environment.

 

5)         It is a cyanide or sulfide bearing waste which, when exposed to pH conditions between 2 and 12.5 can generate toxic gases, vapors, or fumes in a quantity sufficient to present a danger to human health or the environment.

 

6)         It is capable of detonation or explosive reaction if it is subjected to a strong initiating source or if heated under confinement.

 

7)         It is readily capable of detonation or explosive decomposition or reaction at standard temperature and pressure.

 

8)         It is a forbidden explosive, as defined in federal 49 CFR 173.54 (Forbidden Explosives) or a Division 1.1, 1.2, or 1.3 explosive, as defined in 49 CFR 173.50 (Class 1 − Definitions), each incorporated by reference in 35 Ill. Adm. Code 720.111(b).

 

BOARD NOTE:  Corresponding 40 CFR 261.23 cites to 49 CFR 173.53 (Provisions for Using Old Classifications of Explosives).  That citation aids bridging obsolete USDOT rules to the current version.  The Board has not included citation to 49 CFR 173.53 because it imposes no substantive requirements.

 

b)         A solid waste that exhibits the characteristic of reactivity has the USEPA hazardous waste number of D003.

 

(Source:  Amended at 35 Ill. Reg. 17734, effective October 14, 2011)

 

Section 721.124  Toxicity Characteristic

 

a)         A solid waste (except manufactured gas plant waste) exhibits the characteristic of toxicity if, using Method 1311 (Toxicity Characteristic Leaching Procedure (TCLP)) in "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods", USEPA publication number EPA-530/SW-846, as incorporated by reference in 35 Ill. Adm. Code 720.111(a), the extract from a representative sample of the waste contains any of the contaminants listed in the table in subsection (b) at a concentration equal to or greater than the respective value given in that table.  If the waste contains less than 0.5 percent filterable solids, the waste itself, after filtering using the methodology outlined in Method 1311, is the extract for this Section.

 

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

 

b)         A solid waste that exhibits the characteristic of toxicity has the USEPA hazardous waste number specified in the following table that corresponds to the toxic contaminant causing it to be hazardous.

 

MAXIMUM CONCENTRATION OF CONTAMINANTS

FOR THE TOXICITY CHARACTERISTIC

 

USEPA Hazardous Waste No.	Contaminant	CAS Number	Note	Regulatory Level (mg/ℓ)
D004	Arsenic	7440-38-2		5.0
D005	Barium	7440-39-3		100.0
D018	Benzene	71-43-2		0.5
D006	Cadmium	7440-43-9		1.0
D019	Carbon tetrachloride	56-23-5		0.5
D020	Chlordane	57-74-9		0.03
D021	Chlorobenzene	108-90-7		100.0
D022	Chloroform	67-66-3		6.0
D007	Chromium	7440-47-3		5.0
D023	o-Cresol	95-48-7	2	200.0
D024	m-Cresol	108-39-4	2	200.0
D025	p-Cresol	106-44-5	2	200.0
D026	Cresol		2	200.0
D016	2,4-D	94-75-7		10.0
D027	1,4-Dichlorobenzene	106-46-7		7.5
D028	1,2-Dichloroethane	107-06-2		0.5
D029	1,1-Dichloroethylene	75-35-4		0.7
D030	2,4-Dinitrotoluene	121-14-2	1	0.13
D012	Endrin	72-20-8		0.02
D031	Heptachlor (and its epoxide)	76-44-8		0.008
D032	Hexachlorobenzene	118-74-1	1	0.13
D033	Hexachlorobutadiene	87-68-3		0.5
D034	Hexachloroethane	67-72-1		3.0
D008	Lead	7439-92-1		5.0
D013	Lindane	58-89-9		0.4
D009	Mercury	7439-97-6		0.2
D014	Methoxychlor	72-43-5		10.0
D035	Methyl ethyl ketone	78-93-3		200.0
D036	Nitrobenzene	98-95-3		2.0
D037	Pentachlorophenol	87-86-5		100.0
D038	Pyridine	110-86-1	1	5.0
D010	Selenium	7782-49-2		1.0
D011	Silver	7440-22-4		5.0
D039	Tetrachloroethylene	127-18-4		0.7
D015	Toxaphene	8001-35-2		0.5
D040	Trichloroethylene	79-01-6		0.5
D041	2,4,5-Trichlorophenol	95-95-4		400.0
D042	2,4,6-Trichlorophenol	88-06-2		2.0
D017	2,4,5-TP (Silvex)	93-72-1		1.0
D043	Vinyl chloride	75-01-4		0.2

 

Notes to Table:

 

1          Quantitation limit is greater than the calculated regulatory level. The quantitation limit therefore becomes the regulatory level.

 

2          If o-, m-, p-cresol concentrations cannot be differentiated, the total cresol (D026) concentration is used. The regulatory level of total cresol is 200.0 mg/ℓ.

 

(Source:  Amended at 48 Ill. Reg. 9827, effective June 20, 2024)

SUBPART D: LISTS OF HAZARDOUS WASTE

 

Section 721.130  General

 

a)         A solid waste is a hazardous waste if it is listed in this Subpart D unless it has been excluded from this list under 35 Ill. Adm. Code 720.120 and 720.122.

 

b)         The basis for listing the classes or types of wastes listed in this Subpart D is indicated by employing one or more of the following hazard codes:

 

1)         Hazard Codes.

 

A)	Ignitable waste	(I)
B)	Corrosive waste	(C)
C)	Reactive waste	(R)
D)	Toxicity Characteristic waste	(E)
E)	Acute hazardous waste	(H)
F)	Toxic waste	(T)

 

2)         Appendix G identifies the constituent that caused USEPA to list the waste as a toxicity characteristic waste (E) or toxic waste (T) in Sections 721.131 and 721.132.

 

c)         Each hazardous waste listed in this Subpart D is assigned a USEPA hazardous waste number that precedes the name of the waste.  This number must be used in complying with the federal notification requirements of section 3010 of RCRA (42 USC 6930) and certain recordkeeping and reporting requirements under 35 Ill. Adm. Code 702, 703, and 722 through 725, 727, and 728.

 

d)         The following hazardous wastes listed in Section 721.131 or 721.132 are subject to the generator category limits for acute hazardous wastes established in 35 Ill. Adm. Code 722.113(g):  hazardous wastes numbers F020, F021, F022, F023, F026, and F027.

 

(Source:  Amended at 48 Ill. Reg. 16813, effective November 7, 2024)

 

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.

 

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.	(T)
	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), and subsection (b)(4)(B) describes the recordkeeping requirements for motor vehicle manufacturing facilities.
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 hazardous waste number 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) (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) (including sludges and floats generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units), F037, K048, and K051 wastes are not included in this listing.	(T)
F039	Multi-source leachate resulting from the disposal of more than one restricted waste classified as hazardous under this Subpart D.  For purposes of this hazardous waste listing, "leachate" means liquids that have percolated through land-disposed wastes. (This multi-source leachate listing does not apply to leachate resulting from the disposal of more than one of the following USEPA hazardous wastes where the disposal of no other hazardous waste is involved:  F020, F021, F022, F026, F027, and F028.  Leachate from disposal of any combination of these hazardous wastes is considered single-source leachate, and that leachate retains the USEPA hazardous waste numbers of the wastes from which the leachate derived, and the leachate must meet the treatment standards for the underlying hazardous waste numbers.) BOARD NOTE:  Derived from the listing for F039 at 40 CFR 261.31(a) (2017) and the discussion at 55 Fed. Reg. 22520, 22619-22623 (June 1, 1990).	(T)

 

BOARD NOTE:  The primary hazardous properties of these materials have been indicated by the letters T (Toxicity), R (Reactivity), I (Ignitability), and C (Corrosivity).  The letter H indicates Acute Hazardous Waste.  "(I, T)" should be used to specify mixtures that are ignitable and contain toxic constituents.

 

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 facility owner or operator must be engaged in manufacturing complete vehicles (body and chassis or unibody) or chassis only; and

 

B)        The generator must maintain documentation and information in its on-site records that is 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.

 

(Source:  Amended at 42 Ill. Reg. 21673, effective November 19, 2018)

 

Section 721.132  Hazardous Waste from Specific Sources

 

a)         The following solid wastes are listed hazardous wastes from specific sources unless they are excluded under 35 Ill. Adm. Code 720.120 and 720.122 and listed in Appendix I.

 

USEPA Hazardous Waste No.

Industry and Hazardous Waste

Hazard Code

 

Wood Preservation Process Wastes:

 

K001

Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote or pentachlorophenol.

(T)

 

Inorganic Pigments Production Wastes:

 

K002	Wastewater treatment sludge from the production of chrome yellow and orange pigments.	(T)
K003	Wastewater treatment sludge from the production of molybdate orange pigments.	(T)
K004	Wastewater treatment sludge from the production of zinc yellow pigments.	(T)
K005	Wastewater treatment sludge from the production of chrome green pigments.	(T)
K006	Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous and hydrated).	(T)
K007	Wastewater treatment sludge from the production of iron blue pigments.	(T)
K008	Oven residue from the production of chrome oxide green pigments.	(T)

 

Organic Chemicals Production Wastes:

 

K009	Distillation bottoms from the production of acetaldehyde from ethylene.	(T)
K010	Distillation side cuts from the production of acetaldehyde from ethylene.	(T)
K011	Bottom stream from the wastewater stripper in the production of acrylonitrile.	(R, T)
K013	Bottom stream from the acetonitrile column in the production of acrylonitrile.	(R, T)
K014	Bottoms from the acetonitrile purification column in the production of acrylonitrile.	(T)
K015	Still bottoms from the distillation of benzyl chloride.	(T)
K016	Heavy ends or distillation residues from the production of carbon tetrachloride.	(T)
K017	Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.	(T)
K018	Heavy ends from the fractionation column in ethyl chloride production.	(T)
K019	Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production.	(T)
K020	Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.	(T)
K021	Aqueous spent antimony catalyst waste from fluoromethanes production.	(T)
K022	Distillation bottom tars from the production of phenol/acetone from cumene.	(T)
K023	Distillation light ends from the production of phthalic anhydride from naphthalene.	(T)
K024	Distillation bottoms from the production of phthalic anhydride from naphthalene.	(T)
K093	Distillation light ends from the production of phthalic anhydride from ortho-xylene.	(T)
K094	Distillation bottoms from the production of phthalic anhydride from ortho-xylene.	(T)
K025	Distillation bottoms from the production of nitrobenzene by the nitration of benzene.	(T)
K026	Stripping still tails from the production of methyl ethyl pyridines.	(T)
K027	Centrifuge and distillation residues from toluene di­isocyanate production.	(R, T)
K028	Spent catalyst from the hydrochlorinator reactor in the production of 1,1,1-trichloroethane.	(T)
K029	Waste from the product stream stripper in the production of 1,1,1-trichloroethane.	(T)
K095	Distillation bottoms from the production of 1,1,1-trichloroethane.	(T)
K096	Heavy ends from the heavy ends column from the production of 1,1,1-trichloroethane.	(T)
K030	Column bottoms or heavy ends from the combined production of trichloroethylene and perchloroethylene.	(T)
K083	Distillation bottoms from aniline production.	(T)
K103	Process residues from aniline extraction from the production of aniline.	(T)
K104	Combined wastewater streams generated from nitrobenzene/aniline production.	(T)
K085	Distillation or fractionation column bottoms from the production of chlorobenzenes.	(T)
K105	Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes.	(T)
K107	Column bottoms from product separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.	(C, T)
K108	Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.	(I, T)
K109	Spent filter cartridges from the product purification from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.	(T)
K110	Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.	(T)
K111	Product washwaters from the production of dinitrotoluene via nitration of toluene.	(C, T)
K112	Reaction by-product water from the drying column in the production of toluenedi­amine via hydrogenation of dinitrotoluene.	(T)
K113	Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.	(T)
K114	Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.	(T)
K115	Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.	(T)
K116	Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine.	(T)
K117	Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene.	(T)
K118	Spent adsorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.	(T)
K136	Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.	(T)
K156	Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.)	(T)
K157	Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.)	(T)
K158	Baghouse dusts and filter/separation solids from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.)	(T)
K159	Organics from the treatment of thiocarbamate wastes.	(T)
K161	Purification solids (including filtration, evaporation, and centrifugation solids), bag house dust, and floor sweepings from the production of dithiocarbamate acids and their salts. (This listing does not include K125 or K126.)	(R, T)
K174	Wastewater treatment sludges from the production of ethylene dichloride or vinyl chloride monomer (including sludges that result from commingled ethylene dichloride or vinyl chloride monomer wastewater and other wastewater), unless the sludges meet the following conditions:  1) The sludges are disposed of in a RCRA Subtitle C (42 USC 6921-6939e) or non-hazardous landfill licensed or permitted by a state or the federal government; 2) The sludges are not otherwise placed on the land prior to final disposal; and 3) The generator maintains documentation demonstrating that the waste was either disposed of in an on-site landfill or consigned to a transporter or disposal facility that provided a written commitment to dispose of the waste in an off-site landfill.  Upon a showing by the government that a respondent in any enforcement action brought to enforce the requirements of RCRA Subtitle C managed wastewater treatment sludges from the production of vinyl chloride monomer or ethylene dichloride, the respondent must demonstrate that it meets the conditions of the exclusion that are set forth above.  In doing so, the respondent must provide appropriate documentation that the terms of the exclusion were met (e.g., contracts between the generator and the landfill owner or operator, invoices documenting delivery of waste to landfill, etc.).	(T)
K175	Wastewater treatment sludges from the production of vinyl chloride monomer using mercuric chloride catalyst in an acetylene-based process.	(T)

 

Inorganic Chemicals Production Wastes:

 

K071	Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used.	(T)
K073	Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production.	(T)
K106	Wastewater treatment sludge from the mercury cell process in chlorine production.	(T)
K176	Baghouse filters from the production of antimony oxide, including filters from the production of intermediates (e.g., antimony metal or crude antimony oxide).	(E)
K177	Slag from the production of antimony oxide that is speculatively accumulated or disposed of, including slag from the production of intermediates (e.g., antimony metal or crude antimony oxide).	(T)
K178	Residues from manufacturing and manufacturing-site storage of ferric chloride from acids formed during the production of titanium dioxide using the chloride-ilmenite process.	(T)
K181	Nonwastewaters from the production of dyes or pigments (including nonwastewaters commingled at the point of generation with nonwastewaters from other processes) that, at the point of generation, contain mass loadings of any of the constituents identified in subsection (c) that are equal to or greater than the corresponding subsection (c) levels, as determined on a calendar year basis.  These wastes will not be hazardous if the nonwastewaters are managed in one of the following ways:   1)   They are disposed of in a municipal solid waste landfill unit that is subject to the design criteria in 35 Ill. Adm. Code 811.303 through 811.309 and 811.315 through 811.317 and Subpart E of 35 Ill. Adm. Code 811 or 35 Ill. Adm. Code 814.302 and 814.402;   2)   They are disposed of in a hazardous waste landfill unit that is subject to either 35 Ill. Adm. Code 724.401 or 725.401;   3)   They are disposed of in other municipal solid waste landfill units that meet the design criteria in 35 Ill. Adm. Code 811.303 through 811.309 and 811.315 through 811.317 and Subpart E of 35 Ill. Adm. Code 811 or 35 Ill. Adm. Code 814.302 and 814.402, 35 Ill. Adm. Code 724.401, or 35 Ill. Adm. Code 725.401; or   4)   They are treated in a combustion unit that is permitted under 415 ILCS 5/39(d), or an onsite combustion unit that is permitted under 415 ILCS 5/39.5.   For the purposes of this listing, dyes or pigments production is defined in subsection (b)(1). Subsection (d) describes the process for demonstrating that a facility's nonwastewaters are not K181 waste.  This listing does not apply to wastes that are otherwise identified as hazardous under Sections 721.121 through 721.124 and 721.131 through 721.133 at the point of generation.  Also, the listing does not apply to wastes generated before any annual mass loading limit is met, as set forth in subsection (c).	(T)

 

Pesticides Production Wastes:

 

K031	By-product salts generated in the production of MSMA and cacodylic acid.	(T)
K032	Wastewater treatment sludge from the production of chlordane.	(T)
K033	Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane.	(T)
K034	Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.	(T)
K097	Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.	(T)
K035	Wastewater treatment sludges generated in the production of creosote.	(T)
K036	Still bottoms from toluene reclamation distillation in the production of disulfoton.	(T)
K037	Wastewater treatment sludges from the production of disulfoton.	(T)
K038	Wastewater from the washing and stripping of phorate production.	(T)
K039	Filter cake from the filtration of diethylphosphorodithioic acid in the production of phorate.	(T)
K040	Wastewater treatment sludge from the production of phorate.	(T)
K041	Wastewater treatment sludge from the production of toxaphene.	(T)
K098	Untreated process wastewater from the production of toxaphene.	(T)
K042	Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5-T.	(T)
K043	2,6-Dichlorophenol waste from the production of 2,4-D.	(T)
K099	Untreated wastewater from the production of 2,4-D.	(T)
K123	Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salts.	(T)
K124	Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.	(C, T)
K125	Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts.	(T)
K126	Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts.	(T)
K131	Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide.	(C, T)
K132	Spent absorbent and wastewater separator solids from the production of methyl bromide.	(T)

 

Explosives Production Wastes:

 

K044	Wastewater treatment sludges from the manufacturing and processing of explosives.	(R)
K045	Spent carbon from the treatment of wastewater containing explosives.	(R)
K046	Wastewater treatment sludges from the manufacturing, formulation and loading of lead-based initiating compounds.	(T)
K047	Pink/red water from TNT operations.	(R)

 

Petroleum Refining Wastes:

 

K048	Dissolved air flotation (DAF) float from the petroleum refining industry.	(T)
K049	Slop oil emulsion solids from the petroleum refining industry.	(T)
K050	Heat exchanger bundle cleaning sludge from the petroleum refining industry.	(T)
K051	API separator sludge from the petroleum refining industry.	(T)
K052	Tank bottoms (leaded) from the petroleum refining industry.	(T)
K169	Crude oil storage tank sediment from petroleum refining operations.	(T)
K170	Clarified slurry oil tank sediment or in-line filter/separation solids from petroleum refining operations.	(T)
K171	Spent hydrotreating catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media).	(I, T)
K172	Spent hydrorefining catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media).	(I, T)

 

Iron and Steel Production Wastes:

 

K061		Emission control dust/sludge from the primary production of steel in electric furnaces.	(T)
	K062	Spent pickle liquor generated by steel finishing operations of facilities within the iron and steel industry (SIC Codes 331 and 332) (as defined in 35 Ill. Adm. Code 720.110).	(C, T)

 

Primary Aluminum Production Wastes:

 

K088

Spent potliners from primary aluminum reduction.

(T)

 

Secondary Lead Production Wastes:

 

K069

Emission control dust/sludge from secondary lead smelting.

(T)

 

BOARD NOTE:  This listing is administratively stayed for sludge generated from secondary acid scrubber systems.  The stay will remain in effect until this note is removed.

 

K100

Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting.

(T)

 

Veterinary Pharmaceuticals Production Wastes:

 

K084	Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.	(T)
K101	Distillation tar residues from the distillation of aniline-based compounds in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.	(T)
K102	Residue from use of activated carbon for decolorization in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.	(T)

 

Ink Formulation Wastes:

 

K086

Solvent washes and sludges, caustic washes and sludges, or water washes and sludges from cleaning tubs and equipment used in the formulation of ink from pigments, dryers, soaps and stabilizers containing chromium and lead.

(T)

 

Coke Production Wastes:

 

K060	Ammonia still lime sludge from coking operations.	(T)
K087	Decanter tank tar sludge from coking operations.	(T)
K141	Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the production of coke from coal or the recovery of coke by-products produced from coal.  This listing does not include K087 (decanter tank tar sludges from coking operations).	(T)
K142	Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal.	(T)
K143	Process residues from the recovery of light oil, including, but not limited to, those generated in stills, decanters, and wash oil recovery units from the recovery of coke by-products produced from coal.	(T)
K144	Wastewater sump residues from light oil refining, including, but not limited to, intercepting or contamination sump sludges from the recovery of coke by-products produced from coal.	(T)
K145	Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal.	(T)
K147	Tar storage tank residues from coal tar refining.	(T)
K148	Residues from coal tar distillation, including, but not limited to, still bottoms.	(T)
K149	Distillation bottoms from the production of a- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.  (This waste does not include still bottoms from the distillation of benzyl chloride.)	(T)
K150	Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydrochloric acid recovery processes associated with the production of a- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.	(T)
K151	Wastewater treatment sludges, excluding neutralization and biological sludges, generated during the treatment of wastewaters from the production of a- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.	(T)

 

b)         Listing-Specific Definition.  For the purposes of the K181 hazardous waste listing in subsection (a), "dyes or pigments production" includes manufacture of the following product classes:  dyes, pigments, and FDA-certified colors that are in the azo, triarylmethane, perylene, and anthraquinone classes.  Azo products include azo, monoazo, diazo, triazo, polyazo, azoic, benzidine, and pyrazolone products.  Triarylmethane products include both triarylmethane and triphenylmethane products.  Wastes that are not generated at a dyes or pigments manufacturing site, such as wastes from the offsite use, formulation, and packaging of dyes or pigments, are not included in the K181 listing.

 

c)         K181 Listing Levels.  Nonwastewaters containing constituents in amounts equal to or exceeding the following levels during any calendar year are subject to the K181 hazardous waste listing in subsection (a), unless the conditions in the K181 hazardous waste listing are met:

 

Constituent	Chemical Abstracts No.	Mass Levels (kg/yr)
Aniline	62-53-3	9,300
o-Anisidine	90-04-0	110
4-Chloroaniline	106-47-8	4,800
p-Cresidine	120-71-8	660
2,4-Dimethylaniline	95-68-1	100
1,2-Phenylenediamine	95-54-5	710
1,3-Phenylenediamine	108-45-2	1,200

 

d)         Procedures for Demonstrating That Dyes or Pigments Nonwastewaters Are Not K181 Waste.  The procedures described in subsections (d)(1) through (d)(3) and (d)(5) establish when nonwastewaters from the production of dyes or pigments would not be hazardous.  (These procedures apply to wastes that are not disposed of in landfill units or treated in combustion units, as specified in subsection (a)).  If the nonwastewaters are disposed of in landfill units or treated in combustion units as described in subsection (a), then the nonwastewaters are not hazardous.  In order to demonstrate that it is meeting the landfill disposal or combustion conditions contained in the K181 waste listing description, the generator must maintain documentation as described in subsection (d)(4).

 

1)         Determination Based on No K181 Waste Constituents.  A generator that has knowledge (e.g., knowledge of constituents in wastes based on prior sampling and analysis data or information about raw materials used, production processes used, and reaction and degradation products formed) that its waste contains none of the K181 waste constituents (see subsection (c)) can use its knowledge to determine that its waste is not K181 waste.  The generator must document the basis for all such determinations on an annual basis and keep each annual documentation for three years.

 

2)         Determination for Generated Quantities of 1,000 Tonnes (1,000 Metric Tons) Per Year or Less for Wastes That Contain K181 Waste Constituents.  If the total annual quantity of dyes or pigments nonwastewaters generated is 1,000 tonnes or less, the generator can use knowledge of the wastes (e.g., knowledge of constituents in wastes based on prior analytical data or information about raw materials used, production processes used, and reaction and degradation products formed) to conclude that annual mass loadings for the K181 constituents are below the listing levels of subsection (c).  To make this determination, the generator must fulfill the following conditions:

 

A)        Each year, the generator must document the basis for determining that the annual quantity of nonwastewaters expected to be generated will be less than 1,000 tonnes;

 

B)        The generator must track the actual quantity of nonwastewaters generated from January 1 through December 31 of each calendar year.  If, at any time within the year, the actual waste quantity exceeds 1,000 tonnes, the generator must comply with the requirements of subsection (d)(3) for the remainder of that calendar year;

 

C)        The generator must keep a running total of the K181 waste constituent mass loadings over the course of the calendar year; and

 

D)        The generator must keep the following records on site for the three most recent calendar years in which the hazardous waste determinations were made:

 

i)          The quantity of dyes or pigments nonwastewaters generated;

 

ii)         The relevant process information used; and

 

iii)        The calculations performed to determine annual total mass loadings for each K181 waste constituent in the nonwastewaters during the year.

 

3)         Determination for generated quantities greater than 1,000 tonnes per year for wastes that contain K181 constituents.  If the total annual quantity of dyes or pigments nonwastewaters generated is greater than 1,000 tonnes, the generator must perform each of the following steps in order to make a determination that its waste is not K181 waste:

 

A)        The generator must determine which K181 waste constituents (see subsection (c)) are reasonably expected to be present in the wastes based on knowledge of the wastes (e.g., based on prior sampling and analysis data or information about raw materials used, production processes used, and reaction and degradation products formed);

 

B)        If 1,2-phenylenediamine is present in the wastes, the generator can use either knowledge of the wastes or sampling and analysis procedures to determine the level of this constituent in the wastes.  For determinations based on use of knowledge of the wastes, the generator must comply with the procedures for using knowledge of the wastes described in subsection (d)(2) and keep the records described in subsection (d)(2)(D).  For determinations based on sampling and analysis, the generator must comply with the sampling and analysis and recordkeeping requirements described in subsection (d)(3)(C);

 

C)        The generator must develop a waste sampling and analysis plan (or modify an existing plan) to collect and analyze representative waste samples for the K181 waste constituents reasonably expected to be present in the wastes.  At a minimum, the plan must include the following elements:

 

i)          A discussion of the number of samples needed to characterize the wastes fully;

 

ii)         The planned sample collection method to obtain representative waste samples;

 

iii)        A discussion of how the sampling plan accounts for potential temporal and spatial variability of the wastes; and

 

iv)        A detailed description of the test methods to be used, including sample preparation, clean up (if necessary), and determinative methods;

 

D)        The generator must collect and analyze samples in accordance with the waste sampling and analysis plan, and the plan must fulfill the following requirements:

 

i)          The sampling and analysis must be unbiased, precise, and representative of the wastes; and

 

ii)         The analytical measurements must be sufficiently sensitive, accurate, and precise to support any claim that the constituent mass loadings are below the listing levels of subsection (c);

 

E)        The generator must record the analytical results;

 

F)         The generator must record the waste quantity represented by the sampling and analysis results;

 

G)        The genrator must calculate constituent-specific mass loadings (product of concentrations and waste quantity);

 

H)        The generator must keep a running total of the K181 waste constituent mass loadings over the course of the calendar year;

 

I)         The generator must determine whether the mass of any of the K181 waste constituents listed in subsection (c) generated between January 1 and December 31 of any calendar year is below the K181 waste listing levels;

 

J)         The generator must keep the following records on site for the three most recent calendar years in which the hazardous waste determinations are made:

 

i)          The sampling and analysis plan;

 

ii)         The sampling and analysis results (including quality assurance or quality control data);

 

iii)        The quantity of dyes or pigments nonwastewaters generated; and

 

iv)        The calculations performed to determine annual mass loadings; and

 

K)        The generator must conduct non-hazardous waste determinations annually to verify that the wastes remain non-hazardous.

 

i)          The annual testing requirements are suspended after three consecutive successful annual demonstrations that the wastes are non-hazardous.  The generator can then use knowledge of the wastes to support subsequent annual determinations.

 

ii)         The annual testing requirements are reinstated if the manufacturing or waste treatment processes generating the wastes are significantly altered, resulting in an increase of the potential for the wastes to exceed the listing levels.

 

iii)        If the annual testing requirements are suspended, the generator must keep records of the process knowledge information used to support a non-hazardous determination.  If testing is reinstated, the generator must retain a description of the process change.

 

4)         Recordkeeping for the Landfill Disposal and Combustion Exemptions.  For the purposes of meeting the landfill disposal and combustion condition set out in the K181 waste listing description in subsection (a), the generator must maintain on site for three years documentation demonstrating that each shipment of waste was received by a landfill unit that is subject to or which meets the landfill design standards set out in the listing description or that the waste was treated in combustion units, as specified in the listing description in subsection (a).

 

5)         Waste Holding and Handling.  During the interim period, from the point of generation to completion of the hazardous waste determination, the generator must store the wastes appropriately.  If the wastes are determined to be hazardous and the generator has not complied with the hazardous waste storage requirements of 35 Ill. Adm. Code 722.116 during the interim period, the generator could be subject to an enforcement action for improper hazardous waste management.

 

(Source:  Amended at 42 Ill. Reg. 21673, effective November 19, 2018)

 

Section 721.133  Discarded Commercial Chemical Products, Off-Specification Species, Container Residues, and Spill Residues Thereof

 

The following materials or items are hazardous wastes if and when they are discarded or intended to be discarded, as described in Section 721.102(a)(2)(A); when they are mixed with waste oil or used oil or other material and applied to the land for dust suppression or road treatment; when they are otherwise applied to the land in lieu of their original intended use or when they are contained in products that are applied to land in lieu of their original intended use; or when, in lieu of their original intended use, they are produced for use as (or as a component of) a fuel, distributed for use as a fuel, or burned as a fuel.

 

a)         Any commercial chemical product or manufacturing chemical intermediate having the generic name listed in subsection (e) or (f).

 

b)         Any off-specification commercial chemical product or manufacturing chemical intermediate that, if it met specifications, would have the generic name listed in subsection (e) or (f).

 

c)         Any residue remaining in a container or inner liner removed from a container that has held any commercial chemical product or manufacturing chemical intermediate having the generic name listed in subsection (e) or (f), unless the container is empty, as defined in Section 721.107(b)(3) or 35 Ill. Adm. Code 726.607.

 

BOARD NOTE:  Unless the residue is being beneficially used or reused; legitimately recycled or reclaimed; or accumulated, stored, transported, or treated prior to such use, reuse, recycling, or reclamation, the Board considers the residue to be intended for discard, and thus a hazardous waste.  An example of a legitimate reuse of the residue would be if the residue remains in the container and the container is used to hold the same commercial chemical product or manufacturing chemical intermediate it previously held.  An example of the discard of the residue would be if the drum is sent to a drum reconditioner that reconditions the drum but discards the residue.

 

d)         Any residue or contaminated soil, water, or other debris resulting from the cleanup of a spill into or on any land or water of any commercial chemical product or manufacturing chemical intermediate having the generic name listed in subsection (e) or (f) or any residue or contaminated soil, water, or other debris resulting from the cleanup of a spill into or on any land or water of any off-specification chemical product or manufacturing chemical intermediate that, if it met specifications, would have the generic name listed in subsection (e) or (f).

 

BOARD NOTE:  The phrase "commercial chemical product or manufacturing chemical intermediate having the generic name"  refers to a chemical substance that is manufactured or formulated for commercial or manufacturing use that consists of the commercially pure grade of the chemical, any technical grades of the chemical that are produced or marketed, and all formulations in which the chemical is the sole active ingredient.  It does not refer to a material, such as a manufacturing process waste, that contains any of the substances listed in subsection (e) or (f).  If a manufacturing process waste is deemed to be a hazardous waste because it contains a substance listed in subsection (e) or (f), such waste will be listed in either Sections 721.131 or 721.132 or will be identified as a hazardous waste by the characteristics set forth in Subpart C.

 

e)         The commercial chemical products, manufacturing chemical intermediates, or off-specification commercial chemical products or manufacturing chemical intermediates referred to in subsections (a) through (d) are identified as acute hazardous waste (H).  These wastes and their corresponding USEPA hazardous waste numbers are the following:

 

BOARD NOTE:  For the convenience of the regulated community, the primary hazardous properties of these materials have been indicated by the letters T (Toxicity), and R (Reactivity).  The absence of a letter indicates that the compound is only listed for acute toxicity.  Wastes are first listed in alphabetical order by substance and then listed again in numerical order by USEPA hazardous waste number.

 

Alphabetical Listing

 

USEPA Hazardous Waste No.	Chemical Abstracts No. (CAS No.)	Substance	Hazard Code
P023	107-20-0	Acetaldehyde, chloro-
P002	591-08-2	Acetamide, N-(aminothioxomethyl)
P057	640-19-7	Acetamide, 2-fluoro-
P058	62-74-8	Acetic acid, fluoro-, sodium salt
P002	591-08-2	1-Acetyl-2-thiourea
P003	107-02-8	Acrolein
P070	116-06-3	Aldicarb
P203	1646-88-4	Aldicarb sulfone
P004	309-00-2	Aldrin
P005	107-18-6	Allyl alcohol
P006	20859-73-8	Aluminum phosphide	(R, T)
P007	2763-96-4	5-(Aminomethyl)-3-isoxazolol
P008	504-24-5	4-Aminopyridine
P009	131-74-8	Ammonium picrate	(R)
P119	7803-55-6	Ammonium vanadate
P099	506-61-6	Argentate(1-), bis(cyano-C)-, potassium
P010	7778-39-4	Arsenic acid H3AsO4
P012	1327-53-3	Arsenic oxide As2O3
P011	1303-28-2	Arsenic oxide As2O5
P011	1303-28-2	Arsenic pentoxide
P012	1327-53-3	Arsenic tri­oxide
P038	692-42-2	Arsine, diethyl-
P036	696-28-6	Arsonous dichloride, phenyl-
P054	151-56-4	Aziridine
P067	75-55-8	Aziridine, 2-methyl
P013	542-62-1	Barium cyanide
P024	106-47-8	Benzenamine, 4-chloro-
P077	100-01-6	Benzenamine, 4-nitro-
P028	100-44-7	Benzene, (chloromethyl)-
P042	51-43-4	1,2-Benzenediol, 4-(1-hydroxy-2-(methylamino)ethyl) -, (R)-
P046	122-09-8	Benzeneethanamine, a,a-dimethyl-
P014	108-98-5	Benzenethiol
P127	1563-66-2	7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-, methylcarbamate
P188	57-64-7	Benzoic acid, 2-hydroxy-, compound with (3aS-cis)-1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethylpyrrolo(2,3-b) indol-5-yl methylcarbamate ester (1:1)
P001	81-81-2*	2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, and salts, when present at concentrations greater than 0.3 percent
P028	100-44-7	Benzyl chloride
P015	7440-41-7	Beryllium powder
P017	598-31-2	Bromoacetone
P018	357-57-3	Brucine
P045	39196-18-6	2-Butanone,3,3-dimethyl-1-(methylthio)-, O-((methylamino)carbonyl) oxime
P021	592-01-8	Calcium cyanide
P021	592-01-8	Calcium cyanide Ca(CN)2
P189	55285-14-8	Carbamic acid, ((dibutylamino)-thio)methyl-, 2,3-dihydro-2,2-dimethyl-7-benzofuranyl ester
P191	644-64-4	Carbamic acid, dimethyl-, 1-((dimethyl-amino)carbonyl) -5-methyl-1H-pyrazol-3-yl ester
P192	119-38-0	Carbamic acid, dimethyl-, 3-methyl-1-(1-methylethyl)-1H-pyrazol-5-yl ester
P190	1129-41-5	Carbamic acid, methyl-, 3-methylphenyl ester
P127	1563-66-2	Carbofuran
P022	75-15-0	Carbon disulfide
P095	75-44-5	Carbonic dichloride
P189	55285-14-8	Carbosulfan
P023	107-20-0	Chloroacetaldehyde
P024	106-47-8	p-Chloroaniline
P026	5344-82-1	1-(o-Chlorophenyl)thiourea
P027	542-76-7	3-Chloropropionitrile
P029	544-92-3	Copper cyanide
P029	544-92-3	Copper cyanide CuCN
P202	64-00-6	m-Cumenyl methylcarbamate
P030		Cyanides (soluble cyanide salts), not otherwise specified
P031	460-19-5	Cyanogen
P033	506-77-4	Cyanogen chloride
P033	506-77-4	Cyanogen chloride CNCl
P034	131-89-5	2-Cyclohexyl-4,6-dinitrophenol
P016	542-88-1	Dichloromethyl ether
P036	696-28-6	Dichlorophenylarsine
P037	60-57-1	Dieldrin
P038	692-42-2	Diethylarsine
P041	311-45-5	Diethyl-p-nitrophenyl phosphate
P040	297-97-2	O,O-Diethyl O-pyrazinyl phosphorothioate
P043	55-91-4	Diisopropylfluorophosphate (DFP)
P191	644-64-4	Dimetilan
P004	309-00-2	1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1a,4a,4ab,5a,8a,8ab)-
P060	465-73-6	1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1a,4a,4ab,5b,8b,8ab)-
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-, (1aa,2b,2aa,3b,6b,6aa,7b,7aa)-
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-, (1aa,2b,2ab,3a,6a,6ab,7b,7aa)-, and metabolites
P044	60-51-5	Dimethoate
P046	122-09-8	a,a-Dimethylphenethylamine
P047	534-52-1*	4,6-Dinitro-o-cresol and salts
P048	51-28-5	2,4-Dinitrophenol
P020	88-85-7	Dinoseb
P085	152-16-9	Diphosphoramide, octamethyl-
P111	107-49-3	Diphosphoric acid, tetraethyl ester
P039	298-04-4	Disulfoton
P049	541-53-7	Dithiobiuret
P185	26419-73-8	1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O-((methylamino)- carbonyl)oxime
P050	115-29-7	Endosulfan
P088	145-73-3	Endothall
P051	72-20-8	Endrin
P051	72-20-8	Endrin, and metabolites
P042	51-43-4	Epinephrine
P031	460-19-5	Ethanedinitrile
P194	23135-22-0	Ethanimidothioic  acid, 2-(dimethylamino)-N-(((methylamino)carbonyl)oxy)-2-oxo-, methyl ester
P066	16752-77-5	Ethanimidothioic acid, N-(((methylamino)carbonyl)oxy)-, methyl ester
P101	107-12-0	Ethyl cyanide
P054	151-56-4	Ethyleneimine
P097	52-85-7	Famphur
P056	7782-41-4	Fluorine
P057	640-19-7	Fluoroacetamide
P058	62-74-8	Fluoroacetic acid, sodium salt
P198	23422-53-9	Formetanate hydrochloride
P197	17702-57-7	Formparanate
P065	628-86-4	Fulminic acid, mercury (2+) salt	(R, T)
P059	76-44-8	Heptachlor
P062	757-58-4	Hexaethyl tetraphosphate
P116	79-19-6	Hydrazinecarbothioamide
P068	60-34-4	Hydrazine, methyl-
P063	74-90-8	Hydrocyanic acid
P063	74-90-8	Hydrogen cyanide
P096	7803-51-2	Hydrogen phosphide
P060	465-73-6	Isodrin
P192	119-38-0	Isolan
P202	64-00-6	3-Isopropylphenyl-N-methylcarbamate
P007	2763-96-4	3(2H)-Isoxazolone, 5-(aminomethyl)-
P196	15339-36-3	Manganese, bis(dimethylcarbamodithioato-S,S')-
P196	15339-36-3	Manganese dimethyldithiocarbamate
P092	62-38-4	Mercury, (acetato-O)phenyl-
P065	628-86-4	Mercury fulminate	(R, T)
P082	62-75-9	Methanamine, N-methyl-N-nitroso-
P064	624-83-9	Methane, isocyanato-
P016	542-88-1	Methane, oxybis(chloro-
P112	509-14-8	Methane, tetranitro-	(R)
P118	75-70-7	Methanethiol, trichloro-
P198	23422-53-9	Methanimidamide, N,N-dimethyl-N'-(3-(( (methylamino)-carbonyl)oxy)phenyl)-, monohydrochloride
P197	17702-57-7	Methanimidamide, N,N-dimethyl-N'-(2-methyl-4-(((methylamino)carbonyl)oxy) phenyl)-
P199	2032-65-7	Methiocarb
P050	115-29-7	6,9-Methano-2,4,3-benzodioxathiepen, 6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide
P059	76-44-8	4,7-Methano-1H-indene, 1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro-
P066	16752-77-5	Methomyl
P068	60-34-4	Methyl hydrazine
P064	624-83-9	Methyl isocyanate
P069	75-86-5	2-Methyllactonitrile
P071	298-00-0	Methyl parathion
P190	1129-41-5	Metolcarb
P128	315-18-4	Mexacarbate
P072	86-88-4	a-Naphthylthiourea
P073	13463-39-3	Nickel carbonyl
P073	13463-39-3	Nickel carbonyl Ni(CO)4, (T-4)-
P074	557-19-7	Nickel cyanide
P074	557-19-7	Nickel cyanide Ni(CN)2
P075	54-11-5*	Nicotine, and salts (excluding patches, gums and lozenges that are FDA-approved over-the-counter nicotine replacement therapies)
P076	10102-43-9	Nitric oxide
P077	100-01-6	p-Nitroaniline
P078	10102-44-0	Nitrogen dioxide
P076	10102-43-9	Nitrogen oxide NO
P078	10102-44-0	Nitrogen oxide NO2
P081	55-63-0	Nitroglycerine	(R)
P082	62-75-9	N-Nitrosodimethylamine
P084	4549-40-0	N-Nitrosomethylvinylamine
P085	152-16-9	Octamethylpyrophosphoramide
P087	20816-12-0	Osmium oxide OsO4, (T-4)-
P087	20816-12-0	Osmium tetroxide
P088	145-73-3	7-Oxabicyclo(2.2.1)heptane-2,3-dicarboxylic acid
P194	23135-22-0	Oxamyl
P089	56-38-2	Parathion
P034	131-89-5	Phenol, 2-cyclohexyl-4,6-dinitro-
P128	315-18-4	Phenol, 4-(dimethylamino)-3,5-dimethyl-, methylcarbamate (ester)
P199	2032-65-7	Phenol, (3,5-dimethyl-4-(methylthio)-, methylcarbamate
P048	51-28-5	Phenol, 2,4-dinitro-
P047	534-52-1*	Phenol, 2-methyl-4,6-dinitro-, and salts
P202	64-00-6	Phenol, 3-(1-methylethyl)-, methyl carbamate
P201	2631-37-0	Phenol, 3-methyl-5-(1-methylethyl)-, methyl carbamate
P020	88-85-7	Phenol, 2-(1-methylpropyl)-4,6-dinitro-
P009	131-74-8	Phenol, 2,4,6-trinitro-, ammonium salt	(R)
P092	62-38-4	Phenylmercury acetate
P093	103-85-5	Phenylthiourea
P094	298-02-2	Phorate
P095	75-44-5	Phosgene
P096	7803-51-2	Phosphine
P041	311-45-5	Phosphoric acid, diethyl 4-nitrophenyl ester
P039	298-04-4	Phosphorodithioic acid, O,O-diethyl S-(2-(ethylthio)ethyl) ester
P094	298-02-2	Phosphorodithioic acid, O,O-diethyl S-((ethylthio)methyl) ester
P044	60-51-5	Phosphorodithioic acid, O,O-dimethyl S-(2-(methylamino)-2-oxoethyl) ester
P043	55-91-4	Phosphorofluoridic acid, bis(1-methylethyl)ester
P089	56-38-2	Phosphorothioic acid, O,O-diethyl O-(4-nitrophenyl) ester
P040	297-97-2	Phosphorothioic acid, O,O-diethyl O-pyrazinyl ester
P097	52-85-7	Phosphorothioic acid, O-(4-((dimethylamino)sulfonyl)phenyl) O,O-dimethyl ester
P071	298-00-0	Phosphorothioic acid, O,O-dimethyl O-(4-nitrophenyl) ester
P204	57-47-6	Physostigmine
P188	57-64-7	Physostigmine salicylate
P110	78-00-2	Plumbane, tetraethyl-
P098	151-50-8	Potassium cyanide
P098	151-50-8	Potassium cyanide KCN
P099	506-61-6	Potassium silver cyanide
P201	2631-37-0	Promecarb
P203	1646-88-4	Propanal, 2-methyl-2-(methyl-sulfonyl)-, O- ((methylamino)carbonyl) oxime
P070	116-06-3	Propanal, 2-methyl-2-(methylthio)-, O-((methylamino)carbonyl)oxime
P101	107-12-0	Propanenitrile
P027	542-76-7	Propanenitrile, 3-chloro-
P069	75-86-5	Propanenitrile, 2-hydroxy-2-methyl-
P081	55-63-0	1,2,3-Propanetriol, trinitrate-	(R)
P017	598-31-2	2-Propanone, 1-bromo-
P102	107-19-7	Propargyl alcohol
P003	107-02-8	2-Propenal
P005	107-18-6	2-Propen-1-ol
P067	75-55-8	1,2-Propylenimine
P102	107-19-7	2-Propyn-1-ol
P008	504-24-5	4-Pyridinamine
P075	54-11-5*	Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)- and salts (excluding patches, gums and lozenges that are FDA-approved over-the-counter nicotine replacement therapies)
P204	57-47-6	Pyrrolo(2,3-b)indol-5-ol, 1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethyl-, methylcarbamate (ester), (3aS-cis)-
P114	12039-52-0	Selenious acid, dithallium (1+) salt
P103	630-10-4	Selenourea
P104	506-64-9	Silver cyanide
P104	506-64-9	Silver cyanide AgCN
P105	26628-22-8	Sodium azide
P106	143-33-9	Sodium cyanide
P106	143-33-9	Sodium cyanide NaCN
P108	57-24-9*	Strychnidin-10-one, and salts
P018	357-57-3	Strychnidin-10-one, 2,3-dimethoxy-
P108	57-24-9*	Strychnine and salts
P115	7446-18-6	Sulfuric acid, dithallium (1+) salt
P109	3689-24-5	Tetraethyldithiopyrophosphate
P110	78-00-2	Tetraethyl lead
P111	107-49-3	Tetraethylpyrophosphate
P112	509-14-8	Tetranitromethane	(R)
P062	757-58-4	Tetraphosphoric acid, hexaethyl ester
P113	1314-32-5	Thallic oxide
P113	1314-32-5	Thallium oxide Tl2O3
P114	12039-52-0	Thallium (I) selenite
P115	7446-18-6	Thallium (I) sulfate
P109	3689-24-5	Thiodiphosphoric acid, tetraethyl ester
P045	39196-18-4	Thiofanox
P049	541-53-7	Thioimidodicarbonic diamide ((H2N)C(S)) 2NH
P014	108-98-5	Thiophenol
P116	79-19-6	Thiosemicarbazide
P026	5344-82-1	Thiourea, (2-chlorophenyl)-
P072	86-88-4	Thiourea, 1-naphthalenyl-
P093	103-85-5	Thiourea, phenyl-
P123	8001-35-2	Toxaphene
P185	26419-73-8	Tirpate
P118	75-70-7	Trichloromethanethiol
P119	7803-55-6	Vanadic acid, ammonium salt
P120	1314-62-1	Vanadium oxide V2O5
P120	1314-62-1	Vanadium pentoxide
P084	4549-40-0	Vinylamine, N-methyl-N-nitroso-
P001	81-81-2*	Warfarin, and salts, when present at concentrations greater than 0.3 percent
P121	557-21-1	Zinc cyanide
P121	557-21-1	Zinc cyanide Zn(CN)2
P205	137-30-4	Zinc, bis(dimethylcarbamodithioato-S,S')-
P122	1314-84-7	Zinc phosphide Zn3P2, when present at concentrations greater than 10 percent	(R, T)
P205	137-30-4	Ziram

 

Numerical Listing

 

USEPA Hazardous Waste No.

Chemical Abstracts No. (CAS No.)

Substance

Hazard Code

 

P001	81-81-2*	2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, and salts, when present at concentrations greater than 0.3 percent
P001	81-81-2*	Warfarin, and salts, when present at concentrations greater than 0.3 percent
P002	591-08-2	Acetamide, N-(aminothioxomethyl)
P002	591-08-2	1-Acetyl-2-thiourea
P003	107-02-8	Acrolein
P003	107-02-8	2-Propenal
P004	309-00-2	Aldrin
P004	309-00-2	1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1a,4a,4ab,5a,8a,8ab)-
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-, (1aa,2b,2aa,3b,6b,6aa,7b,7aa)-
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-, (1aa,2b,2ab,3a,6a,6ab,7b,7aa)-, and metabolites
P051	72-20-8	Endrin
P051	72-20-8	Endrin, and metabolites
P054	151-56-4	Aziridine
P054	151-56-4	Ethyleneimine
P056	7782-41-4	Fluorine
P057	640-19-7	Acetamide, 2-fluoro-
P057	640-19-7	Fluoroacetamide
P058	62-74-8	Acetic acid, fluoro-, sodium salt
P058	62-74-8	Fluoroacetic acid, sodium salt
P059	76-44-8	Heptachlor
P059	76-44-8	4,7-Methano-1H-indene, 1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro-
P060	465-73-6	1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1a,4a,4ab,5b,8b,8ab)-
P060	465-73-6	Isodrin
P062	757-58-4	Hexaethyl tetraphosphate
P062	757-58-4	Tetraphosphoric acid, hexaethyl ester
P063	74-90-8	Hydrocyanic acid
P063	74-90-8	Hydrogen cyanide
P064	624-83-9	Methane, isocyanato-
P064	624-83-9	Methyl isocyanate
P065	628-86-4	Fulminic acid, mercury (2+) salt	(R, T)
P065	628-86-4	Mercury fulminate	(R, T)
P066	16752-77-5	Ethanimidothioic acid, N-(((methyl­amino)­carbonyl)oxy)-, methyl ester
P066	16752-77-5	Methomyl
P067	75-55-8	Aziridine, 2-methyl
P067	75-55-8	1,2-Propylenimine
P068	60-34-4	Hydrazine, methyl-
P068	60-34-4	Methyl hydrazine
P069	75-86-5	2-Methyllactonitrile
P069	75-86-5	Propanenitrile, 2-hydroxy-2-methyl-
P070	116-06-3	Aldicarb
P070	116-06-3	Propanal, 2-methyl-2-(methylthio)-, O-((methylamino)carbonyl)oxime
P071	298-00-0	Methyl parathion
P071	298-00-0	Phosphorothioic acid, O,O-dimethyl O-(4-nitrophenyl) ester
P072	86-88-4	a-Naphthylthiourea
P072	86-88-4	Thiourea, 1-naphthalenyl-
P073	13463-39-3	Nickel carbonyl
P073	13463-39-3	Nickel carbonyl Ni(CO)4, (T-4)-
P074	557-19-7	Nickel cyanide
P074	557-19-7	Nickel cyanide Ni(CN)2
P075	54-11-5*	Nicotine, and salts (excluding patches, gums and lozenges that are FDA-approved over-the-counter nicotine replacement therapies)
P075	54-11-5*	Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)- and salts (excluding patches, gums and lozenges that are FDA-approved over-the-counter nicotine replacement therapies)
P076	10102-43-9	Nitric oxide
P076	10102-43-9	Nitrogen oxide NO
P077	100-01-6	Benzenamine, 4-nitro-
P077	100-01-6	p-Nitroaniline
P078	10102-44-0	Nitrogen dioxide
P078	10102-44-0	Nitrogen oxide NO2
P081	55-63-0	Nitroglycerine	(R)
P081	55-63-0	1,2,3-Propanetriol, trinitrate-	(R)
P082	62-75-9	Methanamine, N-methyl-N-nitroso-
P082	62-75-9	N-Nitrosodimethylamine
P084	4549-40-0	N-Nitrosomethylvinylamine
P084	4549-40-0	Vinylamine, N-methyl-N-nitroso-
P085	152-16-9	Diphosphoramide, octamethyl-
P085	152-16-9	Octamethylpyrophosphoramide
P087	20816-12-0	Osmium oxide OsO4, (T-4)-
P087	20816-12-0	Osmium tetroxide
P088	145-73-3	Endothall
P088	145-73-3	7-Oxabicyclo(2.2.1)heptane-2,3-dicarboxylic acid
P089	56-38-2	Parathion
P089	56-38-2	Phosphorothioic acid, O,O-diethyl O-(4-nitrophenyl) ester
P092	62-38-4	Mercury, (acetato-O)phenyl-
P092	62-38-4	Phenylmercury acetate
P093	103-85-5	Phenylthiourea
P093	103-85-5	Thiourea, phenyl-
P094	298-02-2	Phorate
P094	298-02-2	Phosphorodithioic acid, O,O-diethyl S-((ethylthio)methyl) ester
P095	75-44-5	Carbonic dichloride
P095	75-44-5	Phosgene
P096	7803-51-2	Hydrogen phosphide
P096	7803-51-2	Phosphine
P097	52-85-7	Famphur
P097	52-85-7	Phosphorothioic acid, O-(4-((dimethylamino)sulfonyl)phenyl) O,O-dimethyl ester
P098	151-50-8	Potassium cyanide
P098	151-50-8	Potassium cyanide KCN
P099	506-61-6	Argentate(1-), bis(cyano-C)-, potassium
P099	506-61-6	Potassium silver cyanide
P101	107-12-0	Ethyl cyanide
P101	107-12-0	Propanenitrile
P102	107-19-7	Propargyl alcohol
P102	107-19-7	2-Propyn-1-ol
P103	630-10-4	Selenourea
P104	506-64-9	Silver cyanide
P104	506-64-9	Silver cyanide AgCN
P105	26628-22-8	Sodium azide
P106	143-33-9	Sodium cyanide
P106	143-33-9	Sodium cyanide NaCN
P108	57-24-9*	Strychnidin-10-one, and salts
P108	57-24-9*	Strychnine and salts
P109	3689-24-5	Tetraethyldithiopyrophosphate
P109	3689-24-5	Thiodiphosphoric acid, tetraethyl ester
P110	78-00-2	Plumbane, tetraethyl-
P110	78-00-2	Tetraethyl lead
P111	107-49-3	Diphosphoric acid, tetraethyl ester
P111	107-49-3	Tetraethylpyrophosphate
P112	509-14-8	Methane, tetranitro-	(R)
P112	509-14-8	Tetranitromethane	(R)
P113	1314-32-5	Thallic oxide
P113	1314-32-5	Thallium oxide Tl2O3
P114	12039-52-0	Selenious acid, dithallium (1+) salt
P114	12039-52-0	Thallium (I) selenite
P115	7446-18-6	Sulfuric acid, dithallium (1+) salt
P115	7446-18-6	Thallium (I) sulfate
P116	79-19-6	Hydrazinecarbothioamide
P116	79-19-6	Thiosemicarbazide
P118	75-70-7	Methanethiol, trichloro-
P118	75-70-7	Trichloromethanethiol
P119	7803-55-6	Ammonium vanadate
P119	7803-55-6	Vanadic acid, ammonium salt
P120	1314-62-1	Vanadium oxide V2O5
P120	1314-62-1	Vanadium pentoxide
P121	557-21-1	Zinc cyanide
P121	557-21-1	Zinc cyanide Zn(CN)2
P122	1314-84-7	Zinc phosphide Zn3P2, when present at concentrations greater than 10 percent	(R, T)
P123	8001-35-2	Toxaphene
P127	1563-66-2	7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-, methylcarbamate
P127	1563-66-2	Carbofuran
P128	315-18-4	Phenol, 4-(dimethylamino)-3,5-dimethyl-, methylcarbamate (ester)
P128	315-18-4	Mexacarbate
P185	26419-73-8	1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O-((methylamino)- carbonyl)oxime
P185	26419-73-8	Tirpate
P188	57-64-7	Benzoic acid, 2-hydroxy-, compound with (3aS-cis)-1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethylpyrrolo(2,3-b)indol-5-yl methylcarbamate ester (1:1)
P188	57-64-7	Physostigmine salicylate
P189	55285-14-8	Carbamic acid, ((dibutylamino)-thio)methyl-, 2,3-dihydro-2,2-dimethyl-7-benzofuranyl ester
P189	55285-14-8	Carbosulfan
P190	1129-41-5	Carbamic acid, methyl-, 3-methylphenyl ester
P190	1129-41-5	Metolcarb
P191	644-64-4	Carbamic acid, dimethyl-, 1-((dimethyl-amino)carbonyl)-5-methyl-1H-pyrazol-3-yl ester
P191	644-64-4	Dimetilan
P192	119-38-0	Carbamic acid, dimethyl-, 3-methyl-1-(1-methylethyl)-1H-pyrazol-5-yl ester
P192	119-38-0	Isolan
P194	23135-22-0	Ethanimidothioic acid, 2-(dimethylamino)-N-(((methylamino)carbonyl)oxy)-2-oxo-, methyl ester
P194	23135-22-0	Oxamyl
P196	15339-36-3	Manganese, bis(dimethylcarbamodithioato-S,S')-
P196	15339-36-3	Manganese dimethyldithiocarbamate
P197	17702-57-7	Formparanate
P197	17702-57-7	Methanimidamide, N,N-dimethyl-N'-(2-methyl-4-(((methylamino)carbonyl)oxy)phenyl)-
P198	23422-53-9	Formetanate hydrochloride
P198	23422-53-9	Methanimidamide, N,N-dimethyl-N'-(3-(((methylamino)-carbonyl)oxy)phenyl)-, monohydrochloride
P199	2032-65-7	Methiocarb
P199	2032-65-7	Phenol, (3,5-dimethyl-4-(methylthio)-, methylcarbamate
P201	2631-37-0	Phenol, 3-methyl-5-(1-methylethyl)-, methyl carbamate
P201	2631-37-0	Promecarb
P202	64-00-6	m-Cumenyl methylcarbamate
P202	64-00-6	3-Isopropylphenyl-N-methylcarbamate
P202	64-00-6	Phenol, 3-(1-methylethyl)-, methyl carbamate
P203	1646-88-4	Aldicarb sulfone
P203	1646-88-4	Propanal, 2-methyl-2-(methyl-sulfonyl)-, O-((methylamino)carbonyl) oxime
P204	57-47-6	Physostigmine
P204	57-47-6	Pyrrolo(2,3-b)indol-5-ol, 1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethyl-, methylcarbamate (ester), (3aS-cis)-
P205	137-30-4	Zinc, bis(dimethylcarbamodithioato-S,S')-
P205	137-30-4	Ziram

 

BOARD NOTE:  An asterisk (*) following the CAS number indicates that the CAS number is given for the parent compound only.

 

f)         The commercial chemical products, manufacturing chemical intermediates, or off-specification commercial chemical products referred to in subsections (a) through (d), are identified as toxic wastes (T) unless otherwise designated.  These wastes and their corresponding USEPA hazardous waste numbers are the following:

 

BOARD NOTE:  For the convenience of the regulated community, the primary hazardous properties of these materials have been indicated by the letters T (Toxicity), R (Reactivity), I (Ignitability), and C (Corrosivity).  The absence of a letter indicates that the compound is only listed for toxicity.  Wastes are first listed in alphabetical order by substance and then listed again in numerical order by USEPA hazardous waste number.

 

USEPA Hazardous Waste No.	Chemical Abstracts No. (CAS No.)	Substance	Hazard Code
U394	30558-43-1	A2213
U001	75-07-0	Acetaldehyde	(I)
U034	75-87-6	Acetaldehyde, trichloro-
U187	62-44-2	Acetamide, N-(4-ethoxyphenyl)-
U005	53-96-3	Acetamide, N-9H-fluoren-2-yl-
U240	P 94-75-7	Acetic acid, (2,4-dichlorophenoxy)-, salts and esters
U112	141-78-6	Acetic acid, ethyl ester	(I)
U144	301-04-2	Acetic acid, lead (2+) salt
U214	563-68-8	Acetic acid, thallium (1+) salt
See F027	93-76-5	Acetic acid, (2,4,5-trichlorophenoxy)-
U002	67-64-1	Acetone	(I)
U003	75-05-8	Acetonitrile	(I, T)
U004	98-86-2	Acetophenone
U005	53-96-3	2-Acetylaminofluorene
U006	75-36-5	Acetyl chloride	(C, R, T)
U007	79-06-1	Acrylamide
U008	79-10-7	Acrylic acid	(I)
U009	107-13-1	Acrylonitrile
U011	61-82-5	Amitrole
U012	62-53-3	Aniline	(I, T)
U136	75-60-5	Arsinic acid, dimethyl-
U014	492-80-8	Auramine
U015	115-02-6	Azaserine
U010	50-07-7	Azirino(2',3':3,4)pyrrolo(1,2-a)indole-4,7-dione, 6-amino-8-(((aminocarbonyl)oxy)methyl)-1,1a,2,8,8a,8b-hexahydro-8a-methoxy-5-methyl-, (1a-S-(1aa,8b,8aa,8ba))-
U280	101-27-9	Barban
U278	22781-23-3	Bendiocarb
U364	22961-82-6	Bendiocarb phenol
U271	17804-35-2	Benomyl
U157	56-49-5	Benz(j)aceanthrylene, 1,2-dihydro-3-methyl-
U016	225-51-4	Benz(c)acridine
U017	98-87-3	Benzal chloride
U192	23950-58-5	Benzamide, 3,5-dichloro-N-(1,1-dimethyl-2-propynyl)-
U018	56-55-3	Benz(a)anthracene
U094	57-97-6	Benz(a)anthracene, 7,12-dimethyl-
U012	62-53-3	Benzenamine	(I, T)
U014	492-80-8	Benzenamine, 4,4'-carbonimidoylbis(N,N-dimethyl-
U049	3165-93-3	Benzenamine, 4-chloro-2-methyl-, hydrochloride
U093	60-11-7	Benzenamine, N,N-dimethyl-4-(phenylazo)-
U328	95-53-4	Benzenamine, 2-methyl-
U353	106-49-0	Benzenamine, 4-methyl-
U158	101-14-4	Benzenamine, 4,4'-methylenebis(2-chloro-
U222	636-21-5	Benzenamine, 2-methyl-, hydrochloride
U181	99-55-8	Benzenamine, 2-methyl-5-nitro-
U019	71-43-2	Benzene	(I, T)
U038	510-15-6	Benzeneacetic acid, 4-chloro-a-(4-chlorophenyl)-a-hydroxy-, ethyl ester
U030	101-55-3	Benzene, 1-bromo-4-phenoxy-
U035	305-03-3	Benzenebutanoic acid, 4-(bis(2-chloroethyl)amino)-
U037	108-90-7	Benzene, chloro-
U221	25376-45-8	Benzenediamine, ar-methyl-
U028	117-81-7	1,2-Benzenedicarboxylic acid, bis(2-ethylhexyl) ester
U069	84-74-2	1,2-Benzenedicarboxylic acid, dibutyl ester
U088	84-66-2	1,2-Benzenedicarboxylic acid, diethyl ester
U102	131-11-3	1,2-Benzenedicarboxylic acid, dimethyl ester
U107	117-84-0	1,2-Benzenedicarboxylic acid, dioctyl ester
U070	95-50-1	Benzene, 1,2-dichloro-
U071	541-73-1	Benzene, 1,3-dichloro-
U072	106-46-7	Benzene, 1,4-dichloro-
U060	72-54-8	Benzene, 1,1'-(2,2-dichloroethylidene)bis(4-chloro-
U017	98-87-3	Benzene, (dichloromethyl)-
U223	26471-62-5	Benzene, 1,3-diisocyanatomethyl-	(R, T)
U239	1330-20-7	Benzene, dimethyl-	(I)
U201	108-46-3	1,3-Benzenediol
U127	118-74-1	Benzene, hexachloro-
U056	110-82-7	Benzene, hexahydro-	(I)
U220	108-88-3	Benzene, methyl-
U105	121-14-2	Benzene, 1-methyl-2,4-dinitro-
U106	606-20-2	Benzene, 2-methyl-1,3-dinitro-
U055	98-82-8	Benzene, (1-methylethyl)-	(I)
U169	98-95-3	Benzene, nitro-	(I, T)
U183	608-93-5	Benzene, pentachloro-
U185	82-68-8	Benzene, pentachloronitro-
U020	98-09-9	Benzenesulfonic acid chloride	(C, R)
U020	98-09-9	Benzenesulfonyl chloride	(C, R)
U207	95-94-3	Benzene, 1,2,4,5-tetrachloro-
U061	50-29-3	Benzene, 1,1'-(2,2,2-trichloroethylidene)bis(4-chloro-
U247	72-43-5	Benzene, 1,1'-(2,2,2-trichloroethylidene)bis(4-methoxy-
U023	98-07-7	Benzene, (trichloromethyl)-	(C, R, T)
U234	99-35-4	Benzene, 1,3,5-trinitro-	(R, T)
U021	92-87-5	Benzidene
U203	94-59-7	1,3-Benzodioxole, 5-(2-propenyl)-
U141	120-58-1	1,3-Benzodioxole, 5-(1-propenyl)-
U090	94-58-6	1,3-Benzodioxole, 5-propyl-
U278	22781-23-3	1,3-Benzodioxol-4-ol, 2,2-dimethyl-, methyl carbamate
U364	22961-82-6	1,3-Benzodioxol-4-ol, 2,2-dimethyl-
U367	1563-38-8	7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-
U064	189-55-9	Benzo(rst)pentaphene
U248	81-81-2	2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, and salts, when present at concentrations of 0.3 percent or less
U022	50-32-8	Benzo(a)pyrene
U197	106-51-4	p-Benzoquinone
U023	98-07-7	Benzotrichloride	(C, R, T)
U085	1464-53-5	2,2'-Bioxirane	(I, T)
U021	92-87-5	(1,1'-Biphenyl)-4,4'-diamine
U073	91-94-1	(1,1'-Biphenyl)-4,4'-diamine, 3,3'-dichloro-
U091	119-90-4	(1,1'-Biphenyl)-4,4'-diamine, 3,3'-dimethoxy-
U095	119-93-7	(1,1'-Biphenyl)-4,4'-diamine, 3,3'-dimethyl-
U225	75-25-2	Bromoform
U030	101-55-3	4-Bromophenyl phenyl ether
U128	87-68-3	1,3-Butadiene, 1,1,2,3,4,4-hexachloro-
U172	924-16-3	1-Butanamine, N-butyl-N-nitroso-
U031	71-36-3	1-Butanol	(I)
U159	78-93-3	2-Butanone	(I, T)
U160	1338-23-4	2-Butanone, peroxide	(R, T)
U053	4170-30-3	2-Butenal
U074	764-41-0	2-Butene, 1,4-dichloro-	(I, T)
U143	303-34-4	2-Butenoic acid, 2-methyl-, 7-((2,3-dihydroxy-2-(1-methoxyethyl)-3-methyl-1-oxobutoxy)methyl)-2,3,5,7a-tetrahydro-1H-pyrrolizin-1-yl ester, (1S-(1a(Z), 7(2S*,3R*), 7aa))-
U031	71-36-3	n-Butyl alcohol	(I)
U136	75-60-5	Cacodylic acid
U032	13765-19-0	Calcium chromate
U372	10605-21-7	Carbamic acid, 1H-benzimidazol-2-yl, methyl ester
U271	17804-35-2	Carbamic acid, (1-((butylamino)carbonyl)-1H-benzimidazol-2-yl)-, methyl ester
U280	101-27-9	Carbamic acid, (3-chlorophenyl)-, 4-chloro-2-butynyl ester
U238	51-79-6	Carbamic acid, ethyl ester
U178	615-53-2	Carbamic acid, methylnitroso-, ethyl ester
U373	122-42-9	Carbamic acid, phenyl-, 1-methylethyl ester
U409	23564-05-8	Carbamic acid, (1,2-phenylenebis(iminocarbonothioyl))bis-, dimethyl ester
U097	79-44-7	Carbamic chloride, dimethyl-
U114	P 111-54-6	Carbamodithioic acid, 1,2-ethanediylbis-, salts and esters
U062	2303-16-4	Carbamothioic acid, bis(1-methylethyl)-, S-(2,3-dichloro-2-propenyl) ester
U389	2303-17-5	Carbamothioic acid, bis(1-methylethyl)-, S-(2,3,3-trichloro-2-propenyl) ester
U387	52888-80-9	Carbamothioic acid, dipropyl-, S-(phenylmethyl) ester
U279	63-25-2	Carbaryl
U372	10605-21-7	Carbendazim
U367	1563-38-8	Carbofuran phenol
U215	6533-73-9	Carbonic acid, dithallium (1+) salt
U033	353-50-4	Carbonic difluoride	(R, T)
U156	79-22-1	Carbonochloridic acid, methyl ester	(I, T)
U033	353-50-4	Carbon oxyfluoride	(R, T)
U211	56-23-5	Carbon tetrachloride
U034	75-87-6	Chloral
U035	305-03-3	Chlorambucil
U036	57-74-9	Chlordane, a and g isomers
U026	494-03-1	Chlornaphazin
U037	108-90-7	Chlorobenzene
U038	510-15-6	Chlorobenzilate
U039	59-50-7	p-Chloro-m-cresol
U042	110-75-8	2-Chloroethyl vinyl ether
U044	67-66-3	Chloroform
U046	107-30-2	Chloromethyl methyl ether
U047	91-58-7	b-Chloronaphthalene
U048	95-57-8	o-Chlorophenol
U049	3165-93-3	4-Chloro-o-toluidine, hydrochloride
U032	13765-19-0	Chromic acid H2CrO4, calcium salt
U050	218-01-9	Chrysene
U051		Creosote
U052	1319-77-3	Cresol (Cresylic acid)
U053	4170-30-3	Crotonaldehyde
U055	98-82-8	Cumene	(I)
U246	506-68-3	Cyanogen bromide CNBr
U197	106-51-4	2,5-Cyclohexadiene-1,4-dione
U056	110-82-7	Cyclohexane	(I)
U129	58-89-9	Cyclohexane, 1,2,3,4,5,6-hexachloro-, (1a,2a,3b,4a,5a,6b)-
U057	108-94-1	Cyclohexanone	(I)
U130	77-47-4	1,3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro-
U058	50-18-0	Cyclophosphamide
U240	P 94-75-7	2,4-D, salts and esters
U059	20830-81-3	Daunomycin
U060	72-54-8	DDD
U061	50-29-3	DDT
U062	2303-16-4	Diallate
U063	53-70-3	Dibenz(a,h)anthracene
U064	189-55-9	Dibenzo(a,i)pyrene
U066	96-12-8	1,2-Dibromo-3-chloropropane
U069	84-74-2	Dibutyl phthalate
U070	95-50-1	o-Dichlorobenzene
U071	541-73-1	m-Dichlorobenzene
U072	106-46-7	p-Dichlorobenzene
U073	91-94-1	3,3'-Dichlorobenzidine
U074	764-41-0	1,4-Dichloro-2-butene	(I, T)
U075	75-71-8	Dichlorodifluoromethane
U078	75-35-4	1,1-Dichloroethylene
U079	156-60-5	1,2-Dichloroethylene
U025	111-44-4	Dichloroethyl ether
U027	108-60-1	Dichloroisopropyl ether
U024	111-91-1	Dichloromethoxy ethane
U081	120-83-2	2,4-Dichlorophenol
U082	87-65-0	2,6-Dichlorophenol
U084	542-75-6	1,3-Dichloropropene
U085	1464-53-5	1,2:3,4-Diepoxybutane	(I, T)
U395	5952-26-1	Diethylene glycol, dicarbamate
U108	123-91-1	1,4-Diethyleneoxide
U028	117-81-7	Diethylhexyl phthalate
U086	1615-80-1	N,N’-Diethylhydrazine
U087	3288-58-2	O,O-Diethyl S-methyl dithiophosphate
U088	84-66-2	Diethyl phthalate
U089	56-53-1	Diethylstilbestrol
U090	94-58-6	Dihydrosafrole
U091	119-90-4	3,3'-Dimethoxybenzidine
U092	124-40-3	Dimethylamine	(I)
U093	60-11-7	p-Dimethylaminoazobenzene
U094	57-97-6	7,12-Dimethylbenz(a)anthracene
U095	119-93-7	3,3'-Dimethylbenzidine
U096	80-15-9	a, a-Dimethylbenzylhydroperoxide	(R)
U097	79-44-7	Dimethylcarbamoyl chloride
U098	57-14-7	1,1-Dimethylhydrazine
U099	540-73-8	1,2-Dimethylhydrazine
U101	105-67-9	2,4-Dimethylphenol
U102	131-11-3	Dimethyl phthalate
U103	77-78-1	Dimethyl sulfate
U105	121-14-2	2,4-Dinitrotoluene
U106	606-20-2	2,6-Dinitrotoluene
U107	117-84-0	Di-n-octyl phthalate
U108	123-91-1	1,4-Dioxane
U109	122-66-7	1,2-Diphenylhydrazine
U110	142-84-7	Dipropylamine	(I)
U111	621-64-7	Di-n-propylnitrosamine
U041	106-89-8	Epichlorohydrin
U001	75-07-0	Ethanal	(I)
U404	121-44-8	Ethanamine, N,N-diethyl-
U174	55-18-5	Ethanamine, N-ethyl-N-nitroso-
U155	91-80-5	1,2-Ethanediamine, N,N-dimethyl-N'-2-pyridinyl-N'-(2-thienylmethyl)-
U067	106-93-4	Ethane, 1,2-dibromo-
U076	75-34-3	Ethane, 1,1-dichloro-
U077	107-06-2	Ethane, 1,2-dichloro-
U131	67-72-1	Ethane, hexachloro-
U024	111-91-1	Ethane, 1,1'-(methylenebis(oxy))bis(2-chloro-
U117	60-29-7	Ethane, 1,1'-oxybis-	(I)
U025	111-44-4	Ethane, 1,1'-oxybis(2-chloro-
U184	76-01-7	Ethane, pentachloro-
U208	630-20-6	Ethane, 1,1,1,2-tetrachloro-
U209	79-34-5	Ethane, 1,1,2,2-tetrachloro-
U218	62-55-5	Ethanethioamide
U226	71-55-6	Ethane, 1,1,1-trichloro-
U227	79-00-5	Ethane, 1,1,2-trichloro-
U410	59669-26-0	Ethanimidothioic acid, N,N'-(thiobis((methylimino)carbonyloxy))bis-, dimethyl ester
U394	30558-43-1	Ethanimidothioic acid, 2-(dimethylamino)-N-hydroxy-2-oxo-, methyl ester
U359	110-80-5	Ethanol, 2-ethoxy-
U173	1116-54-7	Ethanol, 2,2'-(nitrosoimino)bis-
U395	5952-26-1	Ethanol, 2,2'-oxybis-, dicarbamate
U004	98-86-2	Ethanone, 1-phenyl-
U043	75-01-4	Ethene, chloro-
U042	110-75-8	Ethene, (2-chloroethoxy)-
U078	75-35-4	Ethene, 1,1-dichloro-
U079	156-60-5	Ethene, 1,2-dichloro-, (E)-
U210	127-18-4	Ethene, tetrachloro-
U228	79-01-6	Ethene, trichloro-
U112	141-78-6	Ethyl acetate	(I)
U113	140-88-5	Ethyl acrylate	(I)
U238	51-79-6	Ethyl carbamate (urethane)
U117	60-29-7	Ethyl ether	(I)
U114	P 111-54-6	Ethylenebisdithiocarbamic acid, salts and esters
U067	106-93-4	Ethylene dibromide
U077	107-06-2	Ethylene dichloride
U359	110-80-5	Ethylene glycol monoethyl ether
U115	75-21-8	Ethylene oxide	(I, T)
U116	96-45-7	Ethylenethiourea
U076	75-34-3	Ethylidene dichloride
U118	97-63-2	Ethyl methacrylate
U119	62-50-0	Ethyl methanesulfonate
U120	206-44-0	Fluoranthene
U122	50-00-0	Formaldehyde
U123	64-18-6	Formic acid	(C, T)
U124	110-00-9	Furan	(I)
U125	98-01-1	2-Furancarboxaldehyde	(I)
U147	108-31-6	2,5-Furandione
U213	109-99-9	Furan, tetrahydro-	(I)
U125	98-01-1	Furfural	(I)
U124	110-00-9	Furfuran	(I)
U206	18883-66-4	Glucopyranose, 2-deoxy-2-(3-methyl-3-nitrosoureido)-, D-
U206	18883-66-4	D-Glucose, 2-deoxy-2-(((methylnitrosoamino)-carbonyl)amino)-
U126	765-34-4	Glycidylaldehyde
U163	70-25-7	Guanidine, N-methyl-N'-nitro-N-nitroso-
U127	118-74-1	Hexachlorobenzene
U128	87-68-3	Hexachlorobutadiene
U130	77-47-4	Hexachlorocyclopentadiene
U131	67-72-1	Hexachloroethane
U132	70-30-4	Hexachlorophene
U243	1888-71-7	Hexachloropropene
U133	302-01-2	Hydrazine	(R, T)
U086	1615-80-1	Hydrazine, 1,2-diethyl-
U098	57-14-7	Hydrazine, 1,1-dimethyl-
U099	540-73-8	Hydrazine, 1,2-dimethyl-
U109	122-66-7	Hydrazine, 1,2-diphenyl-
U134	7664-39-3	Hydrofluoric acid	(C, T)
U134	7664-39-3	Hydrogen fluoride	(C, T)
U135	7783-06-4	Hydrogen sulfide
U135	7783-06-4	Hydrogen sulfide H2S
U096	80-15-9	Hydroperoxide, 1-methyl-1-phenylethyl-	(R)
U116	96-45-7	2-Imidazolidinethione
U137	193-39-5	Indeno(1,2,3-cd)pyrene
U190	85-44-9	1,3-Isobenzofurandione
U140	78-83-1	Isobutyl alcohol	(I, T)
U141	120-58-1	Isosafrole
U142	143-50-0	Kepone
U143	303-34-4	Lasiocarpene
U144	301-04-2	Lead acetate
U146	1335-32-6	Lead, bis(acetato-O)tetrahydroxytri-
U145	7446-27-7	Lead phosphate
U146	1335-32-6	Lead subacetate
U129	58-89-9	Lindane
U163	70-25-7	MNNG
U147	108-31-6	Maleic anhydride
U148	123-33-1	Maleic hydrazide
U149	109-77-3	Malononitrile
U150	148-82-3	Melphalan
U151	7439-97-6	Mercury
U152	126-98-7	Methacrylonitrile	(I, T)
U092	124-40-3	Methanamine, N-methyl-	(I)
U029	74-83-9	Methane, bromo-
U045	74-87-3	Methane, chloro-	(I, T)
U046	107-30-2	Methane, chloromethoxy-
U068	74-95-3	Methane, dibromo-
U080	75-09-2	Methane, dichloro-
U075	75-71-8	Methane, dichlorodifluoro-
U138	74-88-4	Methane, iodo-
U119	62-50-0	Methanesulfonic acid, ethyl ester
U211	56-23-5	Methane, tetrachloro-
U153	74-93-1	Methanethiol	(I, T)
U225	75-25-2	Methane, tribromo-
U044	67-66-3	Methane, trichloro-
U121	75-69-4	Methane, trichlorofluoro-
U036	57-74-9	4,7-Methano-1H-indene, 1,2,4,5,6,7,8,8-octachloro-2,3,3a,4,7,7a-hexahydro-
U154	67-56-1	Methanol	(I)
U155	91-80-5	Methapyrilene
U142	143-50-0	1,3,4-Metheno-2H-cyclobuta(cd)pentalen-2-one, 1,1a,3,3a,4,5,5,5a,5b,6-decachlorooctahydro-
U247	72-43-5	Methoxychlor
U154	67-56-1	Methyl alcohol	(I)
U029	74-83-9	Methyl bromide
U186	504-60-9	1-Methylbutadiene	(I)
U045	74-87-3	Methyl chloride	(I, T)
U156	79-22-1	Methyl chlorocarbonate	(I, T)
U226	71-55-6	Methylchloroform
U157	56-49-5	3-Methylcholanthrene
U158	101-14-4	4,4'-Methylenebis(2-chloroaniline)
U068	74-95-3	Methylene bromide
U080	75-09-2	Methylene chloride
U159	78-93-3	Methyl ethyl ketone (MEK)	(I, T)
U160	1338-23-4	Methyl ethyl ketone peroxide	(R, T)
U138	74-88-4	Methyl iodide
U161	108-10-1	Methyl isobutyl ketone	(I)
U162	80-62-6	Methyl methacrylate	(I, T)
U161	108-10-1	4-Methyl-2-pentanone	(I)
U164	56-04-2	Methylthiouracil
U010	50-07-7	Mitomycin C
U059	20830-81-3	5,12-Naphthacenedione, 8-acetyl-10-((3-amino-2,3,6-tri­deoxy-a-L-lyxo-hexapyranosyl)oxyl)-7,8,9,10-tetrahydro-6,8,11-trihydroxy-1-methoxy-, (8S-cis)-
U167	134-32-7	1-Naphthalenamine
U168	91-59-8	2-Naphthalenamine
U026	494-03-1	Naphthaleneamine, N,N'-bis(2-chloroethyl)-
U165	91-20-3	Naphthalene
U047	91-58-7	Naphthalene, 2-chloro-
U166	130-15-4	1,4-Naphthalenedione
U236	72-57-1	2,7-Naphthalenedisulfonic acid, 3,3'-((3,3'-dimethyl-(1,1'-biphenyl)-4,4'-diyl)bis(azo)bis(5-amino-4-hydroxy)-, tetrasodium salt
U279	63-25-2	1-Naphthalenol, methylcarbamate
U166	130-15-4	1,4-Naphthoquinone
U167	134-32-7	a-Naphthylamine
U168	91-59-8	b-Naphthylamine
U217	10102-45-1	Nitric acid, thallium (1+) salt
U169	98-95-3	Nitrobenzene	(I, T)
U170	100-02-7	p-Nitrophenol
U171	79-46-9	2-Nitropropane	(I, T)
U172	924-16-3	N-Nitrosodi-n-butylamine
U173	1116-54-7	N-Nitrosodiethanolamine
U174	55-18-5	N-Nitrosodiethylamine
U176	759-73-9	N-Nitroso-N-ethylurea
U177	684-93-5	N-Nitroso-N-methylurea
U178	615-53-2	N-Nitroso-N-methylurethane
U179	100-75-4	N-Nitrosopiperidine
U180	930-55-2	N-Nitrosopyrrolidine
U181	99-55-8	5-Nitro-o-toluidine
U193	1120-71-4	1,2-Oxathiolane, 2,2-dioxide
U058	50-18-0	2H-1,3,2-Oxazaphosphorin-2-amine, N,N-bis(2-chloroethyl)tetrahydro-, 2-oxide
U115	75-21-8	Oxirane	(I, T)
U126	765-34-4	Oxiranecarboxyaldehyde
U041	106-89-8	Oxirane, (chloromethyl)-
U182	123-63-7	Paraldehyde
U183	608-93-5	Pentachlorobenzene
U184	76-01-7	Pentachloroethane
U185	82-68-8	Pentachloronitrobenzene (PCNB)
See F027	87-86-5	Pentachlorophenol
U161	108-10-1	Pentanol, 4-methyl-	(I)
U186	504-60-9	1,3-Pentadiene	(I)
U187	62-44-2	Phenacetin
U188	108-95-2	Phenol
U048	95-57-8	Phenol, 2-chloro-
U039	59-50-7	Phenol, 4-chloro-3-methyl-
U081	120-83-2	Phenol, 2,4-dichloro-
U082	87-65-0	Phenol, 2,6-dichloro-
U089	56-53-1	Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-, (E)-
U101	105-67-9	Phenol, 2,4-dimethyl-
U052	1319-77-3	Phenol, methyl-
U132	70-30-4	Phenol, 2,2'-methylenebis(3,4,6-trichloro-
U411	114-26-1	Phenol, 2-(1-methylethoxy)-, methylcarbamate
U170	100-02-7	Phenol, 4-nitro-
See F027	87-86-5	Phenol, pentachloro-
See F027	58-90-2	Phenol, 2,3,4,6-tetrachloro-
See F027	95-95-4	Phenol, 2,4,5-trichloro-
See F027	88-06-2	Phenol, 2,4,6-trichloro-
U150	148-82-3	L-Phenylalanine, 4-(bis(2-chloroethyl)amino)-
U145	7446-27-7	Phosphoric acid, lead (2+) salt (2:3)
U087	3288-58-2	Phosphorodithioic acid, O,O-diethyl S-methyl ester
U189	1314-80-3	Phosphorus sulfide	(R)
U190	85-44-9	Phthalic anhydride
U191	109-06-8	2-Picoline
U179	100-75-4	Piperidine, 1-nitroso-
U192	23950-58-5	Pronamide
U194	107-10-8	1-Propanamine	(I, T)
U111	621-64-7	1-Propanamine, N-nitroso-N-propyl-
U110	142-84-7	1-Propanamine, N-propyl-	(I)
U066	96-12-8	Propane, 1,2-dibromo-3-chloro-
U083	78-87-5	Propane, 1,2-dichloro-
U149	109-77-3	Propanedinitrile
U171	79-46-9	Propane, 2-nitro-	(I, T)
U027	108-60-1	Propane, 2,2'-oxybis(2-chloro-
See F027	93-72-1	Propanoic acid, 2-(2,4,5-trichlorophenoxy)-
U193	1120-71-4	1,3-Propane sultone
U235	126-72-7	1-Propanol, 2,3-dibromo-, phosphate (3:1)
U140	78-83-1	1-Propanol, 2-methyl-	(I, T)
U002	67-64-1	2-Propanone	(I)
U007	79-06-1	2-Propenamide
U084	542-75-6	1-Propene, 1,3-dichloro-
U243	1888-71-7	1-Propene, 1,1,2,3,3,3-hexachloro-
U009	107-13-1	2-Propenenitrile
U152	126-98-7	2-Propenenitrile, 2-methyl-	(I, T)
U008	79-10-7	2-Propenoic acid	(I)
U113	140-88-5	2-Propenoic acid, ethyl ester	(I)
U118	97-63-2	2-Propenoic acid, 2-methyl-, ethyl ester
U162	80-62-6	2-Propenoic acid, 2-methyl-, methyl ester	(I, T)
U373	122-42-9	Propham
U411	114-26-1	Propoxur
See F027	93-72-1	Propionic acid, 2-(2,4,5-trichlorophenoxy)-
U194	107-10-8	n-Propylamine	(I, T)
U083	78-87-5	Propylene dichloride
U387	52888-80-9	Prosulfocarb
U148	123-33-1	3,6-Pyridazinedione, 1,2-dihydro-
U196	110-86-1	Pyridine
U191	109-06-8	Pyridine, 2-methyl-
U237	66-75-1	2,4-(1H,3H)-Pyrimidinedione, 5-(bis(2-chloroethyl) amino)-
U164	56-04-2	4(1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-thioxo-
U180	930-55-2	Pyrrolidine, 1-nitroso-
U200	50-55-5	Reserpine
U201	108-46-3	Resorcinol
U203	94-59-7	Safrole
U204	7783-00-8	Selenious acid
U204	7783-00-8	Selenium dioxide
U205	7488-56-4	Selenium sulfide	(R, T)
U205	7488-56-4	Selenium sulfide SeS2	(R, T)
U015	115-02-6	L-Serine, diazoacetate (ester)
See F027	93-72-1	Silvex (2,4,5-TP)
U206	18883-66-4	Streptozotocin
U103	77-78-1	Sulfuric acid, dimethyl ester
U189	1314-80-3	Sulfur phosphide	(R)
See F027	93-76-5	2,4,5-T
U207	95-94-3	1,2,4,5-Tetrachlorobenzene
U208	630-20-6	1,1,1,2-Tetrachloroethane
U209	79-34-5	1,1,2,2-Tetrachloroethane
U210	127-18-4	Tetrachloroethylene
See F027	58-90-2	2,3,4,6-Tetrachlorophenol
U213	109-99-9	Tetrahydrofuran	(I)
U214	563-68-8	Thallium (I) acetate
U215	6533-73-9	Thallium (I) carbonate
U216	7791-12-0	Thallium (I) chloride
U216	7791-12-0	Thallium chloride TlCl
U217	10102-45-1	Thallium (I) nitrate
U218	62-55-5	Thioacetamide
U410	59669-26-0	Thiodicarb
U153	74-93-1	Thiomethanol	(I, T)
U244	137-26-8	Thioperoxydicarbonic diamide ((H2N)C(S))2S2, tetramethyl-
U409	23564-05-8	Thiophanate-methyl
U219	62-56-6	Thiourea
U244	137-26-8	Thiram
U220	108-88-3	Toluene
U221	25376-45-8	Toluenediamine
U223	26471-62-5	Toluene diisocyanate	(R, T)
U328	95-53-4	o-Toluidine
U353	106-49-0	p-Toluidine
U222	636-21-5	o-Toluidine hydrochloride
U389	2303-17-5	Triallate
U011	61-82-5	1H-1,2,4-Triazol-3-amine
U227	79-00-5	Ethane, 1,1,2-trichloro-
U227	79-00-5	1,1,2-Trichloroethane
U228	79-01-6	Trichloroethylene
U121	75-69-4	Trichloromonofluoromethane
See F027	95-95-4	2,4,5-Trichlorophenol
See F027	88-06-2	2,4,6-Trichlorophenol
U404	121-44-8	Triethylamine
U234	99-35-4	1,3,5-Trinitrobenzene	(R, T)
U182	123-63-7	1,3,5-Trioxane, 2,4,6-trimethyl-
U235	126-72-7	Tris (2,3-dibromopropyl) phosphate
U236	72-57-1	Trypan blue
U237	66-75-1	Uracil mustard
U176	759-73-9	Urea, N-ethyl-N-nitroso-
U177	684-93-5	Urea, N-methyl-N-nitroso-
U043	75-01-4	Vinyl chloride
U248	81-81-2	Warfarin, and salts, when present at concentrations of 0.3 percent or less
U239	1330-20-7	Xylene	(I)
U200	50-55-5	Yohimban-16-carboxylic acid, 11,17-dimethoxy-18-((3,4,5-trimethoxybenzoyl)oxy)-, methyl ester, (3b,16b,17a,18b,20a)-
U249	1314-84-7	Zinc phosphide Zn3P2, when present at concentrations of 10 percent or less

 

Numerical Listing

 

USEPA Hazardous Waste No.

Chemical Abstracts No. (CAS No.)

Substance

Hazard Code

 

U001	75-07-0	Acetaldehyde	(I)
U001	75-07-0	Ethanal	(I)
U002	67-64-1	Acetone	(I)
U002	67-64-1	2-Propanone	(I)
U003	75-05-8	Acetonitrile	(I, T)
U004	98-86-2	Acetophenone
U004	98-86-2	Ethanone, 1-phenyl-
U005	53-96-3	Acetamide, N-9H-fluoren-2-yl-
U005	53-96-3	2-Acetylaminofluorene
U006	75-36-5	Acetyl chloride	(C, R, T)
U007	79-06-1	Acrylamide
U007	79-06-1	2-Propenamide
U008	79-10-7	Acrylic acid	(I)
U008	79-10-7	2-Propenoic acid	(I)
U009	107-13-1	Acrylonitrile
U009	107-13-1	2-Propenenitrile
U010	50-07-7	Azirino(2',3':3,4)pyrrolo(1,2-a)indole-4,7-dione, 6-amino-8-(((aminocarbonyl)oxy)methyl)-1,1a,2,8,8a,8b-hexahydro-8a-methoxy-5-methyl-, (1a-S-(1aa,8b,8aa,8ba))-
U010	50-07-7	Mitomycin C
U011	61-82-5	Amitrole
U011	61-82-5	1H-1,2,4-Triazol-3-amine
U012	62-53-3	Aniline	(I, T)
U012	62-53-3	Benzenamine	(I, T)
U014	492-80-8	Auramine
U014	492-80-8	Benzenamine, 4,4'-carbonimidoylbis(N,N-dimethyl-
U015	115-02-6	Azaserine
U015	115-02-6	L-Serine, diazoacetate (ester)
U016	225-51-4	Benz(c)acridine
U017	98-87-3	Benzal chloride
U017	98-87-3	Benzene, (dichloromethyl)-
U018	56-55-3	Benz(a)anthracene
U019	71-43-2	Benzene	(I, T)
U020	98-09-9	Benzenesulfonic acid chloride	(C, R)
U020	98-09-9	Benzenesulfonyl chloride	(C, R)
U021	92-87-5	Benzidene
U021	92-87-5	(1,1'-Biphenyl)-4,4'-diamine
U022	50-32-8	Benzo(a)pyrene
U023	98-07-7	Benzene, (trichloromethyl)-	(C, R, T)
U023	98-07-7	Benzotrichloride	(C, R, T)
U024	111-91-1	Dichloromethoxy ethane
U024	111-91-1	Ethane, 1,1'-(methylenebis(oxy))bis(2-chloro-
U025	111-44-4	Dichloroethyl ether
U025	111-44-4	Ethane, 1,1'-oxybis(2-chloro-
U026	494-03-1	Chlornaphazin
U026	494-03-1	Naphthaleneamine, N,N'-bis(2-chloroethyl)-
U027	108-60-1	Dichloroisopropyl ether
U027	108-60-1	Propane, 2,2'-oxybis(2-chloro-
U028	117-81-7	1,2-Benzenedicarboxylic acid, bis(2-ethylhexyl) ester
U028	117-81-7	Diethylhexyl phthalate
U029	74-83-9	Methane, bromo-
U029	74-83-9	Methyl bromide
U030	101-55-3	Benzene, 1-bromo-4-phenoxy-
U030	101-55-3	4-Bromophenyl phenyl ether
U031	71-36-3	1-Butanol	(I)
U031	71-36-3	n-Butyl alcohol	(I)
U032	13765-19-0	Calcium chromate
U032	13765-19-0	Chromic acid H2CrO4, calcium salt
U033	353-50-4	Carbonic difluoride	(R, T)
U033	353-50-4	Carbon oxyfluoride	(R, T)
U034	75-87-6	Acetaldehyde, trichloro-
U034	75-87-6	Chloral
U035	305-03-3	Benzenebutanoic acid, 4-(bis(2-chloroethyl)amino)-
U035	305-03-3	Chlorambucil
U036	57-74-9	Chlordane, a and g isomers
U036	57-74-9	4,7-Methano-1H-indene, 1,2,4,5,6,7,8,8-octachloro-2,3,3a,4,7,7a-hexahydro-
U037	108-90-7	Benzene, chloro-
U037	108-90-7	Chlorobenzene
U038	510-15-6	Benzeneacetic acid, 4-chloro-a-(4-chlorophenyl)-a-hydroxy-, ethyl ester
U038	510-15-6	Chlorobenzilate
U039	59-50-7	p-Chloro-m-cresol
U039	59-50-7	Phenol, 4-chloro-3-methyl-
U041	106-89-8	Epichlorohydrin
U041	106-89-8	Oxirane, (chloromethyl)-
U042	110-75-8	2-Chloroethyl vinyl ether
U042	110-75-8	Ethene, (2-chloroethoxy)-
U043	75-01-4	Ethene, chloro-
U043	75-01-4	Vinyl chloride
U044	67-66-3	Chloroform
U044	67-66-3	Methane, trichloro-
U045	74-87-3	Methane, chloro-	(I, T)
U045	74-87-3	Methyl chloride	(I, T)
U046	107-30-2	Chloromethyl methyl ether
U046	107-30-2	Methane, chloromethoxy-
U047	91-58-7	b-Chloronaphthalene
U047	91-58-7	Naphthalene, 2-chloro-
U048	95-57-8	o-Chlorophenol
U048	95-57-8	Phenol, 2-chloro-
U049	3165-93-3	Benzenamine, 4-chloro-2-methyl-, hydrochloride
U049	3165-93-3	4-Chloro-o-toluidine, hydrochloride
U050	218-01-9	Chrysene
U051		Creosote
U052	1319-77-3	Cresol (Cresylic acid)
U052	1319-77-3	Phenol, methyl-
U053	4170-30-3	2-Butenal
U053	4170-30-3	Crotonaldehyde
U055	98-82-8	Benzene, (1-methylethyl)-	(I)
U055	98-82-8	Cumene	(I)
U056	110-82-7	Benzene, hexahydro-	(I)
U056	110-82-7	Cyclohexane	(I)
U057	108-94-1	Cyclohexanone	(I)
U058	50-18-0	Cyclophosphamide
U058	50-18-0	2H-1,3,2-Oxazaphosphorin-2-amine, N,N-bis(2-chloroethyl)tetrahydro-, 2-oxide
U059	20830-81-3	Daunomycin
U059	20830-81-3	5,12-Naphthacenedione, 8-acetyl-10-((3-amino-2,3,6-trideoxy)-a-L-lyxo-hexapyranosyl)oxyl)-7,8,9,10-tetrahydro-6,8,11-trihydroxy-1-methoxy-, (8S-cis)-
U060	72-54-8	Benzene, 1,1'-(2,2-dichloroethylidene)bis(4-chloro-
U060	72-54-8	DDD
U061	50-29-3	Benzene, 1,1'-(2,2,2-trichloroethylidene)bis(4-chloro-
U061	50-29-3	DDT
U062	2303-16-4	Carbamothioic acid, bis(1-methylethyl)-, S-(2,3-dichloro-2-propenyl) ester
U062	2303-16-4	Diallate
U063	53-70-3	Dibenz(a,h)anthracene
U064	189-55-9	Benzo(rst)pentaphene
U064	189-55-9	Dibenzo(a,i)pyrene
U066	96-12-8	1,2-Dibromo-3-chloropropane
U066	96-12-8	Propane, 1,2-dibromo-3-chloro-
U067	106-93-4	Ethane, 1,2-dibromo-
U067	106-93-4	Ethylene dibromide
U068	74-95-3	Methane, dibromo-
U068	74-95-3	Methylene bromide
U069	84-74-2	1,2-Benzenedicarboxylic acid, dibutyl ester
U069	84-74-2	Dibutyl phthalate
U070	95-50-1	Benzene, 1,2-dichloro-
U070	95-50-1	o-Dichlorobenzene
U071	541-73-1	Benzene, 1,3-dichloro-
U071	541-73-1	m-Dichlorobenzene
U072	106-46-7	Benzene, 1,4-dichloro-
U072	106-46-7	p-Dichlorobenzene
U073	91-94-1	(1,1'-Biphenyl)-4,4'-diamine, 3,3'-dichloro-
U073	91-94-1	3,3'-Dichlorobenzidine
U074	764-41-0	2-Butene, 1,4-dichloro-	(I, T)
U074	764-41-0	1,4-Dichloro-2-butene	(I, T)
U075	75-71-8	Dichlorodifluoromethane
U075	75-71-8	Methane, dichlorodifluoro-
U076	75-34-3	Ethane, 1,1-dichloro-
U076	75-34-3	Ethylidene dichloride
U077	107-06-2	Ethane, 1,2-dichloro-
U077	107-06-2	Ethylene dichloride
U078	75-35-4	1,1-Dichloroethylene
U078	75-35-4	Ethene, 1,1-dichloro-
U079	156-60-5	1,2-Dichloroethylene
U079	156-60-5	Ethene, 1,2-dichloro-, (E)-
U080	75-09-2	Methane, dichloro-
U080	75-09-2	Methylene chloride
U081	120-83-2	2,4-Dichlorophenol
U081	120-83-2	Phenol, 2,4-dichloro-
U082	87-65-0	2,6-Dichlorophenol
U082	87-65-0	Phenol, 2,6-dichloro-
U083	78-87-5	Propane, 1,2-dichloro-
U083	78-87-5	Propylene dichloride
U084	542-75-6	1,3-Dichloropropene
U084	542-75-6	1-Propene, 1,3-dichloro-
U085	1464-53-5	2,2'-Bioxirane	(I, T)
U085	1464-53-5	1,2:3,4-Diepoxybutane	(I, T)
U086	1615-80-1	N,N'-Diethylhydrazine
U086	1615-80-1	Hydrazine, 1,2-diethyl-
U087	3288-58-2	O,O-Diethyl S-methyl dithiophosphate
U087	3288-58-2	Phosphorodithioic acid, O,O-diethyl S-methyl ester
U088	84-66-2	1,2-Benzenedicarboxylic acid, diethyl ester
U088	84-66-2	Diethyl phthalate
U089	56-53-1	Diethylstilbestrol
U089	56-53-1	Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-, (E)-
U090	94-58-6	1,3-Benzodioxole, 5-propyl-
U090	94-58-6	Dihydrosafrole
U091	119-90-4	(1,1'-Biphenyl)-4,4'-diamine, 3,3'-dimethoxy-
U091	119-90-4	3,3'-Dimethoxybenzidine
U092	124-40-3	Dimethylamine	(I)
U092	124-40-3	Methanamine, N-methyl-	(I)
U093	60-11-7	Benzenamine, N,N-dimethyl-4-(phenylazo)-
U093	60-11-7	p-Dimethylaminoazobenzene
U094	57-97-6	Benz(a)anthracene, 7,12-dimethyl-
U094	57-97-6	7,12-Dimethylbenz(a)anthracene
U095	119-93-7	(1,1'-Biphenyl)-4,4'-diamine, 3,3'-dimethyl-
U095	119-93-7	3,3'-Dimethylbenzidine
U096	80-15-9	a, a-Dimethylbenzylhydroperoxide	(R)
U096	80-15-9	Hydroperoxide, 1-methyl-1-phenylethyl-	(R )
U097	79-44-7	Carbamic chloride, dimethyl-
U097	79-44-7	Dimethylcarbamoyl chloride
U098	57-14-7	1,1-Dimethylhydrazine
U098	57-14-7	Hydrazine, 1,1-dimethyl-
U099	540-73-8	1,2-Dimethylhydrazine
U099	540-73-8	Hydrazine, 1,2-dimethyl-
U101	105-67-9	2,4-Dimethylphenol
U101	105-67-9	Phenol, 2,4-dimethyl-
U102	131-11-3	1,2-Benzenedicarboxylic acid, dimethyl ester
U102	131-11-3	Dimethyl phthalate
U103	77-78-1	Dimethyl sulfate
U103	77-78-1	Sulfuric acid, dimethyl ester
U105	121-14-2	Benzene, 1-methyl-2,4-dinitro-
U105	121-14-2	2,4-Dinitrotoluene
U106	606-20-2	Benzene, 2-methyl-1,3-dinitro-
U106	606-20-2	2,6-Dinitrotoluene
U107	117-84-0	1,2-Benzenedicarboxylic acid, dioctyl ester
U107	117-84-0	Di-n-octyl phthalate
U108	123-91-1	1,4-Diethyleneoxide
U108	123-91-1	1,4-Dioxane
U109	122-66-7	1,2-Diphenylhydrazine
U109	122-66-7	Hydrazine, 1,2-diphenyl-
U110	142-84-7	Dipropylamine	(I)
U110	142-84-7	1-Propanamine, N-propyl-	(I)
U111	621-64-7	Di-n-propylnitrosamine
U111	621-64-7	1-Propanamine, N-nitroso-N-propyl-
U112	141-78-6	Acetic acid, ethyl ester	(I)
U112	141-78-6	Ethyl acetate	(I)
U113	140-88-5	Ethyl acrylate	(I)
U113	140-88-5	2-Propenoic acid, ethyl ester	(I)
U114	P 111-54-6	Carbamodithioic acid, 1,2-ethanediylbis-, salts and esters
U114	P 111-54-6	Ethylenebisdithiocarbamic acid, salts and esters
U115	75-21-8	Ethylene oxide	(I, T)
U115	75-21-8	Oxirane	(I, T)
U116	96-45-7	Ethylenethiourea
U116	96-45-7	2-Imidazolidinethione
U117	60-29-7	Ethane, 1,1'-oxybis-	(I)
U117	60-29-7	Ethyl ether	(I)
U118	97-63-2	Ethyl methacrylate
U118	97-63-2	2-Propenoic acid, 2-methyl-, ethyl ester
U119	62-50-0	Ethyl methanesulfonate
U119	62-50-0	Methanesulfonic acid, ethyl ester
U120	206-44-0	Fluoranthene
U121	75-69-4	Methane, trichlorofluoro-
U121	75-69-4	Trichloromonofluoromethane
U122	50-00-0	Formaldehyde
U123	64-18-6	Formic acid	(C, T)
U124	110-00-9	Furan	(I)
U124	110-00-9	Furfuran	(I)
U125	98-01-1	2-Furancarboxaldehyde	(I)
U125	98-01-1	Furfural	(I)
U126	765-34-4	Glycidylaldehyde
U126	765-34-4	Oxiranecarboxyaldehyde
U127	118-74-1	Benzene, hexachloro-
U127	118-74-1	Hexachlorobenzene
U128	87-68-3	1,3-Butadiene, 1,1,2,3,4,4-hexachloro-
U128	87-68-3	Hexachlorobutadiene
U129	58-89-9	Cyclohexane, 1,2,3,4,5,6-hexachloro-, (1a,2a,3b,4a,5a,6b)-
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-(1a(Z), 7(2S*,3R*), 7aa))-
U143	303-34-4	Lasiocarpene
U144	301-04-2	Acetic acid, lead (2+) salt
U144	301-04-2	Lead acetate
U145	7446-27-7	Lead phosphate
U145	7446-27-7	Phosphoric acid, lead (2+) salt (2:3)
U146	1335-32-6	Lead, bis(acetato-O)tetrahydroxytri-
U146	1335-32-6	Lead subacetate
U147	108-31-6	2,5-Furandione
U147	108-31-6	Maleic anhydride
U148	123-33-1	Maleic hydrazide
U148	123-33-1	3,6-Pyridazinedione, 1,2-dihydro-
U149	109-77-3	Malononitrile
U149	109-77-3	Propanedinitrile
U150	148-82-3	Melphalan
U150	148-82-3	L-Phenylalanine, 4-(bis(2-chloroethyl)amino)-
U151	7439-97-6	Mercury
U152	126-98-7	Methacrylonitrile	(I, T)
U152	126-98-7	2-Propenenitrile, 2-methyl-	(I, T)
U153	74-93-1	Methanethiol	(I, T)
U153	74-93-1	Thiomethanol	(I, T)
U154	67-56-1	Methanol	(I)
U154	67-56-1	Methyl alcohol	(I)
U155	91-80-5	1,2-Ethanediamine, N,N-dimethyl-N'-2-pyridinyl-N'-(2-thienylmethyl)-
U155	91-80-5	Methapyrilene
U156	79-22-1	Carbonochloridic acid, methyl ester	(I, T)
U156	79-22-1	Methyl chlorocarbonate	(I, T)
U157	56-49-5	Benz(j)aceanthrylene, 1,2-dihydro-3-methyl-
U157	56-49-5	3-Methylcholanthrene
U158	101-14-4	Benzenamine, 4,4'-methylenebis(2-chloro-
U158	101-14-4	4,4'-Methylenebis(2-chloroaniline)
U159	78-93-3	2-Butanone	(I, T)
U159	78-93-3	Methyl ethyl ketone (MEK)	(I, T)
U160	1338-23-4	2-Butanone, peroxide	(R, T)
U160	1338-23-4	Methyl ethyl ketone peroxide	(R, T)
U161	108-10-1	Methyl isobutyl ketone	(I)
U161	108-10-1	4-Methyl-2-pentanone	(I)
U161	108-10-1	Pentanol, 4-methyl-	(I)
U162	80-62-6	Methyl methacrylate	(I, T)
U162	80-62-6	2-Propenoic acid, 2-methyl-, methyl ester	(I, T)
U163	70-25-7	Guanidine, N-methyl-N'-nitro-N-nitroso-
U163	70-25-7	MNNG
U164	56-04-2	Methylthiouracil
U164	56-04-2	4(1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-thioxo-
U165	91-20-3	Naphthalene
U166	130-15-4	1,4-Naphthalenedione
U166	130-15-4	1,4-Naphthoquinone
U167	134-32-7	1-Naphthalenamine
U167	134-32-7	a-Naphthylamine
U168	91-59-8	2-Naphthalenamine
U168	91-59-8	b-Naphthylamine
U169	98-95-3	Benzene, nitro-	(I, T)
U169	98-95-3	Nitrobenzene	(I, T)
U170	100-02-7	p-Nitrophenol
U170	100-02-7	Phenol, 4-nitro-
U171	79-46-9	2-Nitropropane	(I, T)
U171	79-46-9	Propane, 2-nitro-	(I, T)
U172	924-16-3	1-Butanamine, N-butyl-N-nitroso-
U172	924-16-3	N-Nitrosodi-n-butylamine
U173	1116-54-7	Ethanol, 2,2'-(nitrosoimino)bis-
U173	1116-54-7	N-Nitrosodiethanolamine
U174	55-18-5	Ethanamine, N-ethyl-N-nitroso-
U174	55-18-5	N-Nitrosodiethylamine
U176	759-73-9	N-Nitroso-N-ethylurea
U176	759-73-9	Urea, N-ethyl-N-nitroso-
U177	684-93-5	N-Nitroso-N-methylurea
U177	684-93-5	Urea, N-methyl-N-nitroso-
U178	615-53-2	Carbamic acid, methylnitroso-, ethyl ester
U178	615-53-2	N-Nitroso-N-methylurethane
U179	100-75-4	N-Nitrosopiperidine
U179	100-75-4	Piperidine, 1-nitroso-
U180	930-55-2	N-Nitrosopyrrolidine
U180	930-55-2	Pyrrolidine, 1-nitroso-
U181	99-55-8	Benzenamine, 2-methyl-5-nitro-
U181	99-55-8	5-Nitro-o-toluidine
U182	123-63-7	Paraldehyde
U182	123-63-7	1,3,5-Trioxane, 2,4,6-trimethyl-
U183	608-93-5	Benzene, pentachloro-
U183	608-93-5	Pentachlorobenzene
U184	76-01-7	Ethane, pentachloro-
U184	76-01-7	Pentachloroethane
U185	82-68-8	Benzene, pentachloronitro-
U185	82-68-8	Pentachloronitrobenzene (PCNB)
U186	504-60-9	1-Methylbutadiene	(I)
U186	504-60-9	1,3-Pentadiene	(I)
U187	62-44-2	Acetamide, N-(4-ethoxyphenyl)-
U187	62-44-2	Phenacetin
U188	108-95-2	Phenol
U189	1314-80-3	Phosphorus sulfide	(R)
U189	1314-80-3	Sulfur phosphide	(R)
U190	85-44-9	1,3-Isobenzofurandione
U190	85-44-9	Phthalic anhydride
U191	109-06-8	2-Picoline
U191	109-06-8	Pyridine, 2-methyl-
U192	23950-58-5	Benzamide, 3,5-dichloro-N-(1,1-dimethyl-2-propynyl)-
U192	23950-58-5	Pronamide
U193	1120-71-4	1,2-Oxathiolane, 2,2-dioxide
U193	1120-71-4	1,3-Propane sultone
U194	107-10-8	1-Propanamine	(I, T)
U194	107-10-8	n-Propylamine	(I, T)
U196	110-86-1	Pyridine
U197	106-51-4	p-Benzoquinone
U197	106-51-4	2,5-Cyclohexadiene-1,4-dione
U200	50-55-5	Reserpine
U200	50-55-5	Yohimban-16-carboxylic acid, 11,17-dimethoxy-18-((3,4,5-trimethoxybenzoyl)oxy)-, methyl ester, (3b,16b,17a,18b,20a)-
U201	108-46-3	1,3-Benzenediol
U201	108-46-3	Resorcinol
U203	94-59-7	1,3-Benzodioxole, 5-(2-propenyl)-
U203	94-59-7	Safrole
U204	7783-00-8	Selenious acid
U204	7783-00-8	Selenium dioxide
U205	7488-56-4	Selenium sulfide	(R, T)
U205	7488-56-4	Selenium sulfide SeS2	(R, T)
U206	18883-66-4	Glucopyranose, 2-deoxy-2-(3-methyl-3-nitrosoureido)-, D-
U206	18883-66-4	D-Glucose, 2-deoxy-2-(((methylnitrosoamino)-carbonyl)amino)-
U206	18883-66-4	Streptozotocin
U207	95-94-3	Benzene, 1,2,4,5-tetrachloro-
U207	95-94-3	1,2,4,5-Tetrachlorobenzene
U208	630-20-6	Ethane, 1,1,1,2-tetrachloro-
U208	630-20-6	1,1,1,2-Tetrachloroethane
U209	79-34-5	Ethane, 1,1,2,2-tetrachloro-
U209	79-34-5	1,1,2,2-Tetrachloroethane
U210	127-18-4	Ethene, tetrachloro-
U210	127-18-4	Tetrachloroethylene
U211	56-23-5	Carbon tetrachloride
U211	56-23-5	Methane, tetrachloro-
U213	109-99-9	Furan, tetrahydro-	(I)
U213	109-99-9	Tetrahydrofuran	(I)
U214	563-68-8	Acetic acid, thallium (1+) salt
U214	563-68-8	Thallium (I) acetate
U215	6533-73-9	Carbonic acid, dithallium (1+) salt
U215	6533-73-9	Thallium (I) carbonate
U216	7791-12-0	Thallium (I) chloride
U216	7791-12-0	Thallium chloride TlCl
U217	10102-45-1	Nitric acid, thallium (1+) salt
U217	10102-45-1	Thallium (I) nitrate
U218	62-55-5	Ethanethioamide
U218	62-55-5	Thioacetamide
U219	62-56-6	Thiourea
U220	108-88-3	Benzene, methyl-
U220	108-88-3	Toluene
U221	25376-45-8	Benzenediamine, ar-methyl-
U221	25376-45-8	Toluenediamine
U222	636-21-5	Benzenamine, 2-methyl-, hydrochloride
U222	636-21-5	o-Toluidine hydrochloride
U223	26471-62-5	Benzene, 1,3-diisocyanatomethyl-	(R, T)
U223	26471-62-5	Toluene diisocyanate	(R, T)
U225	75-25-2	Bromoform
U225	75-25-2	Methane, tribromo-
U226	71-55-6	Ethane, 1,1,1-trichloro-
U226	71-55-6	Methylchloroform
U227	79-00-5	Ethane, 1,1,2-trichloro-
U227	79-00-5	1,1,2-Trichloroethane
U228	79-01-6	Ethene, trichloro-
U228	79-01-6	Trichloroethylene
U234	99-35-4	Benzene, 1,3,5-trinitro-	(R, T)
U234	99-35-4	1,3,5-Trinitrobenzene	(R, T)
U235	126-72-7	1-Propanol, 2,3-dibromo-, phosphate (3:1)
U235	126-72-7	Tris(2,3-dibromopropyl) phosphate
U236	72-57-1	2,7-Naphthalenedisulfonic acid, 3,3'-((3,3'-dimethyl-(1,1'-biphenyl)-4,4'-diyl)bis(azo)bis(5-amino-4-hydroxy)-, tetrasodium salt
U236	72-57-1	Trypan blue
U237	66-75-1	2,4-(1H,3H)-Pyrimidinedione, 5-(bis(2-chloroethyl)amino)-
U237	66-75-1	Uracil mustard
U238	51-79-6	Carbamic acid, ethyl ester
U238	51-79-6	Ethyl carbamate (urethane)
U239	1330-20-7	Benzene, dimethyl-	(I, T)
U239	1330-20-7	Xylene	(I, T)
U240	P 94-75-7	Acetic acid, (2,4-dichlorophenoxy)-, salts and esters
U240	P 94-75-7	2,4-D, salts and esters
U243	1888-71-7	Hexachloropropene
U243	1888-71-7	1-Propene, 1,1,2,3,3,3-hexachloro-
U244	137-26-8	Thioperoxydicarbonic diamide ((H2N)C(S))2S2, tetramethyl-
U244	137-26-8	Thiram
U246	506-68-3	Cyanogen bromide CNBr
U247	72-43-5	Benzene, 1,1'-(2,2,2-trichloroethylidene)bis(4-methoxy-
U247	72-43-5	Methoxychlor
U248	81-81-2	2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, and salts, when present at concentrations of 0.3 percent or less
U248	81-81-2	Warfarin, and salts, when present at concentrations of 0.3 percent or less
U249	1314-84-7	Zinc phosphide Zn3P2, when present at concentrations of 10 percent or less
U271	17804-35-2	Benomyl
U271	17804-35-2	Carbamic acid, (1-((butylamino)carbonyl)-1H-benzimidazol-2-yl)-, methyl ester
U278	22781-23-3	Bendiocarb
U278	22781-23-3	1,3-Benzodioxol-4-ol, 2,2-dimethyl-, methyl carbamate
U279	63-25-2	Carbaryl
U279	63-25-2	1-Naphthalenol, methylcarbamate
U280	101-27-9	Barban
U280	101-27-9	Carbamic acid, (3-chlorophenyl)-, 4-chloro-2-butynyl ester
U328	95-53-4	Benzenamine, 2-methyl-
U328	95-53-4	o-Toluidine
U353	106-49-0	Benzenamine, 4-methyl-
U353	106-49-0	p-Toluidine
U359	110-80-5	Ethanol, 2-ethoxy-
U359	110-80-5	Ethylene glycol monoethyl ether
U364	22961-82-6	Bendiocarb phenol
U364	22961-82-6	1,3-Benzodioxol-4-ol, 2,2-dimethyl-
U367	1563-38-8	7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-
U367	1563-38-8	Carbofuran phenol
U372	10605-21-7	Carbamic acid, 1H-benzimidazol-2-yl, methyl ester
U372	10605-21-7	Carbendazim
U373	122-42-9	Carbamic acid, phenyl-, 1-methyl­ethyl ester
U373	122-42-9	Propham
U387	52888-80-9	Carbamothioic acid, dipropyl-, S-(phenylmethyl) ester
U387	52888-80-9	Prosulfocarb
U389	2303-17-5	Carbamothioic acid, bis(1-methylethyl)-, S-(2,3,3-trichloro-2-propenyl) ester
U389	2303-17-5	Triallate
U394	30558-43-1	A2213
U394	30558-43-1	Ethanimidothioic acid, 2-(dimethylamino)-N-hydroxy-2-oxo-, methyl ester
U395	5952-26-1	Diethylene glycol, dicarbamate
U395	5952-26-1	Ethanol, 2,2'-oxybis-, dicarbamate
U404	121-44-8	Ethanamine, N,N-diethyl-
U404	121-44-8	Triethylamine
U409	23564-05-8	Carbamic acid, (1,2-phenylenebis(iminocarbonothioyl))bis-, dimethyl ester
U409	23564-05-8	Thiophanate-methyl
U410	59669-26-0	Ethanimidothioic acid, N,N'- (thiobis((methylimino)carbonyloxy))bis-, dimethyl ester
U410	59669-26-0	Thiodicarb
U411	114-26-1	Phenol, 2-(1-methylethoxy)-, methylcarbamate
U411	114-26-1	Propoxur

 

(Source:  Amended at 44 Ill. Reg. 15142, effective September 3, 2020)

 

Section 721.135  Wood Preserving Wastes

 

a)         Wastes from wood preserving processes at plants that do not resume or initiate use of chlorophenolic preservatives will not meet the listing definition of F032 once the generator has met all of the requirements of subsections (b) and (c).  These wastes may, however, continue to meet another hazardous waste listing description or may exhibit one or more of the hazardous waste characteristics.

 

b)         Generators must either clean or replace all process equipment that may have come into contact with chlorophenolic formulations or constituents thereof, including, but not limited to, treatment cylinders, sumps, tanks, piping systems, drip pads, fork lifts and trams, in a manner that minimizes or eliminates the escape of hazardous waste or constituents, leachate, contaminated drippage or hazardous waste decomposition products to the groundwater, surface water, or atmosphere.

 

1)         Generators must do one of the following:

 

A)        Prepare and follow an equipment cleaning plan and clean equipment in accordance with subsection (b)(2); or

 

B)        Prepare and follow an equipment replacement plan and replace equipment in accordance with subsection (b)(3); or

 

C)        Document cleaning and replacement in accordance with subsections (b)(2) and (b)(3), carried out after termination of use of chlorophenolic preservatives.

 

2)         Cleaning requirements.

 

A)        The generator must prepare and sign a written equipment cleaning plan that describes the following:

 

i)          The equipment to be cleaned;

 

ii)         How the equipment will be cleaned;

 

iii)        The solvent to be used in cleaning;

 

iv)        How solvent rinses will be tested; and

 

v)         How cleaning residues will be disposed of.

 

B)        Equipment must be cleaned as follows:

 

i)          Remove all visible residues from process equipment; and

 

ii)         Rinse process equipment with an appropriate solvent until dioxins and dibenzofurans are not detected in the final solvent rinse.

 

C)        Analytical requirements.

 

i)          Rinses must be tested by using an appropriate method.

 

ii)         "Not detected" means at or below the following lower method calibration limit (MCL):  the 2,3,7,8-TCDD-based MCL is 0.01 parts per trillion (ppt), using a sample weight of 1000 g, an IS spiking level of 1 ppt, and a final extraction volume of 10 to 50 µℓ.  For other congeners, multiply the values by 1 for TCDF, PeCDD, or PeCDF; by 2.5 for HxCDD, HxCDF, HpCDD, or HpCDF; or by 5 for OCDD or OCDF.

 

D)        The generator must manage all residues from the cleaning process as F032 waste.

 

3)         Replacement requirements.

 

A)        The generator must prepare and sign a written equipment replacement plan that describes the following:

 

i)          The equipment to be replaced;

 

ii)         How the equipment will be replaced; and

 

iii)        How the equipment will be disposed of.

 

B)        The generator must manage the discarded equipment as F032 waste.

 

4)         Documentation requirements.  The generator must document that previous equipment cleaning and replacement was performed in accordance with subsections (b)(2) and (b)(3) and that the equipment cleaning and replacement occurred after cessation of use of chlorophenolic preservatives.

 

c)         The generator must maintain the following records documenting the cleaning and replacement as part of the facility's operating record:

 

1)         The name and address of the facility;

 

2)         Formulations previously used and the date on which their use ceased in each process at the plant;

 

3)         Formulations currently used in each process at the plant;

 

4)         The equipment cleaning or replacement plan;

 

5)         The name and address of any persons who conducted the cleaning and replacement;

 

6)         The dates on which cleaning and replacement were accomplished;

 

7)         The dates of sampling and testing;

 

8)         A description of the sample handling and preparation techniques used for extraction, containerization, preservation and chain-of-custody of the samples;

 

9)         A description of the tests performed, the date the tests were performed and the results of the tests;

 

10)         The name and model numbers of the instruments used in performing the tests;

 

11)         QA/QC documentation; and

 

12)         The following statement signed by the generator or the generator's authorized representative:

 

I certify under penalty of law that all process equipment required to be cleaned or replaced under 35 Ill. Adm. Code 721.135 was cleaned or replaced as represented in the equipment cleaning and replacement plan and accompanying documentation.  I am aware that there are significant penalties for providing false information, including the possibility of fine or imprisonment.

 

(Source:  Amended at 40 Ill. Reg. 11367, effective August 9, 2016)