6 CRR-NY 371.4NY-CRR
6 CRR-NY 371.4
6 CRR-NY 371.4
371.4 Lists of hazardous wastes.
(1) A solid waste is a hazardous waste if it is listed in this section, unless it has been excluded from this list under section 370.3(a) and (b) of this Title.
Although the names used for chemicals in this list include common names, trade names and specific isomer names under various chemical naming systems, where any one of these previous names are used, all other equivalent names shall be considered to be listed.
(2) The commissioner will indicate the basis for listing the classes or types of wastes listed in this section by employing one or more of the following hazard codes:
Toxicity characteristic waste
Acute hazardous waste
Appendix 22, infra, identifies the constituent which caused the commissioner to list the waste as a toxicity characteristic waste (E) or toxic waste (T) in subdivisions (b) and (c) of this section.
(3) Each hazardous waste listed in this section is assigned an EPA hazardous waste number which precedes the name of the waste. This number must be used in complying with the notification requirements of section 3010 of the Resource Conservation and Recovery Act and certain recordkeeping and reporting requirements under Parts 372, 373 and 376 (see section 370.1[e] of this Title).
(4) The following hazardous wastes listed in subdivision (b) of this section are subject to the exclusion limits for acutely hazardous waste established in section 371.1(f) of this Part: EPA hazardous waste numbers F020, F021, F022, F023, F026 and F027.
(b) Hazardous waste from nonspecific sources.
(1) The following solid wastes are listed hazardous wastes from nonspecific sources unless they are excluded under section 370.3(a) and (c) of this Title and listed in Appendix 24, infra:
|waste number||Hazardous waste||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/blends used in degreasing containing, before use, total of 10 percent or more (by volume) of one or more of the above halogenated solvents or those solvents listed in F002, F004 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.||(T)|
|F002||The following spent halogenated solvents: tetrachloro-ethylene, 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/blends containing, before use, a total of 10 percent or more (by volume) of one or more of the above halogenated solvents or those 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 nonhalogenated solvents: xylene, acetone, ethyl acetate, ethyl benzene, ethyl ether, methyl isobutyl ketone, n-butyl alcohol, cyclohexanone, and methanol; all spent solvent mixtures/blends containing, before use, only the above spent nonhalogenated solvents; and all spent solvent mixtures/blends containing, before use, one or more of the above nonhalogenated solvents, and a total of 10 percent or more (by volume) of one or more of those solvents listed in F001, F002, F004 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.||(I)*|
|F004||The following spent nonhalogenated solvents: cresols and cresylic acid, and nitrobenzene; all spent solvent mixtures/blends containing, before use, a total of 10 percent or more (by volume) of one or more of the above nonhalogenated solvents or those solvents listed in F001, F002 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.||(T)|
|F005||The following spent nonhalogenated solvents: toluene, methyl ethyl ketone, carbon disulfide, isobutanol, and pyridine, benzene, 2-ethoxyethanol, and 2-nitropropane; all spent solvent mixtures/blends containing, before use, a total of 10 percent or more (by volume) of one or more of the above nonhalogenated solvents or those solvents listed in F001, F002 or F004; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.||(I,T)|
|F006||Wastewater treatment sludges from electroplating operations, except from the following processes: (1) sulfuric acid anodizing of aluminum; (2) tin plating on carbon steel; (3) zinc plating (segregated basis) on carbon steel; (4) aluminum or zinc-aluminum plating on carbon steel; (5) cleaning/stripping associated with tin, zinc and aluminum plating on carbon steel; and (6) chemical etching and milling of aluminum.||(T)|
|F007||Spent cyanide plating bath solutions from electroplating operations.||(R,T)|
|F008||Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process.||(R,T)|
|F009||Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process.||(R,T)|
|F010||Quenching bath residues from oil baths from metal heat treating operations where cyanides are used in the process.||(R,T)|
|F011||Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations.||(R,T)|
|F012||Quenching wastewater treatment sludges from metal heat treating operations where cyanides are used in the process.||(T)|
|F019||Wastewater treatment sludges from the chemical conversion coating of aluminum except from zirconium phosphating in aluminum can washing when such phosphating is an exclusive conversion coating process. Wastewater treatment sludges 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 wastes are not placed on the land prior to shipment to a landfill for disposal and are either: disposed in a municipal or industrial landfill unit that is equipped with at least a single clay liner and is permitted, licensed or otherwise authorized by the state; or disposed in a landfill unit subject to, or otherwise meeting, the landfill requirements in Parts 360 and 363 of this Title and sections 373-2.15(c) and 373-3.14(j) of this Title. For the purposes of this listing, motor vehicle manufacturing is defined in clause (2)(iv)(a) of this subdivision, clause (2)(iv)(b) of this subdivision describes the recordkeeping requirements for motor vehicle manufacturing facilities.||(T)|
|F020||Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tri- or tetrachlorophenol, or of intermediates used to produce their pesticide derivatives. (This listing does not include wastes from the production of hexachlorophene from highly purified 2,4,5-trichlorophenol.)||(H)|
|F02I||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, component in a formulating process) of tri- and tetra-chlorophenols. (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 clean-out wastes, from the production of certain chlorinated aliphatic hydrocarbons by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. (This listing does not include wastewaters, wastewater treatment sludges, spent catalysts, and wastes listed in subdivision [b] or [c] of this section.)||(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 formulation 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 EPA hazardous waste numbers F020, F021, F022, F023, F026 and F027.||(T)|
|F032||Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that currently use or have previously used chlorophenolic formulations (except potentially cross-contaminated wastes that have had the F032 waste code deleted in accordance with subdivision [f] of this section or potentially cross-contaminated wastes that are otherwise currently regulated as hazardous wastes [i.e., F034 or F035], 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 and/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 and/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 frorn wood preserving processes that use creosote and/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, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges generated in aggressive biological treatment units as defined in subparagraph (2)(ii) of this subdivision (including sludges generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and K051 wastes are not included in this listing. This listing does include residuals generated from processing or recycling oil-bearing hazardous secondary materials excluded under section 371.1(e)(1)(xii)(a) of this Part, if those residuals are to be disposed of.||(T)|
|F038||Petroleum refinery secondary (emulsified) oil/water/solids separation sludge; any sludge and/or float generated from the physical and/or chemical separation of oil/water/solids in process wastewaters and oily cooling wastewaters from petroleum refineries. Such wastes include, but are not limited to, all sludges and floats generated in: induced air flotation (IAF) units, tanks and impoundments, and all sludges generated in DAF units. Sludges generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges and floats generated in aggressive biological treatment units as defined in subparagraph (2)(ii) of this subdivision (including sludges and floats generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and F037, K048, and K051 wastes are not included in this listing.||(T)|
|F039||Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one restricted waste classified as hazardous under this section. (Leachate resulting from the disposal of one or more of the following EPA hazardous wastes and no other hazardous waste retains its EPA hazardous waste number(s): F020, F021, F022, F026, F027, and/or F028.)||(T)|
* (I,T) should be used to specify mixtures that are ignitable and contain toxic constituents.
(2) Listing specific definitions:
(i) For the purposes of the F037 and F038 listings, oil/water/solids is defined as oil and/or water and/or solids.
(a) For the purposes of the F037 and F038 listings, aggressive biological treatment units are defined as units which 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:
(1) the units employ a minimum of six hp per million gallons of treatment volume; and
(2) either the hydraulic retention time of the unit is no longer than five days; or
(3) 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 and disposal facilities have the burden of proving that their sludges are exempt from listing as F037 and F038 wastes under this definition. Generators and treatment, storage and disposal facilities must maintain, in their operating or other onsite records, documents and data sufficient to prove that:
(1) the unit is an aggressive biological treatment unit as defined in this subparagraph; and
(2) the sludges sought to be exempted from the definitions of F037 and/or F038 were actually generated in the aggressive biological treatment unit.
(a) For the purposes of 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 purposes of the F038 listing:
(1) 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
(2) floats are considered to be generated at the moment they are formed in the top of the unit.
(iv) For the purposes of the F019 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/utility vehicles (including light duty vans, pick-up trucks, minivans, and sport utility vehicles). Facilities must be engaged in manufacturing complete vehicles (body and chassis or unibody) or chassis only.
(b) Generators must maintain in their on-site records documentation and information sufficient to prove that the wastewater treatment sludges to be exempted from the F019 listing meet the conditions of the listing. These records must include: the volume of waste generated and disposed of offsite; documentation showing when the waste volumes were generated and sent offsite; the name and address of the receiving facility; and documentation confirming receipt of the waste by the receiving facility. Generators must maintain these records on-site for no less than three years. The retention period for the records is automatically extended during the course of any enforcement action or as requested by the department.
(c) Hazardous wastes from specific sources. (1) The following solid wastes are listed hazardous waste from specific sources unless excluded under section 370.3(a) and (c) of this Title and listed in Appendix 24, infra:
|waste number||Hazardous waste||code|
|K001||Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote and/or pentachlorophenol.||(T)|
|K002||Wastewater treatment sludge from the production of chrome yellow and orange pigments.||(T)|
|K003||Wastewater treatment sludge from the production of molybdate orange pigments.||(T)|
|K004||Wastewater treatment sludge from the production of zinc yellow pigments.||(T)|
|K005||Wastewater treatment sludge from the production of chrome green pigments.||(T)|
|K006||Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous and hydrated).||(T)|
|K007||Wastewater treatment sludge from the production of iron blue pigments.||(T)|
|K008||Oven residue from the production of chrome oxide green pigments.||(T)|
|K009||Distillation bottoms from the production of acetaldehyde from ethylene.||(T)|
|K010||Distillation side cuts from the production of acetaldehyde from ethylene.||(T)|
|K011||Bottom stream from the wastewater stripper in the production of acrylonitrile.||(R,T)|
|K013||Bottom stream from the acetonitrile column in the production of acrylonitrile.||(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 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)|
|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-trichloethane.||(T)|
|K029||Waste from the product steam stripper in 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)|
|K085||Distillation or fractionation column bottoms from the production of chlorobenzenes.||(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)|
|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)|
|K103||Process residues from aniline extraction from the production of aniline.||(T)|
|K104||Combined wastewater streams generated from nitrobenzene/aniline production.||(T)|
|K105||Separated aqueous stream from the reactor product washing step in the production of chlorobenzene.||(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 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)|
|K149||Distillation bottoms from the production of alpha- (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 alpha- (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 alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.||(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||Bag house dusts and filter/separation solids form the production of carbamates and arbamoyl 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 and K126.)||(R,T)|
|K174||Wastewater treatment sludges from the production of ethylene dicloride 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: (i) they are disposed of in a subtitle C or non-hazardous landfill licensed or permitted by the State or Federal government; (ii) they are not otherwise placed on the land prior to final disposal; and (iii) 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. Respondents in any action brought to enforce the requirements of subtitle C must, upon a showing by the government that the respondent managed wastewater treatment sludges from the production of vinyl chloride monomer or ethylene dichloride, demonstrate that they meet the terms of the exclusion set forth above. In doing so, they must provide appropriate documentation (e.g., contracts between the generator and the landfill owner/operator, invoices documenting delivery of waste to landfill, etc.) that the terms of the exclusion were met.||(T)|
|K175||Wastewater treatment sludges from the production of vinyl chloride monomer using mercuric chloride catalyst in an acetylene-based process.||(T)|
|K181||Nonwastewaters from the production of dyes and/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 paragraph (3) of this subdivision, that are equal to or greater than the corresponding paragraph (3) levels, as determined on a calendar year basis. These wastes will not be hazardous if the nonwastewaters are: (i) disposed in a landfill permitted under Part 360 of this Title or if out of state disposed in a 40 CFR subtitle D landfill unit subject to the design criteria in 40 CFR 258.40, as incorporated by reference in section 370.1(e) of this Title; (ii) disposed in a Part 373 landfill unit subject to either sections 373-2.14 or 373-3.14(j) of this Title or if out of state disposed in a 40 CFR subtitle C landfill unit subject to either 40 CFR 264.301 or 40 CFR 265.301, as incorporated by reference in section 370.1(e) of this Title; (iii) if out of state, disposed in other 40 CFR subtitle D landfill units that meet the design criteria in 40 CFR 258.40, 264.301, or 265.301 as incorporated by reference in section 370.1(e) of this Title; or (iv) treated in a combustion unit that is permitted under Part 373 or 40 CFR subtitle C, as incorporated by reference in section 370.1(e) of this Title, or an on-site combustion unit that is permitted under the Clean Air Act at 40 CFR parts 60, 61, or 63, as incorporated by reference by section 200.10 of this Title. For the purposes of this listing, dyes and/or pigments production is defined in subparagraph (2)(i) of this subdivision. Paragraph (4) of this subdivision describes the process for demonstrating that a facility’s nonwastewaters are not K181. This listing does not apply to wastes that are otherwise identified as hazardous under section 371.3(b),(c), (d) and (e) of this Part and subdivisions (b), (c) and (d) of this section, at the point of generation. Also, the listing does not apply to wastes generated before any annual mass loading limit is met.||(T)|
|K071||Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used.||(T)|
|K073||Chlorinated hydrocarbon waste from the steps of the diaphragm cell process using graphite anodes in chlorine production.||(T)|
|K106||Wastewater treatment sludges from the mercury cell process in chlorine production.||(T)|
|K031||By-product salts generated in the production of MSMA and cacodylic acid.||(T)|
|K032||Wastewater treatment sludge from the production of chlordane.||(T)|
|K033||Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane.||(T)|
|K034||Filter solids from the filtration of hexachloro-cyclopentadiene 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 diethylphos-phorodithioic 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)|
|K042||Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production 2,4,5-T.||(T)|
|K043||2,6-Dichlorophenol waste from the production of 2,4-D.||(T)|
|K097||Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.||(T)|
|K098||Untreated process wastewater from the production of toxaphene.||(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)|
|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, 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)|
|K044||Wastewater treatment sludges from the manufacturing and processing of explosives.||(R)|
|K045||Spent carbon from the treatment of wastewater containing explosives.||(R)|
|K046||Wastewater treatment sludges from the manufacturing, formulation and loading of lead-based initiating compounds.||(T)|
|K047||Pink/red water from TNT operations.||(R)|
|K048||Dissolved air flotation (DAF) float from the petroleum refining industry.||(T)|
|K049||Slop oil emulsion solids from the petroleum refining industry.||(T)|
|K050||Heat exchanger bundle cleaning sludge from the petroleum refining industry.||(T)|
|K051||API separator sludge from the petroleum refining industry.||(T)|
|K052||Tank bottoms (leaded) from the petroleum refining industry.||(T)|
|K169||Crude oil storage tank sediment from petroleum refining operations.||(T)|
|K170||Clarified slurry oil tank sediment and/or in-line filter/separation solids from petroleum refining operation.||(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:|
|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).||(C,T)|
|K088||Spent potliners from primary aluminum reduction.||(T)|
|K069||Emission control dust/sludge from secondary lead smelting, except sludge generated from secondary acid scrubber systems.||(T)|
|K100||Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting.||(T)|
|K084||Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.||(T)|
|K101||Distillation tar residues from the distillation of aniline-based compounds in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.||(T)|
|K102||Residue from the use of activated carbon for decolorization in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.||(T)|
|K086||Solvent washes and sludges, caustic washes and sludges, or water washes and sludges from cleaning tubs and equipment used in the formulation of ink from pigments, driers, soaps, and stabilizers containing chromium and lead.||(T)|
|K060||Ammonia still lime sludge from coking operations.||(T)|
|K087||Decanter tank tar sludge from coking operations.||(T)|
|K141||Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the production of coke from coal or the recovery of coke by-products produced from coal. This listing does not include K087 (decanter tank tar sludges from coking operations).||(T)|
|K142||Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal.||(T)|
|K143||Process residues from the recovery of light oil, including, but not limited to, those generated in stills, decanters, and wash oil recovery units from the recovery of coke by-products produced from coal.||(T)|
|K144||Wastewater sump residues from light oil refining, including, but not limited to, intercepting or contamination sump sludges from the recovery of coke by-products produced from coal.||(T)|
|K145||Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal.||(T)|
|K147||Tar storage tank residues from coal tar refining.||(T)|
|K148||Residues from coal tar distillation, including but not limited to, still bottoms.||(T)|
(2) Listing specific definitions:
(i) For purposes of the K181 listing, dyes and/or pigments production is defined to include manufacture of the following product classes: dyes, pigments, or FDA certified colors that are classified as azo, triarylmethane, perylene or anthraquinone classes. Azo products include azo, monoazo, diazo, triazo, polyazo, azoic, benzidine, and pyrazolone products. Triarylmethane products include both triarylmethane and triaphenylmethane products. Wastes that are not generated at a dyes and/or pigments manufacturing site, such as wastes from the offsite use, formulation, and packaging of dyes and/or pigments, are not included in the K181 listing.
(3) K181 listing levels. Nonwastewaters containing constituents in amounts equal to or exceeding the following levels during any calendar year are subject to the K181 listing, unless the conditions in the K181 listing are met.
|Constituent||Chemical abstracts No.||Mass levels (kg/yr)|
(4) Procedures for demonstrating that dyes and/or pigment nonwastewaters are not K181. The procedures described in subparagraphs (4)(i) through (4)(iii) and (4)(v) of this subdivision establish when nonwastewaters from the production of dyes/pigments would not be hazardous (these procedures apply to wastes that are not disposed in landfill units or treated in combustion units as specified in paragraph (1) of this subdivision). If the nonwastewaters are disposed in landfill units or treated in combustion units as described in paragraph (1) of this subdivision, then the nonwastewaters are not hazardous. In order to demonstrate that it is meeting the landfill disposal or combustion conditions contained in the K181 listing description, the generator must maintain documentation as described in subparagraph (4)(iv) of this subdivision.
(i) Determination based on no K181 constituents. Generators that have knowledge (e.g., knowledge of constituents in wastes based on prior sampling and analysis data and/or information about raw materials used, production processes used, and reaction and degradation products formed) that their wastes contain none of the K181 constituents (see paragraph  of this subdivision) can use their knowledge to determine that their waste is not K181. The generator must document the basis for all such determinations on an annual basis and keep each annual documentation for three years.
(ii) Determination for generated quantities of 1,000 MT/yr or less for wastes that contain K181 constituents. If the total annual quantity of dyes and/or pigment nonwastewaters generated is 1,000 metric tons or less, the generator can use knowledge of the wastes (e.g., knowledge of constituents in wastes based on prior analytical data and/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 paragraph (3) of this subdivision. To make this determination, the generator must:
(a) Each year document the basis for determining that the annual quantity of nonwastewaters expected to be generated will be less than 1,000 metric tons.
(b) Track the actual quantity of nonwastewaters generated from January 1 through December 31 of each year. If, at any time within the year, the actual waste quantity exceeds 1,000 metric tons, the generator must comply with the requirements of subparagraph (4)(iii) of this subdivision for the remainder of the year.
(c) Keep a running total of the K181 constituent mass loadings over the course of the calendar year.
(d) Keep the following records on site for the three most recent calendar years in which the hazardous waste determinations are made:
(1) The quantity of dyes and/or pigment nonwastewaters generated.
(2) The relevant process information used.
(3) The calculations performed to determine annual total mass loadings for each K181 constituent in the nonwastewaters during the year.
(iii) Determination for generated quantities greater than 1,000 MT/yr for wastes that contain K181 constituents. If the total annual quantity of dyes and/or pigment nonwastewaters generated is greater than 1,000 metric tons, the generator must perform all of the steps described in clauses ([athrough [k) of this subparagraph) in order to make a determination that its waste is not K181.
(a) Determine which K181 constituents (see paragraph  of this subdivision) are reasonably expected to be present in the wastes based on knowledge of the wastes (e.g., based on prior sampling and analysis data and/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 or sampling and analysis procedures to determine the level of this constituent in the wastes. For determinations based on use of knowledge, the generator must comply with the procedures for using knowledge described in subparagraph (ii) of this paragraph and keep the records described in clause (ii)(d) of this paragraph. For determinations based on sampling and analysis, the generator must comply with the sampling and analysis and recordkeeping requirements described below in this subdivision.
(c) Develop a waste sampling and analysis plan (or modify an existing plan) to collect and analyze representative waste samples for K181 constituents reasonably expected to be present in the wastes. At a minimum, the plan must include:
(1) a discussion of the number of samples needed to characterize the wastes fully;
(2) the planned sample collection method to obtain representative waste samples;
(3) a discussion of how the sampling plan accounts for potential temporal and spatial variability of the wastes;
(4) a detailed description of the test methods to be used, including sample preparation, clean up (if necessary), and determinative methods.
(d) Collect and analyze samples in accordance with the waste sampling and analysis plan.
(1) The sampling and analysis must be unbiased, precise, and representative of the wastes.
(2) 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 paragraph (3) of this subdivision.
(e) Record the analytical results.
(f) Record the waste quantity represented by the sampling and analysis results.
(g) Calculate constituent-specific mass loadings (product of concentrations and waste quantity).
(h) Keep a running total of the K181 constituent mass loadings over the course of the calendar year.
(i) Determine whether the mass of any of the K181 constituents listed in paragraph (3) of this subdivision generated between January 1 and December 31 of any year is below the K181 listing levels.
(j) Keep the following records on site for the three most recent calendar years in which the hazardous waste determinations are made:
(1) The sampling and analysis plan.The calculations performed to determine annual mass loadings.
(2) The sampling and analysis results (including QA/QC data).
(3) The quantity of dyes and/or pigment nonwastewaters generated.
(4) The calculations performed to determine annual mass loadings.
(k) Nonhazardous waste determinations must be conducted annually to verify that the wastes remain nonhazardous.
(1) The annual testing requirements are suspended after three consecutive successful annual demonstrations that the wastes are nonhazardous. The generator can then use knowledge of the wastes to support subsequent annual determinations.
(2) 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.
(3) If the annual testing requirements are suspended, the generator must keep records of the process knowledge information used to support a nonhazardous determination. If testing is reinstated, a description of the process change must be retained.
(iv) Recordkeeping for the landfill disposal and combustion exemptions. For the purposes of meeting the landfill disposal and combustion condition set out in the K181 listing description, 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 meets the landfill design standards set out in the listing description, or was treated in combustion units as specified in the listing description.
(v) Waste holding and handling. During the interim period, from the point of generation to completion of the hazardous waste determination, the generator is responsible for storing the wastes appropriately. If the wastes are determined to be hazardous and the generator has not complied with the requirements of Parts 370 through 374-4 and Part 376 of this Title during the interim period, the generator is in violation and could be subject to an enforcement action for improper management.
(d) 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 371.1(c)(2)(i) of this Part, 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 the 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:
(1) any commercial chemical product, or manufacturing chemical intermediate having the generic name listed in paragraph (5) or (6) of this subdivision;
(2) any off-specification commercial chemical product or manufacturing chemical intermediate which, if it met specifications, would have the generic name listed in paragraph (5) or (6) of this subdivision;
(3) any residue remaining in a container or inner liner removed from a container that has been used to hold any commercial chemical product or manufacturing chemical intermediate having the generic names listed in paragraph (5) or (6) of this subdivision, or any residue remaining in a container or inner liner removed from a container that has been used to hold any off-specification chemical product or manufacturing chemical intermediate, which if it met specifications, would have the generic name listed in paragraph (5) or (6) of this subdivision, unless the container is empty as defined in section 371.1(h)(2) of this Part.
Unless the residue is being beneficially used or reused, or legitimately recycled or reclaimed, or being accumulated, stored, transported or treated prior to such use, reuse, recycling or reclamation, EPA and the department consider the residue to be intended for discard, and thus, a hazardous waste. An example of a legitimate reuse of the residue would be where 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 where the drum is sent to a drum reconditioner who reconditions the drum but discards the residues. All waste resulting from the rinsing or cleansing of the container or inner liner, by a nonaqueous solvent, is a hazardous waste. All waste resulting from the aqueous rinsing or cleansing of the container or inner liner is a hazardous waste unless exempt pursuant to section 371.1(d)(1)(ii)(d)(4).
(4) 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 paragraph (5) or (6) of this subdivision, 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 which, if it met specifications, would have the generic name listed in paragraph (5) or (6) of this subdivision.
The phrase “commercial chemical product or manufacturing chemical intermediate having the generic name listed in. . .” refers to a chemical substance which is manufactured or formulated for commercial or manufacturing use which 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 paragraph (5) or (6). Where a manufacturing process waste is deemed to be a hazardous waste because it contains a substance listed in paragraph (5) or (6), such waste will be listed in either subdivision (b) or (c) of this section, or will be identified as a hazardous waste by the characteristics set forth in section 371.3 of this Part.
(5) Acute hazardous waste. The commercial chemical products, manufacturing chemical intermediates or off-specification commercial chemical products or manufacturing chemical intermediates referred to in paragraphs (1) through (4) of this subdivision, are identified as acute hazardous wastes (H) and are subject to the small quantity exclusion defined in section 371.1(f)(5) of this Part.
For the convenience of the regulated community the primary hazardous properties of the materials have been indicated by the letters T [Toxicity], and R [Reactivity]. Absence of a letter indicates that the compound only is listed for acute toxicity.
These wastes and their corresponding EPA hazardous waste numbers are:
|P058||62-74-8||Acetic acid, fluoro-, sodium salt|
|P006||20859-73-8||Aluminum phosphide (R,T)|
|P009||131-74-8||Ammonium picrate (R)|
|P099||506-61-6||Argentate (1-), bis (cyano-C)-, potassium|
|P010||7778-39-4||Arsenic acid H3AsO4|
|P012||1327-53-3||Arsenic oxide As2 O3|
|P011||1303-28-2||Arsenic oxide As2O5|
|P036||696-28-6||Arsonous dichloride, phenyl-|
|P042||51-43-4||1,2-Benzenediol, 4-[1-hydroxy-2-(methylamino) ethyl]-, (R)-|
|P046||122-09-8||Benzeneethanamine, alpha, alpha-dimethyl-|
|P127||1563-66-2||7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-, methylcarbamate|
|P188||57-64-7||Benzoic acid, 2-hydroxy-, compd. w/(3aS-cis)-1,2,3a, 8,8a- hexahydro-1,3a,8-trimethylpyrrolo[2,3-b]indol-5-yl methycarbamate ester (1:1)|
|P001||181-81-2||2H-1-Benzopyran-2-one, 4-hydroxy-3- (3-oxo-1-phenylbutyl)-1, & salts, when present at concentrations greater than 0.3 percent|
|P045||39196-18-4||2-Butanone, 3,3-dimethyl- 1-(methylthio)-, O-[(methylamino) carbonyl] oxime|
|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-5yl ester|
|P190||1129-41-5||Carbamic acid, methyl-, 3-methylphenyl ester|
|P029||544-92-3||Copper cyanide Cu(CN)|
|P030||Cyanides (soluble cyanide salts), not otherwise specified|
|P033||506-77-4||Cyanogen chloride (CN)Cl|
|P040||297-97-2||O,O-Diethyl O-pyrazinyl phosphorothioate|
|P004||309-00-2||1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10- hexa- chloro-1,4,4a,5,8,8a,- hexahydro-, (1alpha, 4alpha, 4abeta, 5alpha, 8alpha, 8abeta) -|
|P060||465-73-6||1,4,5,8- Dimethanonaphthalene, 1,2,3,4,10, 10-hexa-chloro- 1,4,4a,5,8,8a- hexahydro-, (1alpha, 4alpha, 4abeta, 5beta, 8beta, 8abeta) -|
|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-, (1-a-alpha, 2beta, 2aalpha, 3beta, 6beta, 6aalpha, 7beta, 7aalpha) -|
|P051||172-20-8||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-, (1aalpha, 2beta, 2abeta, 3alpha, 6alpha, 6abeta, 7beta, 7aalpha)-, & metabolites|
|P047||1534-52-1||4,6-Dinitro-o-cresol, & salts|
|P111||107-49-3||Diphosphoric acid, tetraethyl ester|
|P051||72-20-8||Endrin, & metabolites|
|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|
|P058||62-74-8||Fluoroacetic acid, sodium salt|
|P065||628-86-4||Fulminic acid, mercury (2+) salt (R,T)|
|P065||628-86-4||Mercury fulminate (R,T)|
|P198||233422-53-9||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]-|
|P050||115-29-7||6,9-Methano-2,4, 3-benzodioxathiepin, 6,7,8,9,10,10- hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide|
|P059||76-44-8||4, 7-Methano-lH-indene, 1,4,5,6,7,8,8-heptachloro- 3a,4,7,7a-tetrahydro-|
|P073||13463-39-3||Nickel carbonyl Ni(CO)4, (T-4)-|
|P074||557-19-7||Nickel cyanide Ni(CN)2|
|P075||154-11-5||Nicotine, & salts|
|P076||10102-43-9||Nitrogen oxide NO|
|P078||10102-44-0||Nitrogen oxide NO2|
|P087||20816-12-0||Osmium oxide OsO4, (T-4)-|
|P088||145-73-3||7-Oxabicyclo[2.2.l]heptane-2, 3-dicarboxylic acid|
|P034||131-89-5||Phenol, 2-cyclohexyl-4, 6-dinitro-|
|P128||315-18-4||Phenol, 4-(dimethylamino)-3,5-dimethyl-,methylcarbamate (ester)|
|P201||2631-37-0||Phenol, 3-methyl-5-(1-methylethyl)-,methyl carbamate|
|P047||1534-52-1||Phenol, 2-methyl-4,6-dinitro-, & salts|
|P020||88-85-7||Phenol, 2-(1-methylpropyl)-4, 6-dinitro-|
|P009||131-74-8||Phenol, 2,4,6-trinitro-, ammonium salt (R)|
|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|
|P098||151-50-8||Potassium cyanide K(CN)|
|P099||506-61-6||Potassium silver cyanide|
|P070||116-06-3||Propanal, 2-methyl-2- (methylthio)-, O- [(methylamino)carbonyl]oxime|
|P203||1646-88-4||Propanal, 2-methyl-2-(methyl-sulfonyl)-, 0-[(methylamino)carbonyl] oxime|
|P081||55-63-0||1,2,3-Propanetriol, trinitrate (R)|
|P075||154-11-5||Pyridine, 3-(1-methyl- 2-pyrrolidinyl)-, (S)-, & salts|
|P204||57-47-6||Pyrrolo[2,3-b]indol-5-ol, 1,2,3,3a,8,8a-hexahydro-1,3a, 8-trimethyl-, methylcarbamate (ester), (3aS-cis)-|
|P114||12039-52-0||Selenious acid, dithallium(1 +) salt|
|P104||506-64-9||Silver cyanide Ag(CN)|
|P106||143-33-9||Sodium cyanide Na(CN)|
|P108||157-24-9||Strychnidin-10-one, & salts|
|P108||157-24-9||Strychnine, & salts|
|P115||7446-18-6||Sulfuric acid, dithallium(1 +) salt|
|P062||757-58-4||Tetraphosphoric acid, hexaethyl ester|
|P113||1314-32-5||Thallium oxide Tl2O3|
|P109||3689-24-5||Thiodiphosphoric acid, tetraethyl ester|
|P049||541-53-7||Thioimidodicarbonic diamide [(H2N)C(S)] 2NH|
|P119||7803-55-6||Vanadic acid, ammonium salt|
|P120||1314-62-1||Vanadium oxide V2O5|
|P001||181-81-2||Warfarin, & salts, when present at concentrations greater than 0.3 percent|
|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)|
____ 1CAS number given for parent compound only.
(6) The commercial chemical products, manufacturing chemical intermediates, or off- specification commercial chemical products referred to in paragraphs (1) through (4) of this subdivision, are identified as toxic waste (T) unless otherwise designated and are subject to the small quantity generator exclusion defined in section 371.1(f)(1) and (7) of this Part. (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]. Absence of a letter indicates that the compound is only listed for toxicity. These wastes and their corresponding EPA hazardous waste numbers are:
|U240||194-75-7||Acetic acid, (2,4-dichlorophenoxy)-, salts & 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)-|
|U006||75-36-5||Acetyl chloride (C,R,T)|
|U008||79-10-7||Acrylic acid (I)|
|U136||75-60-5||Arsinic acid, dimethyl-|
|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,2,8a,8b-hexahydro- 8a- methoxy-5-methyl-, [1aS- (1aalpha, 8beta, 8aalpha,8balpha)]-|
|U157||56-49-5||Benz [j] aceanthrylene, 1,2-dihydro-3-methyl-|
|U192||23950-58-5||Benzamide, 3, 5-dichloro-N- (1,1-dimethyl-2-propynyl) -|
|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)-|
|U158||101-14-4||Benzenamine, 4,4′ -methylenebis [2-chloro-|
|U222||636-21-5||Benzenamine, 2-methyl-, hydrochloride|
|U038||510-15-6||Benzeneacetic acid, 4-chloro-alpha-(4-chlorophenyl)-alpha- hydroxy-, ethyl ester|
|U035||305-03-3||Benzenebutanoic acid, 4-[bis (2- chloroethyl) amino] -|
|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|
|U060||72-54-8||Benzene, 1,1′-(2,2-dichloroethylidene) bis[4-chloro-|
|U223||26471-62-5||Benzene, 1, 3-diisocyanatomethyl- (R, T)|
|U056||110-82-7||Benzene, hexahydro- (I)|
|U055||98-82-8||Benzene, (1-methylethyl)- (I)|
|U020||98-09-9||Benzenesulfonic acid chloride (C,R)|
|U020||98-09-9||Benzenesulfonyl chloride (C,R)|
|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-|
|U202||81-07-2||1,2-Benzisothiazol- 3(2H)-one, 1,1-dioxide, & salts|
|U203||94-59-7||1, 3-Benzodioxole, 5-(2-propenyl)-|
|U141||120-58-1||1, 3-Benzodioxole, 5-(1-propenyl)-|
|U278||22781-23-3||1,3-Benzodioxol-4-ol, 2,2-dimethyl-, methyl carbamate|
|U248||181-81-2||2H-1-Benzopyran-2-one, 4-hydroxy-3- (3-oxo-1- phenyl- butyl)-, & salts, when present at concentrations of 0.3 percent or less|
|U030||101-55-3||4-Bromophenyl phenyl ether|
|U128||87-68-3||1, 3-Butadiene, 1,1,2,3,4,4-hexachloro-|
|U160||1338-23-4||2-Butanone, peroxide (R,T)|
|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- [1alpha(Z), 7(2S*,3R*),7aalpha]]-|
|U031||71-36-3||n-Butyl alcohol (I)|
|U238||51-79-6||Carbamic acid, ethyl ester|
|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|
|U409||23564-05-8||Carbamic acid, [1,2-phenylenebis (iminocarbonothioyl)]bis-, dimethyl ester|
|U373||122-42-9||Carbamic acid, phenyl-, 1-methylethyl ester|
|U178||615-53-2||Carbamic acid, methylnitroso-, ethyl ester|
|U097||79-44-7||Carbamic chloride, dimethyl-|
|U114||111-54-6||Carbamodithioic acid, 1,2-ethanediylbis-, salts & 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|
|U215||6533-73-9||Carbonic acid, dithallium(1+) salt|
|U156||79-22-1||Carbonochloridic acid, methyl ester (I,T)|
|U033||353-50-4||Carbon oxyfluoride (R,T)|
|U036||57-74-9||Chlordane, alpha & gamma isomers|
|U042||110-75-8||2-Chloroethyl vinyl ether|
|U046||107-30-2||Chloromethyl methyl ether|
|U032||13765-19-0||Chromic acid H2CrO4, calcium salt|
|U052||1319-77-3||Cresol (Cresylic acid)|
|U246||506-68-3||Cyanogen bromide (CN)Br|
|U197||106-51-4||2, 5-Cyclohexadiene- 1,4-dione|
|U129||58-89-9||Cyclohexane, 1,2,3,4,5,6-hexachloro-, (1alpha, 2alpha, 3beta, 4alpha, 5alpha, 6beta) -|
|U130||77-47-4||1, 3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro-|
|U240||194-75-7||2,4-D, salts & esters|
|U085||1464-53-5||1,2:3,4-Diepoxybutane (I, T)|
|U395||5952-26-1||Diethylene glycol, dicarbamate|
|U087||3288-58-2||O,O-Diethyl S-methyl dithiophosphate|
|U394||30558-43-1||Ethanimidothioic acid, 2-(dimethylamino)-N-hydroxy-2-oxo-,methyl ester|
|U410||59669-26-0||Ethanimidothioic acid, N,N'-[thiobis[(methylimino)carbonyloxy]]bis-,dimethyl ester|
|U155||91-80-5||1,2-Ethanediamine, N,N-dimethyl-N′ -2-pyridinyl- N′- (2-thienylmethyl) -|
|U024||111-91-1||Ethane, 1,1′ - [methylenebis(oxy)]bis[2-chloro-|
|U208||630-20-6||Ethane, 1,1,1,2- tetrachloro-|
|U209||79-34-5||Ethane, 1,1,2,2- tetrachloro-|
|U173||1116-54-7||Ethanol, 2,2′- (nitrosoimino)bis-|
|U395||5952-26-1||Ethanol, 2,2'-oxybis-, dicarbamate|
|U079||156-60-5||Ethene, 1,2-dichloro-, (E)-|
|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||1111-54-6||Ethylenebisdithiocarbamic acid, salts & esters|
|U359||110-80-5||Ethylene glycol monoethyl ether|
|U115||75-21-8||Ethylene oxide (I,T)|
|U123||64-18-6||Formic acid (C,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] -|
|U163||70-25-7||Guanidine, N-methyl- N′-nitro-N-nitroso-|
|U134||7664-39-3||Hydrofluoric acid (C,T)|
|U134||7664-39-3||Hydrogen fluoride (C,T)|
|U135||7783-06-4||Hydrogen sulfide H2S|
|U096||80-15-9||Hydroperoxide, 1-methyl-1-phenylethyl- (R)|
|U137||193-39-5||Indeno [1,2, 3-cd] pyrene|
|U140||78-83-1||Isobutyl alcohol (I,T)|
|U092||124-40-3||Methanamine, N-methyl- (I)|
|U045||74-87-3||Methane, chloro- (I,T)|
|U119||62-50-0||Methanesulfonic acid, ethyl ester|
|U036||57-74-9||4, 7-Methano-lH-indene, 1,2,4,5,6,7,8,8-octachloro- 2,3,3a,4,7,7a-hexahydro-|
|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-|
|U154||67-56-1||Methyl alcohol (I)|
|U045||74-87-3||Methyl chloride (I,T)|
|U156||79-22-1||Methyl chlorocarbonate (I,T)|
|U159||78-93-3||Methyl ethyl ketone (MEK) (I,T)|
|U160||1338-23-4||Methyl ethyl ketone peroxide (R,T)|
|U161||108-10-1||Methyl isobutyl ketone (I)|
|U162||80-62-6||Methyl methacrylate (I,T)|
|U059||20830-81-3||5,12-Naphthacenedione, 8-acetyl-10- [(3-amino-2,3,6-trideoxy) -alpha-L-lyxo-hexopyranosyl)oxy]-7,8,9,10-tetrahydro-6,8, 11-trihydroxy-1-methoxy-, (8S-cis)-|
|U236||72-57-1||2,7-Naphthalenedisulfonic acid, 3,3′-[(3,3′-dimethyl[l,l′-biphenyl]-4,4′-diyl) bis(azo)bis [5-amino-4-hydroxy]-, tetrasodium salt|
|U217||10102-45-1||Nitric acid, thallium(1 +) salt|
|U058||50-18-0||2H-1,3,2-Oxazaphosphorin- 2-amine, N,N-bis (2-chloroethyl) tetrahydro-, 2-oxide|
|U161||108-10-1||Pentanol, 4-methyl- (I)|
|U089||56-53-1||Phenol, 4,4′- (1,2-diethyl-1,2-ethenediyl)bis-, (E) -|
|U132||70-30-4||Phenol, 2,2′-methylenebis [3,4,6-trichloro-|
|U411||114-26-1||Phenol, 2-(1-methylethoxy)-, methylcarbamate|
|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-methylester|
|U189||1314-80-3||Phosphorus sulfide (R)|
|U110||142-84-7||1-Propanamine, N-propyl- (I)|
|U066||96-12-8||Propane, 1,2-dibromo- 3-chloro-|
|U171||79-46-9||Propane, 2-nitro- (I,T)|
|See F027||93-72-1||Propanoic acid, 2- (2,4,5-trichlorophenoxy)-|
|U235||126-72-7||1-Propanol, 2,3-dibromo-, phosphate (3:1)|
|U140||78-83-1||1-Propanol, 2-methyl- (I,T)|
|U243||1888-71-7||1-Propene, 1,1,2,3,3,3 -hexachloro-|
|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)|
|U237||66-75-1||2,4-(1H, 3H)-Pyrimidinedione, 5-[bis(2-chloroethyl)amino]-|
|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)|
|U103||77-78-1||Sulfuric acid, dimethyl ester|
|U189||1314-80-3||Sulfur phosphide (R)|
|See F027||58-90-2||2,3,4,6- Tetrachlorophenol|
|U215||6533-73-9||Thallium (I) carbonate|
|U216||7791-12-0||Thallium chloride TlCl|
|U217||10102-45-1||Thallium (I) nitrate|
|U244||137-26-8||Thioperoxydicarbonic diamide [(H2N)C(S)]2S2, tetramethyl-|
|U223||26471-62-5||Toluene diisocyanate (R,T)|
|U248||181-81-2||Warfarin, & salts, when present at concentrations of 0.3 percent or less|
|U200||50-55-5||Yohimban-16- carboxylic acid, 11,17-dimethoxy-18-[(3,4, 5-trimethoxybenzoyl)oxy]-, methyl ester, (3beta, 16beta, 17alpha, 18beta, 20alpha)-|
|U249||1314-84-7||Zinc phosphide Zn3P2, when present at concentrations of 10 percent or less|
____ 1CAS number given for parent compound only.
(e) Wastes containing polychlorinated biphenyls (PCBs).
(1) All solid wastes containing 50 parts per million (ppm) by weight (on a dry weight basis for other than liquid wastes) or greater of polychlorinated biphenyls (PCBs) are listed hazardous wastes, excluding small capacitors as defined in paragraph (3) of this subdivision and PCB articles drained in accordance with subparagraphs (2)(ii) and (iii) of this subdivision. PCB articles that contain less than 50 ppm PCBs are not regulated as hazardous waste. Oils in or from electrical equipment whose PCB concentration is unknown, except circuit breakers, reclosers and cable, must be assumed to contain between 50 and 500 ppm PCB and are listed hazardous waste. PCB and PCBs mean any chemical substance that is limited to the biphenyl molecule that has been chlorinated to varying degrees. Any chemical waste, combination of waste, or environmental media that contains less than 50 ppm PCBs are listed hazardous waste only as specifically provided in paragraph (2) of this subdivision. Wastes that may contain PCBs include dielectric fluids, contaminated solvents, waste oil, heat transfer fluids, hydraulic fluids, dredge spoils, and material contaminated as a result of spills. The hazardous code for these PCB wastes shall be toxic waste (T). Environmental media means naturally occurring, non-living substances, including soil, sediment, rock, groundwater, surface water, surface runoff, air, and only such animal and vegetable matters as may be incidentally contained therein (e.g., soil and water bacteria, underground roots, skeletal remains, etc.). These wastes shall have hazardous waste numbers assigned as follows:
|B001||PCB oil (concentrated) from transformers, capacitors, etc.|
|B002||Petroleum oil or other liquid containing 50 ppm or greater of PCBs, but less than 500 ppm PCBs. This includes oil from electrical equipment whose PCB concentration is unknown, except for circuit breakers, reclosers, rectifiers and cable.|
|B003||Petroleum oil or other liquid containing 500 ppm or greater of PCBs.|
|B004||PCB articles containing 50 ppm or greater of PCBs, but less than 500 ppm PCBs, excluding small capacitors. This includes oil-filled electrical equipment whose PCB concentration is unknown, except for circuit breakers, reclosers, rectifiers and cable.|
|B005||PCB articles, other than transformers, that contain 500 ppm or greater of PCBs, excluding small capacitors.|
|B006||PCB transformers. PCB transformers means any transformer that contains 500 ppm PCB or greater.|
|B007||Other PCB wastes, including contaminated soil, solids, sludges, clothing, rags and dredge material.|
|Note: PCBs are also regulated by 40 CFR part 761. A person must comply with both this Part and 40 CFR part 761 (see section 370.1[e] ot this Title).|
(2) Drained PCB articles.
(i) Except as provided in subparagraphs (ii) and (iii) of this paragraph, drained PCB articles containing at least 50 ppm PCBs are regulated as hazardous waste.
(ii) PCB articles, except capacitors, that contain between 50 and 500 ppm PCB, are no longer regulated as PCB listed hazardous waste provided that all free-flowing liquid has been drained from the article. The drained liquid is a listed hazardous waste, as is any solvent used for flushing.
(a) Hydraulic machines containing less than 1,000 ppm PCB are no longer regulated as PCB listed hazardous waste, provided that all free-flowing liquid has been drained from the hydraulic machine. The drained liquid is a liquid hazardous waste, as is any solvent used for flushing.
(b) Hydraulic machines containing 1,000 ppm PCB are no longer regulated as PCB listed hazardous waste, provided that all free-flowing liquid has been drained from the hydraulic machine, and the drained hydraulic machine is flushed with a solvent in which PCBs are readily soluble. The solvent to be used for flushing must contain less than 50 ppm PCB. The drained liquid and the solvent used for flushing are listed hazardous wastes.
(i) PCB article means any manufactured article, other than a PCB container, that contains PCBs and whose surface(s) has been in direct contact with PCBs. PCB article includes capacitors, transformers, electric motors, circuit breakers, reclosers, rectifiers, voltage regulators, switches (including sectionalizers and motor starters), electromagnets, cable, hydraulic machines, pumps, pipes, and any other manufactured item which is formed to a specific shape or design during manufacture, has end use function(s) dependent in whole or in part upon its shape or design during end use, and has either no change of chemical composition during its end use or only those changes of composition which have no commercial purpose separate from that of the PCB article.
(ii) Small capacitor means a capacitor which contains less than 1.36 kg (3 lb.) of dielectric fluid. The following assumptions may be used if the actual weight of the dielectric fluid is unknown. A capacitor whose total volume is less than 1,639 cubic centimeters (100 cubic inches) may be considered to contain less than 1.36 kg (3 lb.) of dielectric fluid and a capacitor whose total volume is more than 3,278 cubic centimeters (200 cubic inches) must be considered to contain more than 1.36 kg (3 lb.) of dielectric fluid. A capacitor whose volume is between 1,639 and 3,278 cubic centimeters may be considered to contain less than 1.36 (3 lb.) of dielectric fluid if the total weight of the capacitor is less than 4.08 kg (9 lb.).
(4) Testing procedures. The procedures in 40 CFR 761.60(g) (see section 370.1[e] of this Title) will be used to determine the concentration of PCBs, unless a petition for equivalent testing or analytical methods is submitted and approved per section 370.3 of this Title.
(f) Deletion of certain hazardous waste codes following equipment cleaning and replacement.
(1) 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 paragraphs (2) and (3) of this subdivision. These wastes may, however, continue to meet another hazardous waste listing description or may exhibit one or more of the hazardous waste characteristics.
(2) 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 ground water, surface water, or atmosphere.
(i) Generators shall do one of the following:
(a) prepare and follow an equipment replacement plan and clean equipment in accordance with this subdivision;
(b) prepare and follow an equipment replacement plan and replace equipment in accordance with this subdivision; or
(c) document cleaning and replacement in accordance with this subdivision, carried out after termination of use of chlorophenolic preservations.
(ii) Cleaning requirements.
(a) Prepare and sign a written equipment cleaning plan that describes:
(1) the equipment to be cleaned;
(2) how the equipment will be cleaned;
(3) the solvent to be used in cleaning;
(4) how solvent rinses will be tested; and
(5) how cleaning residues will be disposed.
(b) Equipment must be cleaned as follows:
(1) remove all visible residues from process equipment; and
(2) rinse process equipment with an appropriate solvent until dioxins and dibenzofurans are not detected in the final solvent rinse.
(c) Analytical requirements.
(1) rinses must be tested by using an appropriate method;
(2) not detected’ means at or below the following lower method calibration limits (MCLs): The 2,3,7,8-TCDD-based MCLB0.01 parts per trillion (ppt), sample weight of 1000 g, IS spiking level of 1 ppt, final extraction volume of 10-50 ΦL (microlitre). For other congenersBmultiply the values by 1 for TCDF/PeCDD/PeCDF, by 2.5 for HxCDD/HxCDF/HpCDD/HpCDF, and by 5 for OCDD/OCDF.
(d) The generator must manage all residues from the cleaning process as F032 waste.
(iii) Replacement requirements.
(a) Prepare and sign a written equipment replacement plan that describes:
(1) the equipment to be replaced;
(2) how the equipment will be replaced; and
(3) how the equipment will be disposed.
(b) The generator must manage the discarded equipment as F032 waste.
(iv) Documentation requirements.
(a) Document that previous equipment cleaning and/or replacement was performed in accordance with this subdivision and occurred after cessation of use of chlorophenolic preservatives.
(3) The generator must maintain the following records documenting the cleaning and replacement as part of the facility's operating record:
(i) the name and address of the facility;
(ii) formulations previously used and the date on which their use ceased in each process at the plant;
(iii) formulations currently used in each process at the plant;
(iv) the equipment cleaning or replacement plan;
(v) the name and address of any persons who conducted the cleaning and replacement;
(vi) the dates on which cleaning and replacement were accomplished;
(vii) the dates of sampling and testing;
(viii) a description of the sample handling and preparation techniques, including techniques used for extraction, containerization, preservation, and chain-of-custody of the samples;
(ix) a description of the tests performed, the date the tests were performed, and the results of the tests;
(x) the name and model numbers of the instrument(s) used in performing the tests;
(xi) QA/QC documentation; and
(xii) the following statement signed by the generator or an authorized representative:
“I certify under penalty of law that all process equipment required to be cleaned or replaced under subdivision (f) of this section 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.”
6 CRR-NY 371.4
Current through February 15, 2022
|End of Document|