Source: http://www.dec.ny.gov/regs/14898.html
Timestamp: 2014-04-24 10:05:45
Document Index: 30643421

Matched Legal Cases: ['art 371', 'art 371', 'art 371', 'art:\n371', '§371', 'arts 372', 'art 761', 'art 761', 'arts 373', 'arts 373', 'arts 373', 'art 370', 'art 370']

Part 371: Identification and Listing Of Hazardous Wastes - Page 2 - NYS Dept. of Environmental Conservation
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Part 371: Identification and Listing Of Hazardous Wastes - Page 2
[page 2 of 3] Pages in this Part:
371.4 - Lists of Hazardous Wastes
Appendix 19 - Representative Sampling Methods
Appendix 20 - Reserved
Appendix 21 - Reserved
Appendix 22 - Basis for Listing Hazardous Waste
§371.4 - Lists of Hazardous Wastes
(Note: 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.)
Ignitable Waste (I) Corrosive Waste (C) Reactive Waste (R) Toxicity Characteristic Waste (E) Acute Hazardous Waste (H) Toxic Waste (T)
(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 of this Title (see subdivision 370.1(e) of this Title).
(4) The following hazardous wastes listed in subdivisions (b) and (c) of this section are subject to the exclusion limits for acutely hazardous waste established in subdivision 371.1(f) of this Title: EPA Hazardous Waste Number F020, F021, F022, F023, F026, and F027.
(b) Hazardous waste from non-specific sources.
(1) The following solid wastes are listed hazardous wastes from non-specific sources unless they are excluded under sections 370.3(a) and (c) of this Title and listed in Appendix 24, infra:
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, 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, and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.
The following spent halogenated solvents: tetrachloroethylene, methylene chloride, trichloroethylene1,1,1-trichloroethane, chlorobenzene, 1,1,2-trichloro-1,2,2-trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane and 1,1,2-trichloroethane; before use, a total of ten 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.
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/blends containing, before use, only the above spent non-halogenated solvents; and all spent solvent mixtures/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, and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.
(I,T)*
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.
Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of 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.)
Waste (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.
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.
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 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.)
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.)
Waste (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.
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.)
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 371.4(f) 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.
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 371.4(b)(2)(ii) (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 371.1(e)(1)(xii)('a'), if those residuals are to be disposed of.
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 371.4(b)(2)(ii) (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.
Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one restricted waste classified as hazardous under section 371.4 of this Part. (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.)
(ii) ('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 6 hp per million gallons of treatment volume; and either ('2') the hydraulic retention time of the unit is no longer than 5 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.
(iii) ('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.
(c) Hazardous Wastes from specific sources.
The following solid wastes are listed hazardous waste from specific sources unless excluded under sections 370.3(a) and 370.3(c) of this Title and listed in Appendix 24.
Heavy ends from the distillation of vinyl chloride chloride monomer production.
Combined wastewater streams generated from nitrobenzene/aniline productions.
Spent filter cartridges from product purification from the production of1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
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.
Chlorinated hydrocarbon waste from the steps of the diaphragm cell process using graphite anodes in chlorine production.
Wastewater treatment sludges from the mercury cell process in chlorine production.
Filter cake from the filtration of diethylphos-phorodithioic acid in the production of phorate.
Heavy ends or distillation residues from the distillation of tetrachlorobenzene in theproduction of 2,4,5-T.
Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylene-bisdithiocarbamic acid and its salts.
Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithio-carbamic acid and its salts.
Spent pickle liquor generated by steel finishing operations of facilities within the iron and steel industry (SIC Code 331 and 332).
Surface impoundment solids contained in and dredged from surface impoundments at primary
Emission control dust or sludge from ferrochromium-silicon production.
Emission control dust/sludge from secondary lead smelting, except sludge generated from secondary acid scrubber systems.
(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 subparagraph 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:
(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 paragraphs (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 paragraphs (5) or (6) of this subdivision, unless the container is empty as defined in 371.1(h)(2).
(Note: 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 subclause 371.1(d)(l)(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-specifications 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.
(Note: 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 paragraphs (5) or (6). Where a manufacturing process was 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 paragraph 371.1(f)(5) of this Title.
(Note: 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:
Acetamide, N (aminothioxomethyl)-
Benzeneethanamine, alpha, alpha-dimethyl-
Benzoic acid, 2-hydroxy-, compd. w/ (3aS-cis)-1,2,3a,8,8a-hexahydro-1,3a,8-trimethylpyrrolo[2,3-b]indol-5-yl methylcarbamate ester (1:1)
2-Butanone,3, 3-dimethyl- 1-(methylthio)-,O-[(methylamino)carbonyl] oxime
Carbamic acid, dimethyl-, 3-methyl-1(1-methylethyl)-1H- pyrazol-5-yl ester.
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)-
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)-
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 aalpha,2beta,2aalpha,3beta,6beta,6aalpha,7beta, 7aalpha)-
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
1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O- [(methylamino)-carbonyl]oxime.
Ethanimidothioc acid,2-(dimethylamino)-N-[[(methylamino) carbonyl]oxy]-2-oxo-, methyl ester.
Methanimidamide, N,N-dimethyl-N'-[3-[[(methylamino) -carbonyl]oxy]phenyl]-, monohydrochloride
Methanimidamide,N,N-dimethyl-N'- [2-methyl-4-[(methylamino)carbonyl]oxy]phenyl]-
6,9-Methano-2,4, 3-benzodioxathiepin,6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide
Propanal, 2-methyl-2- (methylthio)-, O-[(methylamino)carbonyl]oxime
Pyridine, 3-(1-methyl- 2-pyrrolidinyl)-, (S)-, & salts
Pyrrolo[2,3-b]indol-5-ol, 1,2,3,3a,8,8a-hexahydro-1,3a, 8-trimethyl-, methylcarbamate (ester), (3aS-cis)-.
Tetraethyldithio pyrophosphate
2039-52-0
314-62-1
Zinc phosphide Zn3 P2 , when present at concentrations greater than 10% (R,T)
FOOTNOTE 1: CAS 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 paragraphs 371.1(f)(1) and (7) of this Title.
(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).
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)]-
Benzenamine, 4,4' -carbonimidoylbis[N,N-dimethyl-
Benzenamine, 4-chloro- 2-methyl-, hydrochloride
Benzenamine, 4,4' -methylenebis[2-chloro-
Benzeneacetic acid, 4-chloro- alpha-(4-chlorophenyl)-alpha-hydroxy-, ethyl ester
Benzenebutanoic acid, 4-[bis (2-chloroethyl)amino]-
Benzene, 1,1'-(2,2- dichloroethylidene) bis[4-chloro-
Benzene, 1,1'-(2,2,2-trichloroethylidene) bis[4- methoxy-
1,2-Benzisothiazol- 3(2H)-one, 1,1-dioxide, & salts
[1,1'-Biphenyl]-4,4'- diamine, 3,3'-dichloro-
[1,1'-Biphenyl]-4,4'- diamine, 3,3'-dimethoxy-
[1,1'-Biphenyl]-4,4'- diamine, 3,3'-dimethyl-
1,3-Butadiene, 1,1,2, 3,4,4-hexachloro-
1-Butanamine, N-butyl- N-nitroso-
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]]-
Carbamic acid,[1-[(butylamino)carbonyl]- 1H-benzimidazol-2-yl]-,methyl ester
2,5-Cyclohexadiene- 1,4-dione
Cyclohexane, 1,2,3,4, 5,6-hexachloro-, (1alpha,2alpha,3beta,4alpha,5alpha,6beta)-
1,2-Dibromo- 3-chloropropane
alpha,alpha- Dimethylbenzylhydroperoxide (R)
1,2-Ethanediamine, N,N-dimethyl-N'-2-pyridinyl-N'- (2-thienylmethyl)-
Ethane, 1,1'- [methylenebis(oxy)]bis[2-chloro-
Ethane, 1,1,1,2- tetrachloro-
Ethane, 1,1,2,2- tetrachloro-
Ethanol, 2,2'-oxybis-, dicarbamate.
D-Glucose, 2-deoxy-2- [[(methylnitrosoamino)-carbonyl]amino]-
Guanidine, N-methyl- N'-nitro-N-nitroso-
7783--06-4
4,7-Methano-1H-indene, 1,2,4,5,6,7,8,8 -octachloro-2,3,3a,4,7, 7a-hexahydro-
1,3,4-Metheno- 2H-cyclobuta[cd]pentalen-2-one, 1,1a,3,3a,4,5, 5,5a,5b,6-decachlorooctahydro-
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)-
116-54-7
N-Nitroso- N-methylurethane
2H-1,3,2-Oxazaphosphorin- 2-amine, N,N-bis (2-chloroethyl)tetrahydro-,2-oxide
Pentanol, 4-methyl- (I)
Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-,(E)-
Phenol, 2,2'-methylenebis [3,4,6-trichloro-
Phenol, 2,3,4,6 -tetrachloro-
Phosphorodithioic acid, O,O-diethyl S-methylester
Propane, 1,2-dibromo- 3-chloro-
Propanoic acid, 2- (2,4,5-trichlorophenoxy)-
1-Propene, 1,1,2,3,3,3 -hexachloro-
2,3,4,6- Tetrachlorophenol
Yohimban-16- carboxylic acid, 11,17-dimethoxy- 18-[(3,4,5- trimethoxybenzoyl)oxy]-, methyl ester,(3beta,16beta,17alpha,18beta,20alpha)-
(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" means 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 wastes 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 matter 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: .DEC Hazardous Waste Number Waste
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 and cable.
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, and cable.
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 subdivision 370.1(e)).
(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.
(iii) ('a') Hydraulic machines containing less than 1000 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 listed hazardous waste, as is any solvent used for flushing.
('b') Hydraulic machines containing 1000 ppm PCB or greater 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, 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 lbs.) 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 lbs.) 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 lbs.) 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 kg (3 lb.) of dielectric fluid if the total weight of the capacitor is less than 4.08 kg (9 lbs.)
(4) Testing Procedures. The procedures in 40 CFR 761.60(g) (see subdivision 370.1(e) of this Part) 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.
('a') Prepare and follow an equipment cleaning 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.
('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;
('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 in accordance with SW-846, Method 8290.
('2') "Not detected" means at or below the lower method calibration limit (MCL) in SW-846, Method 8290, Table 1.
('d') The generator must manage all residues from the cleaning process as F032 waste.
('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.
('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.
"I certify under penalty of law that all process equipment required to be cleaned or replaced under 6 NYCRR 371.4(f) 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."
(i) Comparable/Syngas Fuel Exclusion. Wastes that meet the following comparable/syngas fuel requirements are not solid wastes:
(i) Physical specifications.--
('a') Heating value. The heating value must exceed 5,000 BTU/lbs. (11,500 J/g).
('b') Viscosity. The viscosity must not exceed: 50 cs, as-fired.
(ii) Constituent specifications. For compounds listed in table 1 to this subdivision the specification levels and, where non-detect is the specification, minimum required detection limits are: (see Table 1).
(2) Synthesis gas fuel specification.--Synthesis gas fuel (i.e., syngas fuel) that is generated from hazardous waste must:
(v) Contain less than 1 ppmv of each hazardous constituent in the target list of Appendix 23 constituents.
. Table 1 to subdivision 371.4(i)
(mg/kg at
10,000 BTU/lb)
Total Organic Halogens as Cl
or individual halogenated organics listed below
Polychlorinated biphenyls, total (Arocolors, total)a
Bis(2-ethylhexyl)phthalate (Di-2-ethylhexyl phthalate)
o-Cresol (2-Methyl phenol)
m-Cresol (3-Methyl phenol)
p-Cresol (4-Methyl phenol)
Propargyl alcohol (2-Propyn-l-ol)
Sulfonated Organics
Tetraethyldithiopyrophosphate (Sulfotepp)
Nitrogenated Organics
O,O-Diethyl O-pyrazinyl phophoro- thioate (Thionazin)
p-(Dimethylamino)azobenzene (4-Dimethylaminoazobenzene)
, -Dimethylphenethylamine
Ethylenethiourea (2- Imidazolidinethione)
2-Methyllactonitrile (Acetone cyanohydrin)
MNNG (N-Metyl-N-nitroso-N'-nitroguanidine)
1-Naphthylamine, ( -Naphthylamine)
2-Naphthylamine, ( -Naphthylamine)
4-Nitroaniline, (p-Nitroaniline)
p-Nitrophenol, (p-Nitrophenol)
N-Nitrosodiphenylamine, (Diphenylnitrosamine)
1,4-Phenylene diamine, (p-Phenylenediamine)
2-Picoline (alpha-Picoline)
Propythioracil (6-Propyl-2-thiouracil)
Toluene-2,6-diamine (2,6-Diaminotoluene)
1,3,5-Trinitrobenzene, (sym-Trinitobenzene)
Halogenated Organics:
104-57-8
Benzal chloride (Dichloromethyl benzene)
100-44-77
Bis(2-chloroethyl)ether (Dichloroethyl ether)
4-Bromophenyl phenyl ether (p-Bromo diphenyl ether)
2-Chloronaphthalene (beta-Chloronaphthalene)
Dichloromethoxy ethane (Bis(2-chloroethoxy)methane)
Epichlorohydrin (1-Chloro-2,3-epoxy propane)
Hexachloro-1,3-butadiene (Hexachlorobutadiene)
Hexachloropropene (Hexachloropropylene)
Lindane (gamma-Hexachlorocyclohexane) (gamma-BHC)
Pentachloronitrobenzene (PCNB) (Quintobenzene) (Quintozene)
Silvex (2,4,5-Trichlorophenoxypropionic acid)
Trichlorofluoromethane (Trichlormonofluoromethane)
(3) Implementation.--Waste that meets the comparable or syngas fuel specifications provided by paragraphs (1) or (2) of this subdivision (these constituent levels must be achieved by the comparable fuel when generated, or as a result of treatment or blending, as provided in subparagraphs (iii)('c') or (iv) of this paragraph) is excluded from the definition of solid waste provided that the following requirements are met:
(i) Notices--For purposes of this section, the person claiming and qualifying for the exclusion is called the comparable/syngas fuel generator and the person burning the comparable/syngas fuel is called the comparable/syngas burner. The person who generates the comparable fuel or syngas fuel must claim and certify to the exclusion.
('a') State RCRA and CAA Directors in other Authorized States or USEPA Regional RCRA and CAA Directors in Unauthorized States. (This is the Commissioner, in New York State)--
('1') The generator must submit a one-time notice to the Regional or State RCRA and CAA Directors in whose jurisdiction the exclusion is being claimed and where the comparable/syngas fuel will be burned, certifying compliance with the conditions of the exclusion and providing documentation as required by paragraph (3)(i)('a')('3') of this subdivision;
('2') If the generator is a company that generates comparable/syngas fuel at more than one facility, the generator shall specify at which sites the comparable/syngas fuel will be generated;
('3') A comparable/syngas fuel generator's notification to the Directors must contain the following items:
('i') The name, address, and RCRA ID number of the person/facility claiming the exclusion;
('ii') The applicable EPA Hazardous Waste Codes for the hazardous waste;
('iii') Name and address of the units, meeting the requirements of subparagraph (3)(ii) of this subdivision, that will burn the comparable/syngas fuel; and
('iv') The following statement is signed and submitted by the person claiming the exclusion or his authorized representative:
"Under penalty of criminal and civil prosecution for making or submitting false statements, representations, or omissions, I certify that the requirements of 6 NYCRR 371.4(i) have been met for all waste identified in this notification. Copies of the records and information required at 6 NYCRR 371.4(i)(3)(x) are available at the comparable/syngas fuel generator's facility. Based on my inquiry of the individuals immediately responsible for obtaining the information, the information is, to the best of my knowledge and belief, true, accurate, and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment for knowing violations."
('b') Public notice.--Prior to burning an excluded comparable/syngas fuel, the burner must publish in a major newspaper of general circulation local to the site where the fuel will be burned, a notice entitled "Notification of Burning a Comparable/Syngas Fuel Excluded Under the Resource Conservation and Recovery Act" containing the following information:
('1') Name, address, and facility ID number of the generating facility;
('2') Name and address of the unit(s)that will burn the comparable/syngas fuel;
('3') A brief, general description of the manufacturing, treatment, or other process generating the comparable/syngas fuel;
('4') An estimate of the average and maximum monthly and annual quantity of the waste claimed to be excluded; and
('5') Name and mailing address of the Regional or State Directors to whom the claim was submitted.
(ii) Burning.--The comparable/syngas fuel exclusion for fuels meeting the requirements of paragraphs (1) or (2) and subparagraph (3)(i) of this subdivision applies only if the fuel is burned in the following units that also shall be subject to Federal/State/local air emission requirements, including all applicable CAA MACT requirements:
('a') Industrial furnaces as defined in section 370.2 of this Title;
('b') Boilers, as defined in section 370.2 of this Title, that are further defined as follows:
('1') Industrial boilers located on the site of a facility engaged in a manufacturing process where substances are transformed into new products, including the component parts of products, by mechanical or chemical processes; or
('2') Utility boilers used to produce electric power, steam, heated or cooled air, or other gases or fluids for sale;
('c') Hazardous waste incinerators subject to regulation under section 373-2.15 or section 373-3.15 of this Title or applicable CAA MACT standards.
(iii) Blending to meet the viscosity specification.--A hazardous waste blended to meet the viscosity specification shall:
('a') As generated and prior to any blending, manipulation, or processing meet the constituent and heating value specifications of clause (1)(i)('a') and subparagraph (1)(ii) of this subdivision;
('b') Be blended at a facility that is subject to the applicable requirements of Subparts 373-2 and 373-3, or paragraph 372.2(a)(8)of this Title; and
('c') Not violate the dilution prohibition of subparagraph (3)(vi) of this subdivision.
(iv) Treatment to meet the comparable fuel exclusion specifications.--
('a') A hazardous waste may be treated to meet the exclusion specifications of subparagraphs (1)(i) and (ii) of this subdivision provided the treatment:
('1') Destroys or removes the constituent listed in the specification or raises the heating value by removing or destroying hazardous constituents or materials;
('2') Is performed at a facility that is subject to the applicable requirements of Subparts 373-2 and 373-3, or paragraph 372.2(a)(8)of this Title; and
('3') Does not violate the dilution prohibition of subparagraph (3)(vi)of this subdivision.
('b') Residuals resulting from the treatment of a hazardous waste listed in section 371.4 of this Part to generate a comparable fuel remain a hazardous waste.
(v) Generation of a syngas fuel.--
('a') A syngas fuel can be generated from the processing of hazardous wastes to meet the exclusion specifications of paragraph (2) of this subdivision provided the processing:
('1') Destroys or removes the constituent listed in the specification or raises the heating value by removing or destroying constituents or materials;
('2') Is performed at a facility that is subject to the applicable requirements of Subparts 373-2 and 373-3, or paragraph 372.2(a)(8)of this Title or is an exempt recycling unit pursuant to paragraph 371.1(g)(3)of this Part; and
('b') Residuals resulting from the treatment of a hazardous waste listed in section 371.4 of this Part to generate a syngas fuel remain a hazardous waste.
(vi) Dilution prohibition for comparable and syngas fuels.--No generator, transporter, handler, or owner or operator of a treatment, storage, or disposal facility shall in any way dilute a hazardous waste to meet the exclusion specifications of clause (1)(i)('a'), subparagraph (1) (ii) or paragraph (2) of this subdivision.
(vii) Waste analysis plans. The generator of a comparable/syngas fuel shall develop and follow a written waste analysis plan which describes the procedures for sampling and analysis of the hazardous waste to be excluded. The waste analysis plan shall be developed in accordance with the applicable sections of the "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods" (SW-846), as incorporated by reference in subdivision 370.1(e) of this Title. The plan shall be followed and retained at the facility excluding the waste.
('a') At a minimum, the plan must specify:
('1') The parameters for which each hazardous waste will be analyzed and the rationale for the selection of those parameters;
('2') The test methods which will be used to test for these parameters;
('3') The sampling method which will be used to obtain a representative sample of the waste to be analyzed;
('4') The frequency with which the initial analysis of the waste will be reviewed or repeated to ensure that the analysis is accurate and up to date; and
('5') If process knowledge is used in the waste determination, any information prepared by the generator in making such determination.
('b') The waste analysis plan shall also contain records of the following:
('1') The dates and times waste samples were obtained, and the dates the samples were analyzed;
('2') The names and qualifications of the person(s) who obtained the samples;
('3') A description of the temporal and spatial locations of the samples;
('4') The name and address of the laboratory facility at which analyses of the samples were performed;
('5') A description of the analytical methods used, including any clean-up and sample preparation methods;
('6') All quantitation limits achieved and all other quality control results for the analysis (including method blanks, duplicate analyses, matrix spikes, etc.), laboratory quality assurance data, and description of any deviations from analytical methods written in the plan or from any other activity written in the plan which occurred;
('7') All laboratory results demonstrating that the exclusion specifications have been met for the waste; and
('8') All laboratory documentation that support the analytical results, unless a contract between the claimant and the laboratory provides for the documentation to be maintained by the laboratory for the period specified in subparagraph (3)(xi) of this subdivision and also provides for the availability of the documentation to the claimant upon request.
('c') Syngas fuel generators shall submit for approval, prior to performing sampling, analysis, or any management of a syngas fuel as an excluded waste, a waste analysis plan containing the elements of clause (3)(vii)('a') of this subdivision to the appropriate regulatory authority. The approval of waste analysis plans must be stated in writing and received by the facility prior to sampling and analysis to demonstrate the exclusion of a syngas. The approval of the waste analysis plan may contain such provisions and conditions as the regulatory authority deems appropriate.
('a') General. For each waste for which an exclusion is claimed, the generator of the hazardous waste must test for all the constituents on Appendix 23, except those that the generator determines, based on testing or knowledge, should not be present in the waste. The generator is required to document the basis of each determination that a constituent should not be present. The generator may not determine that any of the following categories of constituents should not be present:
('1') A constituent that triggered the toxicity characteristic for the waste constituents that were the basis of the listing of the waste stream, or constituents for which there is a treatment standard for the waste code in subdivision 376.4(a) of this Title;
('2') A constituent detected in previous analysis of the waste;
('3') Constituents introduced into the process that generates the waste; or
('4') Constituents that are byproducts or side reactions to the process that generates the waste.
Note to subparagraph (3)(viii): Any claim under this subparagraph must be valid and accurate for all hazardous constituents; a determination not to test for a hazardous constituent will not shield a generator from liability should that constituent later be found in the waste above the exclusion specifications.
('b') For each waste for which the exclusion is claimed where the generator of the comparable/syngas fuel is not the original generator of the hazardous waste, the generator of the comparable/syngas fuel may not use process knowledge pursuant to clause (3)(viii)('a') of this subdivision and must test to determine that all of the constituent specifications of subparagraph (1)(ii) and paragraph (2) of this subdivision have been met.
('c') The comparable/syngas fuel generator may use any reliable analytical method to demonstrate that no constituent of concern is present at concentrations above the specification levels. It is the responsibility of the generator to ensure that the sampling and analysis are unbiased, precise, and representative of the waste. For the waste to be eligible for exclusion, a generator must demonstrate that:
('1') Each constituent of concern is not present in the waste above the specification level at the 95% upper confidence limit around the mean; and
('2') The analysis could have detected the presence of the constituent at or below the specification level at the 95% upper confidence limit around the mean.
('d') Nothing in this subparagraph preempts, overrides or otherwise negates the provision in paragraph 372.2(a)(2) of this Title, which requires any person who generates a solid waste to determine if that waste is a hazardous waste.
('e') In an enforcement action, the burden of proof to establish conformance with the exclusion specification shall be on the generator claiming the exclusion.
('f') The generator must conduct sampling and analysis in accordance with their waste analysis plan developed under subparagraph (3)(vii) of this subdivision.
('g') Syngas fuel and comparable fuel that has not been blended in order to meet the kinematic viscosity specifications shall be analyzed as generated.
('h') If a comparable fuel is blended in order to meet the kinematic viscosity specifications, the generator shall:
('1') Analyze the fuel as generated to ensure that it meets the constituent and heating value specifications; and
('2') After blending, analyze the fuel again to ensure that the blended fuel continues to meet all comparable/syngas fuel specifications.
('i') Excluded comparable/syngas fuel must be re-tested, at a minimum, annually and must be retested after a process change that could change the chemical or physical properties of the waste.
(ix) Speculative accumulation. Any persons handling a comparable/syngas fuel are subject to the speculative accumulation test under subparagraph 371.1(c)(4)(iv) of this Part.
('a') All information required to be submitted to the implementing authority as part of the notification of the claim:
('1') The owner/operator name, address, and RCRA facility ID number of the person claiming the exclusion;
('2') The applicable EPA Hazardous Waste Codes for each hazardous waste excluded as a fuel; and
('3') The certification signed by the person claiming the exclusion or his authorized representative.
('b') A brief description of the process that generated the hazardous waste and process that generated the excluded fuel, if not the same;
('c') An estimate of the average and maximum monthly and annual quantities of each waste claimed to be excluded;
('d') Documentation for any claim that a constituent is not present in the hazardous waste as required under clause (3)(viii)('a') of this subdivision;
('e') The results of all analyses and all detection limits achieved as required under subparagraph (3)(viii) of this subdivision;
('f') If the excluded waste was generated through treatment or blending, documentation as required under subparagraph (3)(iii) or (iv) of this subdivision;
('g') If the waste is to be shipped off-site, a certification from the burner as required under subparagraph (3)(xii) of this subdivision;
('h') A waste analysis plan and the results of the sampling and analysis that includes the following:
('7') All laboratory analytical results demonstrating that the exclusion specifications have been met for the waste; and
('8') All laboratory documentation that support the analytical results, unless a contract between the claimant and the laboratory provides for the documentation to be maintained by the laboratory for the period specified in subparagraph (3)(xi) of this subdivision and also provides for the availability of the documentation to the claimant upon request; and
('i') If the generator ships comparable/syngas fuel off-site for burning, the generator must retain for each shipment the following information on-site:
('1') The name and address of the facility receiving the comparable/syngas fuel for burning;
('2') The quantity of comparable/syngas fuel shipped and delivered;
('3') The date of shipment or delivery;
('4') A cross-reference to the record of comparable/syngas fuel analysis or other information used to make the determination that the comparable/syngas fuel meets the specifications as required under subparagraph (3)(viii) of this subdivision; and
('5') A one-time certification by the burner as required under subparagraph (3)(xii) of this subdivision.
(xi) Records retention. Records must be maintained for the period of three years. A generator must maintain a current waste analysis plan during that three year period.
('a') Certifying that the comparable/syngas fuel will only be burned in an industrial furnace or boiler, utility boiler, or hazardous waste incinerator, as required under paragraph (c)(2) of this section;
('b') Identifying the name and address of the units that will burn the comparable/syngas fuel; and
('c') Certifying that the state in which the burner is located is authorized to exclude wastes as comparable/syngas fuel under the provisions of this section.
(xiii) Ineligible waste codes. Wastes that are listed because of presence of dioxins or furans, as set out in Appendix 22, are not eligible for this exclusion, and any fuel produced from or otherwise containing these wastes remains a hazardous waste subject to full Part 370, 371, 372, 373, 374, and 376 hazardous waste management requirements.
§Appendix 19 - Representative Sampling Methods
Extremely viscous liquid--ASTM Standard D140-70 Crushed or powdered material--ASTM Standard D346-75 Soil or rock-like material--ASTM Standard D420-69 Soil-like material--ASTM Standard D1452-65 Fly Ash-like material--ASTM Philadelphia, PA 19103) (See 6 NYCRR subdivision 370.1(e)).
Containerized liquid waste--"COLIWASA" described in "Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods," EPA Publication SW-846, U.S. Environmental Protection Agency, 26 W. St. Clair St., Cincinnati, Ohio 45268)
Liquid waste in pits, ponds, lagoons, and similar reservoirs.--"Pond Sampler" described in "Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods." These methods are also described in "Samplers and Sampling Procedures for Hazardous Waste Streams," EPA 600/2-80-018, January 1980. (See 6 NYCRR Part 370.1(e)).
§Appendix 20 - Reserved
Note: The Toxicity Characteristic Leaching Procedure (TCLP) Method 1311 is published in "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods," EPA Publication SW-846, as incorporated by reference in subdivision 370.1(e) of this Title.
§Appendix 21 - Reserved
Chemical Analysis Test Methods Note: Appropriate analytical procedures to determine whether a sample contains a given toxic constituent are specified in Chapter Two, "Choosing the Correct Procedure" found in "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods," EPA Publication SW-846, as incorporated by reference in subdivision 370.1(e) of this Title. Prior to final sampling and analysis method selection, the individual should consult the specific section or method described in SW-846 for additional guidance on which of the approved methods should be employed for a specific sample analysis situation.
§Appendix 22 - Basis for Listing Hazardous Waste
EPA Hazardous Waste No
Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, carbon tetrachloride, chlorinated fluorocarbons.
Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, 1,1,2-trichloroethane, chlorobenzene, 1,1,2-trichloro- 1,2,2-trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane.
Cyanide (salts). F008 Cyanide (salts). F009 Cyanide (salts). F010 Cyanide (salts). F011 Cyanide (salts). F012 Cyanide (complexed).
Tetra-and pentachlorodibenzo-p-dioxins; tetra and pentachlorodibenzofurans; tri- and tetrachlorophenols and their chlorophenoxy derivative acids, esters, ethers, amine and other salts.
Penta- and hexachlorodibenzo-p-dioxins; penta and hexachlorodibenzofurans; pentachlorophenol and its derivatives.
Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta, and hexachlorodibenzofurans.
Tetra-, and pentachlorodibenzo-p-dioxins, tetra and pentachlorodibenzofurans; tri- and tetra-chlorophenols and their chlorophenoxy derivative acids, esters, ethers, amine and other salts.
Chloromethane; dichloromethane; trichloromethane; carbon tetrachloride; chloroethylene; 1,1- dichloroethane; 1,2-dichloroethane; trans-1,2- dichloroethylene; 1,1-dichloroethylene; 1,1,1-trichloroethane; 1,1,2-trichloroethane; trichloroethylene; 1,1,1,2-tetrachloroethane; 1,1,2,2-tetrachloroethane; tetrachloroethylene; pentachloroethane; hexachloroethane; allyl chloride (3-chloropropene); dichloropropane; dichloropropene; 2-chloro- 1,3-butadiene; hexachloro- 1,3-butadiene; hexachlorocyclopentadiene; hexachlorocyclohexane; benzene; chlorobenzene; dichlorobenzene; 1,2,4-trichlorobenzene; tetrachlorobenzene; pentachlorobenzene; hexachlorobezene; toluene; naphthalene.
Chloromethane; dichloromethane; trichloromethane; carbon tetrachloride; chloroethylene; 1,1- dichloroethane; 1,2-dichloroethane; trans-1,2- dichloroethylene; 1,1-dichloroethylene; 1,1,1-trichloroethane; 1,1,2-trichloroethane; trichloroethylene; 1,1,1,2-tetrachloroethane; 1,1,2,2-tetrachloroethane; tetrachloroethylene; pentachloroethane; hexachloroethane; allyl chloride (3-chloropropene); dichloropropane; dichloropropene; 2-chloro- 1,3-butadiene; hexachloro- 1,3-butadiene; hexachlorocyclopentadiene; benzene; chlorobenzene; dichlorobenzenes; 1,2,4-trichlorobenzene; tetrachlorobenzene; pentachlorobenzene; hexachlorobenzene; toluene; naphthalene.
Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans; tri-, tetra-, and pentachlorophenols and their chlorophenoxy derivative acids, esters, ethers, amine and other salts.
Benz(a)anthracene, benzo(a)pyrene, dibenz(a,h)- anthracene,indeno(1,2,3-cd)pyrene, pentachlorophenol, arsenic, chromium, tetra-, penta-, hexa-, heptachlorodibenzo-p-dioxins, tetra-, penta-, hexa-, heptachlorodibenzofurans.
Benzene, benzo(a)pyrene chrysene, lead, chromium.
All constituents for which treatment standards are specified for multi-source leachate (wastewaters and nonwastewaters) under subdivision 376.4(d).
Hexavalent chromium lead.
Acrylonitrite, acetonitrite, hydrocyanic acid.
Hydrocyanic acid, acrylonitrite, acetonitrile.
Epichlorohydrin, chloroethers (bis(chloromethyl) ether and bis(2-chloroethyl) ethers), trichloropropane, dichloropropanols.
Ethylene dichloride, 1,1,1-trichloroethane, 1,1,2-trichloroethane, tetrachloroethanes (1,1,2,2-tetrachloroethane and 1,1,1,2- tetrachloroethane), trichloroethylene, tetrachloroethylene, carbon tetrachloride, chloroform, vinyl chloride, vinylidene chloride.
Phorate, formaldehyde, phosphorodithioic and phosphoro-thioic acid esters.
Chloroform, carbon tetrachloride, hexachloroethane, trichloroethane, tetrachloroethylene, dichloroethylene, 1,1,2,2-tetrachloroethene.
Benzene, dichlorobenzene, trichlorobenzenes, tetrachlorobenzene, pentachlorobenzene, hexachlorobenzene, benzyl chloride.
Phenol, napthalene.
Phthalica anhydride.
Benzotrichloride, benzyl chloride, chloroform, chloromethane, chlorobenzene, 1,4-dichlorobenzene, hexachlorobenzene, pentachlorobenzene, 1,2,4,5- tetrachlorobenzene, toluene.
Benzo(a)pyrene, dibenz(a,h)anthracene, benzo(a)anthracene, benzo(b)fluoranthene, benzo(k)fluoranthene,3-methylcholanthrene, 7,12-dimethylbenz(a)anthracene.