40 CFR PART 268 -- LAND DISPOSAL RESTRICTIONS

§268.8 Landfill and surface impoundment disposal restrictions.

(a) Prior to May 8, 1990, wastes which are otherwise prohibited from land disposal under §268.33(f) of this part may be disposed in a landfill or surface impoundment which is in compliance with the requirements of §268.5(h)(2) provided that the requirements of this section are met. As of May 8, 1990, this section is no longer in effect.

(1) Prior to such disposal, the generator has made a good faith effort to locate and contract with treatment and recovery facilities practically available which provide the greatest environmental benefit.

(2) If a generator determines that there is no practically available treatment for his waste, he must fulfill the following specific requirements:

(i) Prior to the initial shipment of waste, the generator must submit a demonstration to the Regional Administrator that includes: a list of facilities and facility officials contacted, addresses, telephone numbers, and contact dates, as well as a written discussion of why he was not able to obtain treatment or recovery for that waste. The generator must also provide to the Regional Administrator the following certification:

I certify under penalty of law that the requirements of 40 CFR §§268.8(a)(1) have been met and that disposal in a landfill or surface impoundment is the only practical alternative to treatment currently available. I believe that the information submitted is true, accurate, and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment.

The generator does not need to wait for Regional Administrator approval of the demonstration/certification before shipment of the waste. However, if the Regional Administrator invalidates the demonstration/certification for the reasons outlined in §v268.8(b)(2), the generator must immediately cease further shipments of the waste, and immediately inform all facilities that received the waste of such invalidation, and keep records of such communication on-site in his files.

(ii) With the initial shipment of waste, the generator must submit a copy of the demonstration and the certification discussed above in §268.8(a)(2)(i) to the receiving facility. With each subsequent waste shipment, only the certification is required to be submitted provided that the conditions being certified remain unchanged. Such a generator must retain on-site a copy of the demonstration (if applicable) and certification required for each waste shipment for at least five years from the date that the waste that is the subject of such documentation was last sent to on-site or off-site disposal. The five-year record retention requirement is automatically extended during the course of any unresolved enforcement action regarding the regulated activity or as requested by the Administrator.

(3) If a generator determines that there are practically available treatments for his waste, he must contract to use the practically available technology that yields the greatest environmental benefit. He must also fulfill the following specific requirements:

(i) The generator must submit to the Regional Administrator, prior to the initial shipment of waste, a demonstration that includes: a list of facilities and facility officials contacted, addresses, telephone numbers, and contact dates, as well as a written discussion explaining why the treatment or recovery technology chosen provides the greatest environmental benefit. The generator must also provide to the Regional Administrator the following certification:

I certify under penalty of law that the requirements of 40 CFR §268.8(a)(1) have been met and that I have contracted to treat my waste (or otherwise provide treatment) by the practically available technology which yields the greatest environmental benefit, as indicated in my demonstration. I believe that the information submitted is true, accurate, and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment.

The generator does not need to wait for Regional Administrator approval of the demonstration/certification before shipment of the waste.

(ii) With the initial shipment of waste, the generator must submit to the receiving facility a copy of the demonstration and the certification discussed above in §268.8(a)(3)(i). With each subsequent waste shipment, only the certification is required to be submitted provided that the conditions being certified remain unchanged. Such a must retain on-site a copy of the demonstration (if applicable) and certification required for each waste shipment for at least five years from the date that the waste that is the subject of such documentation was last sent to on-site or off-site disposal. The five-year record retention requirement is automatically extended during the course of any unresolved enforcement action regarding the regulated activity or as requested by the Administrator.

(4) Where the generator has determined that there is practically available treatment for his waste prior to disposal, with the initial shipment of waste, such generator must submit a copy of the demonstration and the certification required in paragraph (a)(2)(B) of this section to the receiving facility. With each subsequent waste shipment, only the certification is required to be submitted provided that the conditions being certified remain unchanged. Such a generator must retain on-site a copy of the demonstration (if applicable) and certification required for each waste shipment for at least five years from the date that the waste that is the subject of such documentation was last sent to on-site or off-site disposal. The five-year record retention requirement is automatically extended during the course of any unresolved enforcement action regarding the regulated activity or as requested by the Administrator.

(b) After receiving the demonstration and certification, the Regional Administrator may request any additional information which he deems necessary to evaluate the certification, and submit a new demonstration and certification as provided in §268.8(a) to the receiving facility.

(1) A generator who has submitted a certification under this section must immediately notify the Regional Administrator when he has knowledge of any change in the conditions which formed the basis of his certification.

(2) If, after review of the certification, the Regional Administrator determines that practically available treatment exists where the generator has certified otherwise, or that there exists some other method of practically available treatment yielding greater environmental benefit than that which the generator has certified, the Regional Administrator may invalidate the certification.

(3) If the Regional Administrator invalidates a certification, the generator must immediately cease further shipments of the waste, and inform all facilities that received the waste of such invalidation and keep records of such communication on-site in his files.

(c) A treatment, recovery or storage facility receiving wastes subject to a valid certification must keep copies of the generator's demonstration (if applicable) and certification in his operating record.

(1) The owner or operator of a treatment or recovery facility must certify that he has treated the waste in accordance with the generator's demonstration. The following certification is required:

I certify under penalty of law that I have personally examined and am familiar with the treatment technology and operation of the treatment process used to support this certification and that, based on my inquiry of those individuals immediately responsible for obtaining this information, I believe that the treatment process has been operated and maintained properly so as to comply with treatment as specified in the generator's demonstration. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment.

(2) The owner or operator of a treatment, recovery or storage facility must, for each initial shipment of waste, send a copy of the generator's demonstration (if applicable) and certification under 268.8(a)(2)(i) or 268.8(a)(3)(i) and certification under §268.8(c)(1) (if applicable) to the facility receiving the waste or treatment residues. With each subsequent waste shipment, only the certification is required to be submitted provided that the conditions certified remain unchanged.

(d) The owner or operator of a disposal facility must ensure that those wastes prohibited under §268.33(f) are subject to a certification according to the requirements of this section prior to disposal in a landfill or surface impoundment, and that the units receiving such wastes must meet the minimum technological requirements of §268.5(h)(2).

(e) Once the certification is received by the Regional Administrator, and provided that the wastes have been treated by the treatment (if any), determined by the generator to yield the greatest environmental benefit practically available, the wastes or treatment residuals may be disposed in a landfill or surface impoundment unit meeting the requirements of 268.5(h)(2), unless otherwise prohibited by the Regional Administrator.

(Approved by the Office of Management and Budget under control number 2050-0085)

(53 FR 31214, Aug. 17, 1988, as amended at 54 FR 36971, Sept. 6, 1989; 55 FR 22688, June 1, 1990; 55 FR 23935, June 13, 1990)


§268.9 Special rules regarding wastes that exhibit a characteristic

(a) The initial generator of a solid waste must determine each EPA Hazardous Waste Number (waste code) applicable to the waste in order to determine the applicable treatment standards under subpart D of this part. For purposes of Part 268, the waste will carry the waste code for any applicable listed waste (Part 261, Subpart D). In addition, where the waste exhibits a characteristic, the waste will carry one or more of the characteristic waste codes (Part 261, Subpart C), except when the treatment standard for the listed waste operates in lieu of the treatment standard for the characteristic waste, as specified in paragraph (b) of this section. If the generator determines that their waste displays a hazardous characteristic (and is not D001 non-wastewaters treated by CMBST, RORGS, OR POLYM of § 268.42, Table 1), the generator must determine the underlying hazardous constituents (as defined at § 268.2(i)) in the characteristic waste.
(b) Where a prohibited waste is both listed under 40 CFR Part 261, subpart D and exhibits a characteristic under 40 CFR Part 261, subpart C, the treatment standard for the waste code listed in 40 CFR Part 261, subpart D will operate in lieu of the standard for the waste code under 40 CFR Part 261, subpart C, provided that the treatment standard for the listed waste includes a treatment standard for the constituent that causes the waste to exhibit the characteristic. Otherwise, the waste must meet the treatment standards for all applicable listed and characteristic waste codes.
(c) In addition to any applicable standards determined from the initial point of generation, no prohibited waste which exhibits a characteristic under 40 CFR Part 261, subpart C may be land disposed unless the waste complies with the treatment standards under subpart D of this part.
(d) Wastes that exhibit a characteristic are also subject to § 268.7 requirements, except that once the waste is no longer hazardous, a one-time notification and certification must be placed in the generators or treaters files and sent to the EPA region or authorized state. The notification and certification that is placed in the generators or treaters files must be updated if the process or operation generating the waste changes and/or if the subtitle D facility receiving the waste changes. However, the generator or treater need only notify the EPA region or an authorized state on an annual basis if such changes occur. Such notification and certification should be sent to the EPA region or authorized state by the end of the calendar year, but no later that December 31.
(1) The notification must include the following information:
(i) Name and address of the RCRA Subtitle D facility receiving the waste shipment; and
(ii) A description of the waste as initially generated, including the applicable EPA hazardous waste code(s), treatability group(s), and underlying hazardous constituents (as defined in § 268.2(i)), unless the waste will be treated and monitored for all underlying hazardous constituents. If all underlying hazardous constituents will be treated and monitored, there is no requirement to list any of the underlying hazardous constituents on the notice.
(2) The certification must be signed by an authorized representative and must state the language found in § 268.7(b)(5).
(i) If treatment removes the characteristic but does not treat underlying hazardous constituents, then the certification found in § 268.7(b)(5)(iv) applies.
(ii) (Reserved).

[55 FR 22520, June 1, 1990, as amended at 55 FR 3864, Jan. 31, 1991; 57 FR 37194, Aug. 18, 1992; 58 FR 29860, May 24, 1993; 59 FR 47982, Sept. 19, 1994; 60 FR 242, Jan. 3, 1995; 61 FR 15566, Apr. 8, 1996; 61 FR 15660, Apr. 8, 1996; 62 FR 25998, May 12, 1997]


Subpart B -- Schedule for Land Disposal Prohibition and Establishment of Treatment Standards

Source: 51 FR 19305, May 28, 1986, unless otherwise noted.

§268.10 Identification of wastes to be evaluated by August 8, 1988.

EPA will take action under sections 3004(g)(5) and 3004(m), of the Conservation and Recovery Act, by August 8, 1988, for the following wastes (for ease of understanding the wastes have been listed by the section of 40 CFR Part 261 under which they were listed):


§261.31 Wastes

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.

F007 -- Spent cyanide plating bath solutions from electroplating operations.

F008 -- Plating bath sludges from the bottom of plating baths from electroplating operations where cyanides are used in the process.

F009 -- Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process.

F019 -- Wastewater treatment sludges from the chemical conversion coating of aluminum.


§261.32 Wastes

K001 -- Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote and/or pentachlorophenol.

K004 -- Wastewater treatment sludge from the production of zinc yellow pigments.

K008 -- Over residue from the production of chrome oxide green pigments.

K011 -- Bottom stream from the wastewater stripper in the production of acrylonitrile.

K013 -- Bottom stream from the acetonitrile column in the production of acrylonitrile.

K014 -- Bottoms from the acetonitrile purification column in the production of acrylonitrile.

K015 -- Still bottoms from the distillation of benzyl chloride.

K016 -- Heavy ends or distillation residues from the production of carbon tetrachloride.

K017 -- Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.

K018 -- Heavy ends from the fractionation column in ethyl chloride production.

K020 -- Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.

K021 -- Aqueous spent antimony catalyst waste from fluoromethanes production.

K022 -- Distillation bottom tars from the production of phenol/acetone from cumane.

K024 -- Distillation bottoms from the production of phthalic anhydride from naphthalene.

K030 -- Column bottom or heavy ends from the combined production of trichloroethylene and perchloroethylene.

K031 -- By-products salts generated in the production of MSMA and cacodylic acid.

K035 -- Wastewater treatment sludges generated in the production of creosote.

K036 -- Still bottoms from toluene reclamation distillation in the production of disulfoton.

K037 -- Wastewater treatment sludge from the production of disulfoton.

K044 -- Wastewater treatment sludges from the manufacturing and processing of explosives.

K045 -- Spent carbon from the treatment of wastewater containing explosives.

K046 -- Wastewater treatment sludges from the manufacturing, formulation and loading of lead-based initiating compounds.

K047 -- Pink/red water from TNT operations.

K060 -- Ammonia still lime sludge from coking operations.

K061 -- Emission control dust/sludge from the primary production of steel in electric furnaces.

K062 -- Spent pickle liquor from steel finishing operations in chlorine production.

K069 -- Emission control dust/sludge from secondary lead smelting.

K071 -- Brine purification muds from the mercury cells process in chlorine production, where separately prepurified brine is not used.

K073 -- Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes

K083 -- Distillation bottoms from aniline production.

K084 -- Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.

K085 -- Distillation of fractionation column bottoms from the production of chlorobenzenes.

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.

K087 -- Decanter tank tar sludge from coking operations.

K099 -- Untreated wastewater from the production of 2,4-D.

K101 -- Distillation tar residues from the distillation of aniline-based compounds in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.

K102 -- Residue from the use of activated carbon for decolorization in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.

K103 -- Process residues from aniline extraction from the production of aniline.

K104 -- Combined wastewater streams generated from nitrobenzene/aniline production.

K106 -- Waste water treatment sludge from the mercury cell process in chlorine production.


§261.33(e) Wastes

P001 -- Warfarin, when present at concentration greater than 0.3%

P004 -- Aldrin

P005 -- Allyl alcohol

P010 -- Arsenic acid

P011 -- Arsenic (V) oxide

P012 -- Arsenic (III) oxide

P015 -- Beryllium dust

P016 -- Bis-(chloromethyl) ether

P018 -- Brucine

P020 -- Dinoseb

P030 -- Soluble cyanide salts not elsewhere specified

P036 -- Dichlorophenylarsine

P037 -- Dieldrin

P039 -- Disulfoton

P041 -- Diethyl-p-nitrophenyl phosphate

P048 -- 2,4-Dinitrophenol

P050 -- Endosulfan

P058 -- Fluoracetic acid, sodium salt

P059 -- Heptachlor

P063 -- Hydrogen cyanide

P068 -- Methyl Hydrazine

P069 -- Methyllactonitrile

P070 -- Aldicarb

P071 -- Methyl parathion

P081 -- Nitroglycerine

P082 -- N-Nitrosodimethylamine

P084 -- N-Nitrosomethylvinylamine

P087 -- Osmium tetraoxide

P089 -- Parathion

P092 -- Phenylmercuric acetate

P094 -- Phorate

P097 -- Famphur

P102 -- Propargyl alcohol

P105 -- Sodium azide

P108 -- Strychnine and salts

P110 -- Tetraethyl lead

P115 -- Thallium (I) sulfate

P120 -- Vanadium pentoxide

P122 -- Zinc phosphide, when present at concentrations greater than 10%

P123 -- Toxaphene


§261.33(f) Wastes

U007 -- Acrylamide

U009 -- Acrylonitrile

U010 -- Mitomycin C

U012 -- Aniline

U016 -- Benz(c)acridine

U018 -- Benz(a)anthracene

U019 -- Benzene

U022 -- Benzo(a)pyrene

U029 -- Methyl bromide

U031 -- n-Butanol

U036 -- Chlordane, technical

U037 -- Chlorobenzene

U041 -- n-Chloro-2,3-epoxypropane

U043 -- Vinyl chloride

U044 -- Chloroform

U046 -- Chloromethyl methyl ether

U050 -- Chrysene

U051 -- Creosote

U053 -- Crotonaldehyde

U061 -- DDT

U063 -- Dibenz o (a, h) anthracene

U064 -- 1,2:7,8 Dibenzopyrene

U066 -- Dibromo-3-chloropropane 1,2-

U067 -- Ethylene dibromide

U074 -- 1,4-Dichloro-2-butene

U077 -- Ethane, 1,2-dichloro-

U078 -- Dichloroethylene, 1,1-

U086 -- N,N Diethylhydrazine

U089 -- Diethylstilbestrol

U103 -- Dimethyl sulfate

U105 -- 2,4-Dinitrotoluene

U108 -- Dioxane, 1,4-

U115 -- Ethylene oxide

U122 -- Formaldehyde

U124 -- Furan

U129 -- Lindane

U130 -- Hexachlorocyclopentadiene

U133 -- Hydrazine

U134 -- Hydrofluoric acid

U137 -- Indeno(1,2,3-cd)pyrene

U151 -- Mecury

U154 -- Methanol

U155 -- Methapyrilene

U157 -- 3-Methylcholanthrene

U158 -- 4,4-Methylene-bis-(2-chloroaniline)

U159 -- Methyl ethyl ketone

U171 -- Nitropropane, 2-

U177 -- N-Nitroso-N-methylurea

U180 -- N-Nitrosopyrrolidine

U185 -- Pentachloronitrobenzene

U188 -- Phenol

U192 -- Pronamide

U200 -- Reserpine

U209 -- Tetrachloroethane, 1,1,2,2-

U210 -- Tetrachloroethylene

U211 -- Carbon tetrachloride

U219 -- Thiourea

U220 -- Toluene

U221 -- Toluenediamine

U223 -- Toluene diisocyanate

U226 -- Methylchloroform

U227 -- Trichloroethane, 1,1,2-

U228 -- Trichloroethylene

U237 -- Uracil mustard

U238 -- Ethyl carbamate

U248 -- Warfarin, when present at concentrations of 0.3% or less

U249 -- Zinc phosphide, when present at concentrations of 10% or less

(51 FR 19305, May 28, 1986, as amended at 56 FR 3878, Jan. 31, 1991)


§268.11 Identification of wastes to be evaluated by June 8, 1989.

EPA will take action under sections 3004(g)(5) and 3004(m) of the Resource Conservation and Recovery Act, by June 8, 1989, for the following wastes (for ease of understanding the wastes have been listed by the section of 40 CFR Part 261 under which they were listed):

§261.31 Wastes

F010 -- Quenching bath sludge from oil baths from metal heat treating operations where cyanides are used in the process.

F011 -- Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations.

F012 -- Quenching wastewater treatment sludges from metal heat operations where cyanides are used in the process.

F024 -- Wastes including but not limited to, distillation residues, heavy ends, tars and reactor clean-out wastes from the production of chlorinated aliphatic hydrocarbons, having carbon content from one to five, utilizing free radical catalyzed processes. (This listing does not include light ends, spent filters and filter aids, spend desiccants, wastewater, wastewater treatment sludges, spent catalysts, and wastes listed in §261.32.).

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