Details and Instructions for M&EC's WAC and Waste Profiles

Note: Once you have read these instructions, follow the link below to access M&EC's Waste Profile form.

Click here to go to M&EC's Waste Profile Form (editable RTF file).

East Tennessee Waste Treatment Center Waste Acceptance Criteria

Approvals:

________________________________________ Bill Hillis, President, M&EC	________________ (date)
________________________________________ Ron Anderson, General Manager, M&EC	________________ (date)
________________________________________ Guy Wilson, Radiation Safety Officer, M&EC	________________ (date)

Purpose

The Broad Spectrum Waste Acceptance Criteria (WAC) defines the technical requirements for waste acceptance at the East Tennessee Waste Treatment Center (ETWTC). The document has been designed to lead the generator through the steps of categorizing waste; characterizing the waste; completing the required documentation; and packaging the waste for shipment to the ETWTC.

The ETWTC reserves the right to revise this WAC, as it deems necessary based on regulatory, administrative, technical, or operational changes.

Waste Acceptance Criteria Objectives

The WAC is designed to ensure the following objectives are met:

All waste is uniformly evaluated to determine acceptability under current licenses, permits, and operating guidelines
All waste has physical and chemical hazards identified to allow for safe and appropriate handling of waste during shipment and processing
All waste is characterized in terms of physical and chemical constituents to determine compatibility of the waste with facility equipment and determine optimum operating conditions
All waste is accompanied by complete documentation as required by the facility’s licenses, permits and operating guidelines

Applicability

This WAC applies to all waste accepted by the ETWTC for treatment and/or subsequent disposal as approved by the State of Tennessee.

The ETWTC System Description

The ETWTC facility is designed to accept and treat the following waste types:

Resource and Recovery Conservation Act (RCRA) Regulated Waste
Low Level Radioactive Waste
Toxic Substance Control Act (TSCA) Regulated Waste (PCB waste)
Mixed Waste (RCRA/LLW), (TSCA/LLW), (RCRA/TSCA)

The ETWTC facility is comprised of processing units that are designed to treat the above mentioned waste types into a stable chemical form for disposal. The treatment units consist of process equipment, which will neutralize, precipitate, and stabilize waste that is suitable for alternate uses or off-site disposal. The ETWTC treatment process also uses Direct Chemical Oxidation, reactive waste treatment methods, and Macro-encapsulation for treating special selected waste streams.

Acceptance Restrictions

Hazardous Restrictions

The Environmental Protection Agency (EPA) Hazardous Waste Codes that may be received by the ETWTC are identified in Attachment A.

The ETWTC does not accept waste meeting the following criteria:

Waste packaged as compressed gas
Medical wastes as defined under 40 CFR 259
Biological waste

The ETWTC reserves the right to reject waste after reviewing the customer’s Waste Data Sheet based on technical, economical or operational infeasibility. The ETWTC may limit or delay acceptance of certain wastes based on regulatory or operational conditions effective at the time. These limitations include:

Facility inventory - permits, licenses, regulatory limits, storage capacity
Operational mode - current configuration of equipment
Operational efficiency - treating reactive waste, mercury, and PCB contaminated waste

ETWTC will make every effort to minimize most limitations through scheduling.

Radiological Restrictions

The total radioactivity of a shipment must be approved by the RSO prior to shipment to the ETWTC, based on the quantity of radioactive material already in inventory at the ETWTC. The activity of a shipment shall not exceed the following limits (subject to approval by the RSO):

For atomic numbers 1 - 92, 80 Curies total activity
For atomic numbers 93 - 101, .8 Curies total not to exceed 90 nanocuries per gram of material
Special nuclear material shall not exceed the following limits, subject to approval by the RSO

For 235U, 300 grams total
For 239Pu, 200 grams total
For a combination of 235U and 239Pu, the sum of (the grams of 235U divided by 300) and (the grams of 239Pu divided by 200) shall be less than or equal to one
Special nuclear material is also subject to the Curie limitations specified above

Waste containing more than one nanocurie per gram of tritium shall be subject to approval of the RSO prior to shipment to the ETWTC.
Waste containing 226Ra, 232Th, 14C, 129I, 94Nb, or 99Tc shall be subject to approval by the RSO.
Radioactive material shall undergo a receipt survey for compliance with applicable regulations regarding exposure rates and removable radiocontaminant levels. Packaging shall comply with applicable regulatory criteria for the form of material received.
Exposure rates shall not exceed 100 millirem per hour on contact with the external surface of the waste or material received.
Exposure rates shall not exceed 50 millirem per hour measured at a distance of twelve inches (30 cm) from the surface of any single package (if the package is placed in a low background area).
Exposure rates shall not exceed 10 millirem per hour at a distance of three feet from any single package (if the package is placed in a low background area).
Allowable removable radiocontaminant levels on the external surface of packages received shall not exceed the following values. For gross measurements, use the most restrictive applicable case:

ISOTOPES	dpm/100cm²
U-natural, ²³⁵U, ²³⁸U, and associated decay products	1,000
Transuranics, ²²⁶Ra, ²²⁸Ra, ²³⁰Th, ²³⁸Th, ²³¹Pa, ²²⁷Ac, ¹²⁵I, ¹²⁹I	(20)
Th-Nat, ²³²Th, ⁹⁰Sr, ²²³Ra, ²²⁴Ra, ²³²U, ¹²⁶I, ¹³¹I, ¹³³I	200
Beta-gamma emitters (nuclides with decay modes other than alpha emission or spontaneous fission) except ⁹⁰Sr and others noted above	1,000
Tritium Organic Compounds; surfaces contaminated with HT, HTO, and metal tritide aerosols	10,000

PHYSICAL, CHEMICAL, RADIOLOGICAL CHARACTERIZATION

The ETWTC requires certain physical, chemical, and radiological data, prior to treatment. This data shall be used to evaluate the waste against permits, licenses and administrative criteria; evaluate safety considerations; and to optimize processing. It is critical to the ETWTC operations that the characterization data supplied by the generator be representative of the waste submitted. All waste streams should be characterized in accordance with EPA’s Test Methods for Evaluating Solid Waste, Physical/Chemical Methods (SW-846) [Current Edition]. If a generator’s waste is regulated under laws, permits, or agreements that specify alternate sampling or analytical methods, the generator will be allowed to substitute for those methods. Alternate sampling or analytical methods must be made known to the ETWTC Waste Receipt Manager.

ANALYTICAL DATA REQUIREMENTS

Analytical requirements for the ETWTC are based on whole waste characterization; not characterization of the individual contaminants. Decisions in regards to handling and processing the waste are based on the analytical data and/or process knowledge, so it is critical that the physical, chemical, and radiological constituents of the waste are identified.

Use of Process Knowledge

The generator may supplement sampling and analysis with process knowledge. All process knowledge determinations, however, must be documented in writing with supporting documentation such as original waste specification sheets or Material Safety Data Sheets. This information is to be submitted with the analytical data and the completed data sheets for evaluation by the ETWTC. The ETWTC reserves the right to request analyses if the process knowledge is not sufficient to adequately characterize the waste.

Note: If a physical evaluation of individual containers is conducted, it is beneficial to take photographs of the contents. These photographs are extremely beneficial to the ETWTC in evaluating wastes, particularly solids that may vary substantially and require size reduction.

Waste Acceptance

Upon completion of the characterization, the waste will be evaluated for acceptance.

Waste Packaging Requirements

General Information

All waste shall be packaged, marked, labeled, and shipped in accordance with all federal, state, and local regulations and agreements. This shall include, but is not limited to; requirements by the Department of Transportation (DOT), the Resource Conservation & Recovery Act (RCRA), the Toxic Substances Control Act (TSCA) and the Tennessee Department of Environment and Conservation (TDEC).

The ETWTC reserves the right to schedule on-site reviews of the generator’s packaging, storage, and shipping operations prior to acceptance of waste.

Container Specifications

All drums shall have an open top or bunghole for inspection upon receipt. Drums shall have a capacity not to exceed 85 gallons. All drums exceeding 50 pounds shall be placed on pallets or configured for fork truck access. All containers shall be clearly labeled as to its contents upon receipt. The generator shall certify that pallets used during the shipping process can be released after unloading (i.e., non-radioactive, non-hazardous, etc.). Pallets found to be contaminated may be returned to the generator.

Overpacks and special waste/shipping containers (i.e., B-25 boxes, B-12 boxes, Century Containers) are acceptable for receipt at the ETWTC with prior approval from the Waste Receipt Manager.

Package Freeboard Specification

The generator shall leave a minimum container/tank freeboard of 5%. This requirement will provide protection against damage due to weather-related phase changes during shipment, liquid expansion, gas over-pressurization, and spillage while opening the container or tank. Overfilled containers or tanks may be rejected.

Package and Vehicle Contamination Limits

The external surfaces of packages and inner floor and walls of closed van type vehicles shall be visually free of residue on arrival at the ETWTC. Decontamination of contaminated vehicles will be the responsibility of the generator.

Waste Receipt and Disposition

Waste Acceptance

Upon receipt, the ETWTC shall inspect all containers or tanks for integrity. In addition, the information provided on the manifest or bill of lading and other shipping papers shall be compared to the actual shipment. The ETWTC Waste Receipt Manager will notify the generator upon receipt of the waste shipment to discuss any discrepancies. It is important that the technical contact identified is available, by phone, at the time the shipment is received. The ETWTC will make every effort to contact the appropriate site contact; however, the shipment may be rejected if there is a discrepancy, which cannot be resolved at the time of receipt.

The ETWTC will handle all significant manifest discrepancies in accordance with applicable federal and state regulations, and copies of all discrepancy reports and resolutions shall be maintained.

Rejection of Waste Upon Receipt

A waste may be rejected in total or in part upon receipt for the following:

Waste is determined to be prohibited as outlined in Acceptance Restriction Section of this WAC
Generator cannot provide sampling, laboratory and/or analytical support data upon request
Volume or weight of waste is in excess of what was indicated on 48 Hour Notification Form
Waste received in non-conforming containers
Waste arrives in structurally compromised containers
Drummed waste in excess of 50 pounds received non-palletized
Waste containers filled beyond 5% freeboard specification
Discrepancies are noted with the paperwork which cannot be resolved with the generator or technical contact
Failure to rectify discrepancies between the generator’s data and the fingerprint analysis

Any evidence of fraudulent information detected in the information submitted will result in the immediate rejection of the shipment. Nonconforming waste which resolution cannot be resolved shall be returned to the generator.

Residuals Management

All residuals from the treatment process (i.e., oversized solid wastes) shall be either returned to the generator or disposed by the ETWTC as ETWTC newly generated waste.

TABLE A EPA Hazardous Waste Codes That Will Be Resident in the Mixed Waste (Hazardous and Radioactive) to be Processed in the Proposed East Tennessee Waste Treatment Center
Waste Code	Waste Description and Treatment/Regulatory Subcategory Note: Radioactive component of the mixed waste is described in the application for radioactive material license a copy of which is provided at the end of this table.
D001	Ignitable Characteristic Wastes, except for the § 261.21(a)(1) High TOC Subcategory.
D002	Corrosive Characteristic Wastes.
D003	Reactive Sulfides Subcategory based on 261.23(a)(5).
D004	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for arsenic based on the extraction procedure (EP) in SW846 Methods 1310.
D005	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for barium based on the extraction procedure (EP) in SW846 Method 1310.
D006	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for cadmium based on the extraction procedure (EP) in SW846 Method 1310.
D007	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for chromium based on the extraction procedure (EP) in SW846 Method 1310.
D008	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for lead based on the extraction procedure (EP) in SW846 Method 1310.
D009	Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the extraction procedure (EP) in SW846 Method 1310; and contain greater than or equal to 260 mg/kg total mercury that also contain organics and are not incinerator residues. (High Mercury-Organic Subcategory)
D010	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for selenium based on the extraction procedure (EP) in SW846 Method 1310.
D011	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for silver based on the extraction procedure (EP) in SW846 Method 1310.
D012	Wastes that are TC for Endrin based on the TCLP in SW846 Method 1311.
D013	Wastes that are TC for Lindane based on the TCLP in SW846 Method 1311.
D014	Wastes that are TC for Methoxychlor based on the TCLP in SW846 Method 1311.
D015	Wastes that are TC for Toxaphene based on the TCLP in SW846 Method 1311.
D016	Wastes that are TC for 2,4-D(2,4-Dichlorophenoxyacetic acid) based on the TCLP in SW846 Method 1311.
D017	Wastes that are TC for 2,4,5-TP (Silvex) based on the TCLP in SW846 Method 1311.
D018	Wastes that are TC for Benzene based on the TCLP in SW846 Method 1311.
D019	Wastes that are TC for Carbon tetrachloride based on the TCLP in SW846 Method 1311.
D020	Wastes that are TC for Chlordane based on the TCLP in SW846 Method 1311.
D021	Wastes that are TC for Chlorobenzene based on the TCLP in SW846 Method 1311.
D022	Wastes that are TC for Chloroform based on the TCLP in SW846 Method 1311.
D023	Wastes that are TC for o-Cresol based on the TCLP in SW846 Method 1311.
D024	Wastes that are TC for m-Cresol based on the TCLP in SW846 Method 1311.
D025	Wastes that are TC for p-Cresol based on the TCLP in SW846 Method 1311.
D026	Wastes that are TC for Cresols (Total) based on the TCLP in SW846 Method 1311.
D027	Wastes that are TC for p-Dichloro- benzene based on the TCLP in SW846 Method 1311.
D028	Wastes that are TC for 1,2-Dichloroethane based on the TCLP in SW846 Method 1311.
D029	Wastes that are TC for 1,1-Dichloroethylene based on the TCLP in SW846 Method 1311.
D030	Wastes that are TC for 2,4-Dinitrotoluene based on the TCLP in SW846 Method 1311.
D031	Wastes that are TC for Heptachlor based on the TCLP in SW846 Method 1311.
D032	Wastes that are TC for Hexachloro- benzene based on the TCLP in SW846 Method 1311.
D033	Wastes that are TC for Hexachlorobutadiene based on the TCLP in SW846 Method 1311.
D034	Wastes that are TC for Hexachloroethane based on the TCLP in SW846 Method 1311.
D035	Wastes that are TC for Methyl ethyl ketone based on the TCLP in SW846 Method 1311.
D036	Wastes that are TC for Nitrobenzene based on the TCLP in SW846 Method 1311.
D037	Wastes that are TC for Pentachlorophenol based on the TCLP in SW846 Method 1311.
D038	Wastes that are TC for Pyridine based on the TCLP in SW846 Method 1311.
D039	Wastes that are TC for Tetrachloroethylene based on the TCLP in SW846 Method 1311.
D040	Wastes that are TC for Trichloroethylene based on the TCLP in SW846 Method 1311.
D041	Wastes that are TC for 2,4,5-Trichlorophenol based on the TCLP in SW846 Method 1311.
D042	Wastes that are TC for 2,4,6-Trichlorophenol based on the TCLP in SW846 Method 1311.
D043	Wastes that are TC for Vinyl chloride based on the TCLP in SW846 Method 1311.
F001, F002, F003, F004, & F005	F001, F002, F003, F004 and/or F005 solvent wastes that contain any combination of one or more of the following spent solvents: acetone, benzene, n-butyl alcohol, carbon disulfide, carbon tetrachloride, chlorinated fluorocarbons, chlorobenzene, o-cresol, m-cresol, p-cresol, cyclohexanone, o-dichlorobenzene, 2-ethoxyethanol, ethyl acetate, ethyl benzene, ethyl ether, isobutyl alcohol, methanol, methylene chloride, methyl ethyl ketone, methyl isobutyl ketone, nitrobenzene, 2-nitropropane, pyridine, tetrachloroethylene, toluene, 1,1,1-trichloroethane, 1,1,2-trichloroethane, 1,1,2-trichloro-1,2,2-trifluorethane, trichloroethylene, trichloromonofluoromethane, and/or xylenes [except as specifically noted in other subcategories]. See further details of these listings in § 261.31.
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 residues 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.
F010	Quenching bath residues 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 waste water treatment sludges from metal heat treating operations where cyanides are used in the process.
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.
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: (1) tri- or tetrachlorophenol, or of intermediates used to produce their pesticide derivatives, excluding wastes from the production of Hexachlorophene from highly purified 2,4,5-trichlorophenol
F021	Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of pentachlorophenol, or of intermediates used to produce its derivatives
F022	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 its derivatives.
F023	Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials or equipment previously used for the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tri- and tetrachlorophenols. (This listing does not include wastes from equipment used only for the production or use of Hexachlorophene from highly purified 2,4,5-trichlorophenol).
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 § 261.31 or § 261.32.)
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.
F026	Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials or 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.
F027	Discarded unused formulations containing tri-, tetra-, or pentachlorophenol or discarded unused formulations containing compounds derived from these chlorophenols. (This listing does not include formulations containing hexachlorophene synthesized from prepurified 2,4,5-trichlorophenol as the sole component).
F028	Residues resulting from the incineration or thermal treatment of soil contaminated with EPA Hazardous Wastes Nos. F020, F021, F023, F026, and F027.
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 shlorophenolic formulations (except potentially cross-contaminated wastes that have had the F032 waste code deleted in accordance with § 261.35 of this chapter or potentially cross-contaminated waste 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.
F039	Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one restricted waste classified as hazardous under subpart D of this part. (Leachate resulting from the disposal of one or more of the following EPA Hazardous Wastes and no other Hazardous Wastes retains its EPA Hazardous Waste Number(s): F020, F021, F022, F026, F027, and/or F028.).
P003	Acrolein
P004	Aldrin
P010	Arsenic acid
P011	Arsenic pentoxide
P012	Arsenic trioxide
P013	Barium cyanide
P015	Beryllium dust
P021	Calcium cyanide
P022	Carbon disulfide
P024	p-Chloroaniline
P028	Benzyl chloride
P029	Copper cyanide
P030	Cyanides (soluble salts and complexes)
P031	Cyanogen
P033	Cyanogen chloride
P037	Dieldrin
P039	Disulfoton
P044	Dimethoate
P047	4,6-Dinitro-o-cresol
P048	2,4-Dinitrophenol
P050	Endosulfan
P051	Endrin
P056	Fluorine
P059	Heptachlor
P060	Isodrin
P063	Hydrogen cyanide
P065	Mercury fulminate nonwastewaters, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC.
P071	Methyl parathion
P074	Nickel-cyanide
P075	Nicotine and salts
P076	Nitric oxide
P077	p-Nitroaniline
P082	N-Nitrosodimethylamine
P085	Octamethylpyrophosphoramide
P087	Osmium tetroxide
P089	Parathion
P094	Phorate
P098	Potassium cyanide.
P0101	Ethyl cyanide (Propanenitrile)
P0102	Propargyl alcohol
P0103	Selenourea
P0104	Silver cyanide
P0105	Sodium azide
P0106	Sodium cyanide
P0108	Strychnine and salts
P109	Tetraethyldithiopyrophosphate
P113	Thallic oxide
P116	Thiosemicarbazide
P119	Ammonium vanadate
P120	Vanadium pentoxide
P123	Toxaphene
U001	Acetaldehyde
U002	Acetone
U003	Acetonitrile
U004	Acetophenone
U005	2-Acetylaminofluorene
U006	Acetyl chloride
U007	Acrylamide
U008	Acrylic acid
U009	Acrylonitrile
U010	Mitomycin C
U011	Amitrole
U012	Aniline
U018	Benz(a)anthracene
U019	Benzene
U020	Benzenesulfonyl chloride
U021	Benzidine
U022	Benzo(a)pyrene
U024	bis(2-Chloroethoxy)methane
U025	bis(2-Chloroethyl)ether
U027	bis(2-Chloroisopropyl)ether
U028	bis(2-Ethylhexyl)phthalate
U029	Methyl bromide (Bromomethane)
U030	4-Bromophenyl phenyl ether
U031	n-Butyl alcohol
U032	Calcium chromate
U033	Carbon oxyfluoride
U034	Trichloroacetaldehyde (Chloral)
U035	Chlorambucil
U036	Chlordane
U037	Chlorobenzene
U038	Chlorobenzilate
U039	p-Chloro-m-cresol
U041	Epichlorohydrin (1-Chloro-2,3-epoxypropane)
U042	2-Chloroethyl vinyl ether
U043	Vinyl chloride
U044	Chloroform
U045	Chloromethane (Methyl chloride)
U046	Chloromethyl methyl ether
U047	2-Chloronaphthalene
U048	2-Chlorophenol
U050	Chrysene
U052	Cresols (Cresylic acid)
U053	Crotonaldehyde
U055	Cumene
U056	Cyclohexane
U057	Cyclohexanone
U060	DDD
U061	DDT
U063	Dibenz(a,h)anthracene
U068	Dibromomethane
U069	Di-n-butyl phthalate
U070	o-Dichlorobenzene
U071	m-Dichlorobenzene
U072	p-Dichlorobenzene
U075	Dichlorodifluoromethane
U076	1,1-Dichloroethane
U077	1,2-Dichloroethane
U078	1,1-Dichloroethylene
U079	1,2-Dichloroethylene
U080	Methylene chloride
U081	2,4-Dichlorophenol
U082	2,6-Dichlorophenol
U083	1,2-Dichloropropane
U084	1,3-Dichloroproplyene
U088	Diethyl phthalate
U089	Diethyl stilbestrol
U101	2,4-Dimethylphenol
U102	Dimethyl phthalate
U103	Dimethyl sulfate
U105	2,4-Dinitrotoluene
U106	2,6-Dinitrotoluene
U107	Di-n-octyl phthalate
U108	1,4-Dioxane
U109	1,2-Diphenylhydrazine
U110	Dipropylamine
U111	Di-n-propylnitrosamine
U112	Ethyl acetate
U113	Ethyl acrylate
U115	Ethylene oxide
U117	Ethyl ether
U118	Ethyl methacrylate
U119	Ethyl methane sulfonate
U120	Fluoranthene
U121	Trichloromonofluoromethane
U122	Formaldehyde
U123	Formic acid
U124	Furan
U125	Furfural
U126	Glycidylaldehyde
U127	Hexachlorobenzene
U128	Hexachlorobutadiene
U129	Lindane
U130	Hexachlorocyclopentadiene
U131	Hexachloroethane
U132	Hexachlorophene
U133	Hydrazine
U134	Hydrogen fluoride
U135	Hydrogen Sulfide
U136	Cacodylic acid
U137	Indeno(1,2,3-cd)pyrene
U138	Iodomethane
U140	Isobutyl alcohol
U141	Isosafrole
U142	Kepone
U144	Lead acetate
U145	Lead phosphate
U146	Lead subacetate
U147	Maleic anhydride
U148	Maleic hydrazide
U149	Malononitrile
U150	Melphalan
U151	U151 (mercury) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.
U154	Methanol
U156	Methyl chlorocarbonate
U157	3-Methylcholanthrene
U158	4,4'-Methylene bis(2-chloroaniline)
U159	Methyl ethyl ketone
U160	Methyl ethyl ketone peroxide
U161	Methyl isobutyl ketone
U162	Methyl methacrylate
U165	Naphthalene
U166	1,4-Naphthoquinone
U167	1-Naphthlyamine
U168	2-Naphthlyamine
U169	Nitrobenzene
U170	p-Nitrophenol
U172	N-Nitrosodi-n-butylamine
U176	N-Nitroso-N-ethylurea
U177	N-Nitroso-N-methylurea
U180	N-Nitrosopyrrolidine
U181	5-Nitro-o-toluidine
U182	Paraldehyde
U187	Phenacetin
U188	Phenol
U189	Phosphorus sulfide
U191	2-Picoline
U194	n-Propylamine
U196	Pyridine
U197	p-Benzoquinone
U201	Resorcinol
U203	Safrole
U204	Selenium dioxide
U205	Selenium sulfide
U206	Streptozotocin
U207	1,2,4,5-Tetrachlorobenzene
U208	1,1,1,2-Tetrachloroethane
U209	1,1,2,2-Tetrachloroethane
U210	Tetrachloroethylene
U211	Carbon tetrachloride
U213	Tetrahydrofuran
U214	Thallium (I) acetate
U215	Thallium (I) carbonate
U216	Thallium (I) chloride
U217	Thallium (I) nitrate
U218	Thioacetamide
U219	Thiourea
U220	Toluene
U221	Toluenediamine
U222	o-Toluidine hydrochloride
U223	Toluene diisocyanate
U225	Bromoform (Tribromomethane)
U226	1,1,1-Trichloroethane
U227	1,1,2-Trichloroethane
U228	Trichloroethylene
U234	1,3,5-Trinitrobenzene
U235	tris-(2,3-Dibromopropyl)-phosphate
U236	Trypan Blue
U237	Uracil mustard
U238	Urethane (Ethyl carbamate)
U239	Xylenes
U240	2,4-D (2,4-Dichlorophenoxyacetic acid)
U243	Hexachloropropylene
U244	Thiram
U246	Cyanogen bromide
U247	Methoxychlor
U248	Warfarin, & salts, when present at concentrations of 0.3% or less.
U249	Zinc phosphide, Zn₃P₂, when present at concentrations of 10% or less.
U271	Benomyl
U277	Sulfallate
U278	Bendiocarb
U279	Carbaryl
U280	Barban
U328	o-Toluidine
U353	p-Toluidine
U359	2-Ethoxyethanol
U383	Potassium dimethyl dithiocarbamate

TABLE B EPA Hazardous Waste Codes That Will Be Resident in the Mixed Waste (Hazardous and Radioactive) to be Processed in the Proposed East Tennessee Waste Treatment Center
Waste Code	Waste Description and Treatment/Regulatory Subcategory Note: Radioactive component of the mixed waste is described in the application for radioactive material license a copy of which is provided at the end of this table.
D002	Corrosive Characteristic Wastes.
D003	Reactive Sulfides Subcategory based on 261.23(a)(5).
D004	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for arsenic based on the extraction procedure (EP) in SW846 Methods 1310.
D005	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for barium based on the extraction procedure (EP) in SW846 Method 1310.
D006	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for cadmium based on the extraction procedure (EP) in SW846 Method 1310.
D007	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for chromium based on the extraction procedure (EP) in SW846 Method 1310.
D008	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for lead based on the extraction procedure (EP) in SW846 Method 1310.
D009	Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the extraction procedure (EP) in SW846 Method 1310; and contain greater than or equal to 260 mg/kg total mercury that also contain organics and are not incinerator residues. (High Mercury-Organic Subcategory)
D010	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for selenium based on the extraction procedure (EP) in SW846 Method 1310.
D011	Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for silver based on the extraction procedure (EP) in SW846 Method 1310.
D012	Wastes that are TC for Endrin based on the TCLP in SW846 Method 1311.
D013	Wastes that are TC for Lindane based on the TCLP in SW846 Method 1311.
D014	Wastes that are TC for Methoxychlor based on the TCLP in SW846 Method 1311.
D015	Wastes that are TC for Toxaphene based on the TCLP in SW846 Method 1311.
D016	Wastes that are TC for 2,4-D(2,4-Dichlorophenoxyacetic acid) based on the TCLP in SW846 Method 1311.
D017	Wastes that are TC for 2,4,5-TP (Silvex) based on the TCLP in SW846 Method 1311.
D018	Wastes that are TC for Benzene based on the TCLP in SW846 Method 1311.
D019	Wastes that are TC for Carbon tetrachloride based on the TCLP in SW846 Method 1311.
D020	Wastes that are TC for Chlordane based on the TCLP in SW846 Method 1311.
D021	Wastes that are TC for Chlorobenzene based on the TCLP in SW846 Method 1311.
D022	Wastes that are TC for Chloroform based on the TCLP in SW846 Method 1311.
D023	Wastes that are TC for o-Cresol based on the TCLP in SW846 Method 1311.
D024	Wastes that are TC for m-Cresol based on the TCLP in SW846 Method 1311.
D025	Wastes that are TC for p-Cresol based on the TCLP in SW846 Method 1311.
D026	Wastes that are TC for Cresols (Total) based on the TCLP in SW846 Method 1311.
D027	Wastes that are TC for p-Dichloro- benzene based on the TCLP in SW846 Method 1311.
D028	Wastes that are TC for 1,2-Dichloroethane based on the TCLP in SW846 Method 1311.
D029	Wastes that are TC for 1,1-Dichloroethylene based on the TCLP in SW846 Method 1311.
D030	Wastes that are TC for 2,4-Dinitrotoluene based on the TCLP in SW846 Method 1311.
D031	Wastes that are TC for Heptachlor based on the TCLP in SW846 Method 1311.
D032	Wastes that are TC for Hexachloro- benzene based on the TCLP in SW846 Method 1311.
D033	Wastes that are TC for Hexachlorobutadiene based on the TCLP in SW846 Method 1311.
D034	Wastes that are TC for Hexachloroethane based on the TCLP in SW846 Method 1311.
D035	Wastes that are TC for Methyl ethyl ketone based on the TCLP in SW846 Method 1311.
D036	Wastes that are TC for Nitrobenzene based on the TCLP in SW846 Method 1311.
D037	Wastes that are TC for Pentachlorophenol based on the TCLP in SW846 Method 1311.
D038	Wastes that are TC for Pyridine based on the TCLP in SW846 Method 1311.
D039	Wastes that are TC for Tetrachloroethylene based on the TCLP in SW846 Method 1311.
D040	Wastes that are TC for Trichloroethylene based on the TCLP in SW846 Method 1311.
D041	Wastes that are TC for 2,4,5-Trichlorophenol based on the TCLP in SW846 Method 1311.
D042	Wastes that are TC for 2,4,6-Trichlorophenol based on the TCLP in SW846 Method 1311.
D043	Wastes that are TC for Vinyl chloride based on the TCLP in SW846 Method 1311.
F001, F002, & F004	F001, F002, and/or F004 solvent wastes that contain any combination of one or more of the following spent solvents: carbon tetrachloride, chlorinated fluorocarbons, chlorobenzene, o-cresol, m-cresol, p-cresol, o-dichlorobenzene, methylene chloride, nitrobenzene, tetrachloroethylene, 1,1,1-trichloroethane, 1,1,2-trichloroethane, 1,1,2-trichloro-1,2,2-trifluorethane, trichloroethylene, and/or trichloromonofluoromethane. See further details of these listings in § 261.31.
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 residues 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.
F010	Quenching bath residues 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 waste water treatment sludges from metal heat treating operations where cyanides are used in the process.
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.
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: (1) tri- or tetrachlorophenol, or of intermediates used to produce their pesticide derivatives, excluding wastes from the production of Hexachlorophene from highly purified 2,4,5-trichlorophenol
F021	Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of pentachlorophenol, or of intermediates used to produce its derivatives
F022	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 its derivatives.
F023	Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials or equipment previously used for the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tri- and tetrachlorophenols. (This listing does not include wastes from equipment used only for the production or use of Hexachlorophene from highly purified 2,4,5-trichlorophenol).
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 § 261.31 or § 261.32.)
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.
F026	Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials or 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.
F027	Discarded unused formulations containing tri-, tetra-, or pentachlorophenol or discarded unused formulations containing compounds derived from these chlorophenols. (This listing does not include formulations containing hexachlorophene synthesized from prepurified 2,4,5-trichlorophenol as the sole component).
F028	Residues resulting from the incineration or thermal treatment of soil contaminated with EPA Hazardous Wastes Nos. F020, F021, F023, F026, and F027.
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 shlorophenolic formulations (except potentially cross-contaminated wastes that have had the F032 waste code deleted in accordance with § 261.35 of this chapter or potentially cross-contaminated waste 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.
F039	Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one restricted waste classified as hazardous under subpart D of this part. (Leachate resulting from the disposal of one or more of the following EPA Hazardous Wastes and no other Hazardous Wastes retains its EPA Hazardous Waste Number(s): F020, F021, F022, F026, F027, and/or F028.).
P003	Acrolein
P004	Aldrin
P010	Arsenic acid
P011	Arsenic pentoxide
P012	Arsenic trioxide
P013	Barium cyanide
P015	Beryllium dust
P021	Calcium cyanide
P022	Carbon disulfide
P024	p-Chloroaniline
P028	Benzyl chloride
P029	Copper cyanide
P030	Cyanides (soluble salts and complexes)
P031	Cyanogen
P033	Cyanogen chloride
P037	Dieldrin
P039	Disulfoton
P044	Dimethoate
P047	4,6-Dinitro-o-cresol
P048	2,4-Dinitrophenol
P050	Endosulfan
P051	Endrin
P056	Fluorine
P059	Heptachlor
P060	Isodrin
P063	Hydrogen cyanide
P065	Mercury fulminate nonwastewaters, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC.
P071	Methyl parathion
P074	Nickel-cyanide
P075	Nicotine and salts
P076	Nitric oxide
P077	p-Nitroaniline
P082	N-Nitrosodimethylamine
P085	Octamethylpyrophosphoramide
P087	Osmium tetroxide
P089	Parathion
P094	Phorate
P098	Potassium cyanide.
P0101	Ethyl cyanide (Propanenitrile)
P0102	Propargyl alcohol
P0103	Selenourea
P0104	Silver cyanide
P0105	Sodium azide
P0106	Sodium cyanide
P0108	Strychnine and salts
P109	Tetraethyldithiopyrophosphate
P113	Thallic oxide
P116	Thiosemicarbazide
P119	Ammonium vanadate
P120	Vanadium pentoxide
P123	Toxaphene
U001	Acetaldehyde
U004	Acetophenone
U005	2-Acetylaminofluorene
U006	Acetyl chloride
U007	Acrylamide
U009	Acrylonitrile
U010	Mitomycin C
U011	Amitrole
U018	Benz(a)anthracene
U020	Benzenesulfonyl chloride
U021	Benzidine
U022	Benzo(a)pyrene
U024	bis(2-Chloroethoxy)methane
U025	bis(2-Chloroethyl)ether
U027	bis(2-Chloroisopropyl)ether
U028	bis(2-Ethylhexyl)phthalate
U029	Methyl bromide (Bromomethane)
U030	4-Bromophenyl phenyl ether
U032	Calcium chromate
U033	Carbon oxyfluoride
U034	Trichloroacetaldehyde (Chloral)
U035	Chlorambucil
U036	Chlordane
U037	Chlorobenzene
U038	Chlorobenzilate
U039	p-Chloro-m-cresol
U041	Epichlorohydrin (1-Chloro-2,3-epoxypropane)
U042	2-Chloroethyl vinyl ether
U043	Vinyl chloride
U044	Chloroform
U046	Chloromethyl methyl ether
U047	2-Chloronaphthalene
U048	2-Chlorophenol
U050	Chrysene
U052	Cresols (Cresylic acid)
U053	Crotonaldehyde
U060	DDD
U061	DDT
U063	Dibenz(a,h)anthracene
U068	Dibromomethane
U069	Di-n-butyl phthalate
U070	o-Dichlorobenzene
U071	m-Dichlorobenzene
U072	p-Dichlorobenzene
U075	Dichlorodifluoromethane
U076	1,1-Dichloroethane
U077	1,2-Dichloroethane
U078	1,1-Dichloroethylene
U079	1,2-Dichloroethylene
U080	Methylene chloride
U081	2,4-Dichlorophenol
U082	2,6-Dichlorophenol
U083	1,2-Dichloropropane
U084	1,3-Dichloroproplyene
U088	Diethyl phthalate
U089	Diethyl stilbestrol
U101	2,4-Dimethylphenol
U102	Dimethyl phthalate
U103	Dimethyl sulfate
U105	2,4-Dinitrotoluene
U106	2,6-Dinitrotoluene
U107	Di-n-octyl phthalate
U108	1,4-Dioxane
U109	1,2-Diphenylhydrazine
U111	Di-n-propylnitrosamine
U118	Ethyl methacrylate
U119	Ethyl methane sulfonate
U120	Fluoranthene
U121	Trichloromonofluoromethane
U122	Formaldehyde
U123	Formic acid
U126	Glycidylaldehyde
U127	Hexachlorobenzene
U128	Hexachlorobutadiene
U129	Lindane
U130	Hexachlorocyclopentadiene
U131	Hexachloroethane
U132	Hexachlorophene
U133	Hydrazine
U134	Hydrogen fluoride
U135	Hydrogen Sulfide
U136	Cacodylic acid
U137	Indeno(1,2,3-cd)pyrene
U138	Iodomethane
U141	Isosafrole
U142	Kepone
U144	Lead acetate
U145	Lead phosphate
U146	Lead subacetate
U147	Maleic anhydride
U148	Maleic hydrazide
U149	Malononitrile
U150	Melphalan
U151	U151 (mercury) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.
U157	3-Methylcholanthrene
U158	4,4'-Methylene bis(2-chloroaniline)
U160	Methyl ethyl ketone peroxide
U165	Naphthalene
U166	1,4-Naphthoquinone
U167	1-Naphthlyamine
U168	2-Naphthlyamine
U170	p-Nitrophenol
U172	N-Nitrosodi-n-butylamine
U176	N-Nitroso-N-ethylurea
U177	N-Nitroso-N-methylurea
U180	N-Nitrosopyrrolidine
U181	5-Nitro-o-toluidine
U182	Paraldehyde
U187	Phenacetin
U188	Phenol
U189	Phosphorus sulfide
U191	2-Picoline
U194	n-Propylamine
U196	Pyridine
U197	p-Benzoquinone
U201	Resorcinol
U203	Safrole
U204	Selenium dioxide
U205	Selenium sulfide
U206	Streptozotocin
U207	1,2,4,5-Tetrachlorobenzene
U208	1,1,1,2-Tetrachloroethane
U209	1,1,2,2-Tetrachloroethane
U210	Tetrachloroethylene
U211	Carbon tetrachloride
U213	Tetrahydrofuran
U214	Thallium (I) acetate
U215	Thallium (I) carbonate
U216	Thallium (I) chloride
U217	Thallium (I) nitrate
U218	Thioacetamide
U219	Thiourea
U220	Toluene
U221	Toluenediamine
U222	o-Toluidine hydrochloride
U223	Toluene diisocyanate
U225	Bromoform (Tribromomethane)
U226	1,1,1-Trichloroethane
U227	1,1,2-Trichloroethane
U228	Trichloroethylene
U234	1,3,5-Trinitrobenzene
U235	tris-(2,3-Dibromopropyl)-phosphate
U236	Trypan Blue
U237	Uracil mustard
U238	Urethane (Ethyl carbamate)
U240	2,4-D (2,4-Dichlorophenoxyacetic acid)
U243	Hexachloropropylene
U244	Thiram
U246	Cyanogen bromide
U247	Methoxychlor
U248	Warfarin, & salts, when present at concentrations of 0.3% or less.
U249	Zinc phosphide, Zn₃P₂, when present at concentrations of 10% or less.
U271	Benomyl
U277	Sulfallate
U278	Bendiocarb
U279	Carbaryl
U280	Barban
U328	o-Toluidine
U353	p-Toluidine
U359	2-Ethoxyethanol
U383	Potassium dimethyl dithiocarbamate

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