Table 10 - Technology Codes and Description of Technology-Based Standards

Technology code Description of technology-based standards ADGAS: Venting of compressed gases into an absorbing or reacting media (i.e., solid or liquid)-venting can be accomplished through physical release utilizing valves/piping; physical penetration of the container; and/or penetration through detonation. AMLGM: Amalgamation of liquid, elemental mercury contaminated with radioactive materials utilizing inorganic reagents such as copper, zinc, nickel, gold, and sulfur that result in a nonliquid, semi-solid amalgam and thereby reducing potential emissions of elemental mercury vapors to the air. BIODG: Biodegradation of organics or non-metallic inorganics (i.e., degradable inorganics that contain the elements of phosphorus, nitrogen, and sulfur) in units operated under either aerobic or anaerobic conditions such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., Total Organic Carbon can often be used as an indicator parameter for the biodegradation of many organic constituents that cannot be directly analyzed in wastewater residues). CARBN: Carbon adsorption (granulated or powdered) of non-metallic inorganics, organo-metallics, and/or organic constituents, operated such that a surrogate compound or indicator parameter has not undergone breakthrough (e.g., Total Organic Carbon can often be used as an indicator parameter for the adsorption of many organic constituents that cannot be directly analyzed in wastewater residues). Breakthrough occurs when the carbon has become saturated with the constituent (or indicator parameter) and substantial change in adsorption rate associated with that constituent occurs. CHOXD: Chemical or electrolytic oxidation utilizing the following oxidation reagents (or waste reagents) or combinations of reagents: (1) Hypochlorite (e.g. bleach); (2) chlorine; (3) chlorine dioxide; (4) ozone or UV (ultraviolet light) assisted ozone; (5) peroxides; (6) persulfates; (7) perchlorates; (8) permangantes; and/or (9) other oxidizing reagents of equivalent efficiency, performed in units operated such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., Total Organic Carbon can often be used as an indicator parameter for the oxidation of many organic constituents that cannot be directly analyzed in wastewater residues). Chemical oxidation specifically includes what is commonly referred to as alkaline chlorination. CHRED: Chemical reduction utilizing the following reducing reagents (or waste reagents) or combinations of reagents: (1) Sulfur dioxide; (2) sodium, potassium, or alkali salts or sulfites, bisulfites, metabisulfites, and polyethylene glycols (e.g., NaPEG and KPEG); (3) sodium hydrosulfide; (4) ferrous salts; and/or (5) other reducing reagents of equivalent efficiency, performed in units operated such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., Total Organic Halogens can often be used as an indicator parameter for the reduction of many halogenated organic constituents that cannot be directly analyzed in wastewater residues). Chemical reduction is commonly used for the reduction of hexavalent chromium to the trivalent state. CMBST: High temperature organic destruction technologies, such as combustion in incinerators, boilers, or industrial furnaces operated in accordance with the applicable requirements of Chapter 21, 015 or Chapter 22, 015 or Chapter 7, 008 and in other units operated in accordance with applicable technical operating requirements; and certain non-combustive technologies, such as the Catalytic Extraction Process. DEACT: Deactivation to remove the hazardous characteristics of a waste due to its ignitability, corrosivity, and/or reactivity. FSUBS: Fuel substitution in units operated in accordance with applicable technical operating requirements. HLVIT: Vitrification of high level mixed radioactive wastes in units in compliance with all applicable radioactive protection requirements under control of the Nuclear Regulatory Commission. IMERC: Incineration of wastes containing organics and mercury in units operated in accordance with the technical operating requirements of Chapter 21, 015 and Chapter 22, 015. All wastewater and nonwastewater residues derived from this process must then comply with the corresponding treatment standards per waste code with consideration of any applicable subcategories (e.g., High or Low Mercury Subcategories). INCIN: Incineration in units operated in accordance with the technical operating requirements of Chapter 21, 015 and Chapter 22, 015. LLEXT: Liquid-liquid extraction (often referred to as solvent extraction) of organics from liquid wastes into an immiscible solvent for which the hazardous constituents have a greater solvent affinity, resulting in an extract high in organics that must undergo either incineration, reuse as a fuel, or other recovery/reuse and a raffinate (extracted liquid waste) proportionately low in organics that must undergo further treatment as specified in the standard. MACRO: Macroencapsulation with surface coating materials such as polymeric organics (e.g. resins and plastics) or with a jacket of inert inorganic materials to substantially reduce surface exposure to potential leaching media. Macroencapsulation specifically does not include any material that would be classified as a tank or container according to Chapter 1. NEUTR: Neutralization with the following reagents (or waste reagents) or combinations of reagents: (1) Acids; (2) bases; or (3) water (including wastewaters) resulting in a pH greater than 2 but less than 12.5 as measured in the aqueous residuals. NLDBR: No land disposal based on recycling. POLYM: Formation of complex high-molecular weight solids through polymerization of monomers in high-TOC D001 non-wastewaters which are chemical components in the manufacture of plastics. PRECP: Chemical precipitation of metals and other inorganics as insoluble precipitates of oxides, hydroxides, carbonates, sulfides, sulfates, chlorides, flourides, or phosphates. The following reagents (or waste reagents) are typically used alone or in combination: (1) Lime (i.e., containing oxides and/or hydroxides of calcium and/or magnesium; (2) caustic (i.e., sodium and/or potassium hydroxides; (3) soda ash (i.e., sodium carbonate); (4) sodium sulfide; (5) ferric sulfate or ferric chloride; (6) alum; or (7) sodium sulfate. Additional floculating, coagulation or similar reagents/processes that enhance sludge dewatering characteristics are not precluded from use. RBERY: Thermal recovery of Beryllium. RCGAS: Recovery/reuse of compressed gases including techniques such as reprocessing of the gases for reuse/resale; filtering/adsorption of impurities; remixing for direct reuse or resale; and use of the gas as a fuel source. RCORR: Recovery of acids or bases utilizing one or more of the following recovery technologies: (1) Distillation (i.e., thermal concentration); (2) ion exchange; (3) resin or solid adsorption; (4) reverse osmosis; and/or (5) incineration for the recovery of acid-Note: this does not preclude the use of other physical phase separation or concentration techniques such as decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies. RLEAD: Thermal recovery of lead in secondary lead smelters. RMERC: Retorting or roasting in a thermal processing unit capable of volatilizing mercury and subsequently condensing the volatilized mercury for recovery. The retorting or roasting unit (or facility) must be subject to one or more of the following: (a) a National Emissions Standard for Hazardous Air Pollutants (NESHAP) for mercury; (b) a Best Available Control Technology (BACT) or a Lowest Achievable Emission Rate (LAER) standard for mercury imposed pursuant to a Prevention of Significant Deterioration (PSD) permit; or (c) a state permit that establishes emission limitations (within meaning of Section 302 of the Clean Air Act) for mercury. All wastewater and nonwastewater residues derived from this process must then comply with the corresponding treatment standards per waste code with consideration of any applicable subcategories (e.g., High or Low Mercury Subcategories). RMETL: Recovery of metals or inorganics utilizing one or more of the following direct physical/removal technologies: (1) Ion exchange; (2) resin or solid (i.e., zeolites) adsorption; (3) reverse osmosis; (4) chelation/solvent extraction; (5) freeze crystalization; (6) ultrafiltration and/or (7) simple precipitation (i.e., crystalization) - Note: This does not preclude the use of other physical phase separation or concentration techniques such as decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies. RORGS: Recovery of organics utilizing one or more of the following technologies: (1) Distillation; (2) thin film evaporation; (3) steam stripping; (4) carbon adsorption; (5) critical fluid extraction; (6) liquid-liquid extraction; (7) precipitation/crystalization (including freeze crystallization); or (8) chemical phase separation techniques (i.e., addition of acids, bases, demulsifiers, or similar chemicals); - Note: this does not preclude the use of other physical phase separation techniques such as a decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies. RTHRM: Thermal recovery of metals or inorganics from nonwastewaters in units identified as industrial furnaces according to Chapter 1, 069.1, 069.06, 069.07, 069.11 and 069.12 under the definition of "industrial furnaces". RZINC: Resmelting in high temperature metal recovery units for the purpose of recovery of zinc. STABL: Stabilization with the following reagents (or waste reagents) or combinations of reagents: (1) Portland cement; or (2) lime/pozzolans (e.g., fly ash and cement kiln dust) - this does not preclude the addition of reagents (e.g., iron salts, silicates, and clays) designed to enhance the set/cure time and/or compressive strength, or to overall reduce the leachability of the metal or inorganic. SSTRP: Steam stripping of organics from liquid wastes utilizing direct application of steam to the wastes operated such that liquid and vapor flow rates, as well as, temperature and pressure ranges have been optimized, monitored, and maintained. These operating parameters are dependent upon the design parameters of the unit such as, the number of separation stages and the internal column design. Thus, resulting in a condensed extract high in organics that must undergo either incineration, reuse as a fuel, or other recovery/reuse and an extracted wastewater that must undergo further treatment as specified in the standard. WETOX: Wet air oxidation performed in units operated such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., Total Organic Carbon can often be used as an indicator parameter for the oxidation of many organic constituents that cannot be directly analyzed in wastewater residues). WTRRX: Controlled reaction with water for highly reactive inorganic or organic chemicals with precautionary controls for protection of workers from potential violent reactions as well as precautionary controls for potential emissions of toxic/ignitable levels of gases released during the reaction.

Technology description Performance and/or design and operating standard Contaminant restrictions2 A. Extraction Technologies: 1. Physical Extraction a. Abrasive Blasting: Removal of contaminated debris surface layers using water and/or air pressure to propel a solid media (e.g., steel shot, aluminum oxide grit, plastic beads). Glass, Metal, Plastic, Rubber: Treatment to a clean debris surface.3 Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Removal of at least 0.6 cm of the surface layer; treatment to a clean debris surface.3 All Debris: None. b. Scarification, Grinding, and Planing: Process utilizing striking piston heads, saws, or rotating grinding wheels such that contaminated debris surface layers are removed. Same as above. Same as above. c. Spalling: Drilling or chipping holes at appropriate locations and depth in the contaminated debris surface and applying a tool which exerts a force on the sides of those holes such that the surface layer is removed. The surface layer removed remains hazardous debris subject to the debris treatment standards. Same as above. Same as above. d. Vibratory Finishing: Process utilizing scrubbing media, flushing fluid, and oscillating energy such that hazardous contaminants or contaminated debris surface layers are removed.4 Same as above. Same as above. e. High Pressure Steam and Water Sprays: Application of water or steam sprays of sufficient temperature, pressure, residence time, agitation, surfactants, and detergents to remove hazardous contaminants from debris surfaces or to remove contaminated debris surface layers. Same as above. Same as above. 2. Chemical Extraction a. Water Washing and Spraying: Application of water sprays or water baths of sufficient temperature, pressure, residence time, agitation, surfactants, acids, bases, and detergents to remove hazardous contaminants from debris surfaces and surface pores or to remove contaminated debris surface layers. All Debris: Treatment to a clean debris surface3; Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm ( 1/2 inch) in one dimension (i.e., thickness limit,5 except that this thickness limit may be waived under an "Equivalent Technology" approval under 40 CFR 268.42(b);8 debris surfaces must be in contact with water solution for at least 15 minutes Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Contaminant must be soluble to at least 5% by weight in water solution or 5% by weight in emulsion; if debris is contaminated with a dioxin-listed waste,6 an "Equivalent Technology" approval under 40 CFR 268.42(b) must be obtained.8 b. Liquid Phase Solvent Extraction: Removal of hazardous contaminants from debris surfaces and surface pores by applying a nonaqueous liquid or liquid solution which causes the hazardous contaminants to enter the liquid phase and be flushed away from the debris along with the liquid or liquid solution while using appropriate agitation, temperature, and residence time.4 Same as above. Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Same as above, except that contaminant must be soluble to at least 5% by weight in the solvent. c. Vapor Phase Solvent Extraction: Application of an organic vapor using sufficient agitation, residence time, and temperature to cause hazardous contaminants on contaminated debris surfaces and surface pores to enter the vapor phase and be flushed away with the organic vapor.4 Same as above, except that brick, cloth, concrete, paper, pavement, rock and wood surfaces must be in contact with the organic vapor for at least 60 minutes. Same as above. 3. Thermal Extraction a. High Temperature Metals Recovery: Application of sufficient heat, residence time, mixing, fluxing agents, and/or carbon in a smelting, melting, or refining furnace to separate metals from debris. For refining furnaces, treated debris must be separated from treatment residuals using simple physical or mechanical means,9 and, prior to further treatment, such residuals must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris. Debris contaminated with a dioxin-listed waste:5 Obtain an "Equivalent Technology" approval under 40 CFR 268.42(b).8 b. Thermal Desorption: Heating in an enclosed chamber under either oxidizing or nonoxidizing atmospheres at sufficient temperature and residence time to vaporize hazardous contaminants from contaminated surfaces and surface pores and to remove the contaminants from the heating chamber in a gaseous exhaust gas.7 All Debris: Obtain an "Equivalent Technology" approval under 40 CFR 268.42(b);8 treated debris must be separated from treatment residuals using simple physical or mechanical means,9 and, prior to further treatment, such residue must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris. Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 10 cm (4 inches) in one dimension (i.e., thickness limit),5 except that this thickness limit may be waived under the "Equivalent Technology" approval under 40 CFR 268.42(b). All Debris: Metals other than mercury. B. Destruction Technologies: 1. Biological Destruction (Biodegradation): Removal of hazardous contaminants from debris surfaces and surface pores in an aqueous solution and biodegradation of organic or nonmetallic inorganic compounds (i.e., inorganics that contain phosphorus, nitrogen, or sulfur) in units operated under either aerobic or anaerobic conditions. All Debris: Obtain an "Equivalent Technology" approval under 40 CFR 268.42(b);8 treated debris must be separated from treatment residuals using simple physical or mechanical means,9 and, prior to further treatment, such residue must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris. Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm ( 1/2 inch) in one dimension (i.e., thickness limit),5 except that this thickness limit may be waived under the "Equivalent Technology" approval under 40 CFR 268.42(b). All Debris: Metal contaminants. 2. Chemical Destruction a. Chemical Oxidation: Chemical or electolytic oxidation utilizing the following oxidation reagents (or waste reagents) or combination of reagents-(1) hypochlorite (e.g., bleach); (2) chlorine; (3) chlorine dioxide; (4) ozone or UV (ultraviolet light) assisted ozone; (5) peroxides; (6) persulfates; (7) perchlorates; (8) perman-ganates; and/or (9) other oxidizing reagents of equivalent destruction efficiency.4 Chemical oxidation specifically includes what is referred to as alkaline chlorination. All Debris: Obtain an "Equivalent Technology" approval under 268.42(b);8 treated debris must be separated from treatment residuals using simple physical or mechanical means,9 and, prior to further treatment, such residue must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris. Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm ( 1/2 inch) in one dimension (i.e., thickness limit),5 except that this thickness limit may be waived under the "Equivalent Technology" approval under 40 CFR 268.42(b). All Debris: Metal contaminants. b. Chemical Reduction: Chemical reaction utilizing the following reducing reagents (or waste reagents) or combination of reagents: (1) sulfur dioxide; (2) sodium, potassium, or alkali salts of sulfites, bisulfites, and metabisulfites, and polyethylene glycols (e.g., NaPEG and KPEG); (3) sodium hydrosulfide; (4) ferrous salts; and/or (5) other reducing reagents of equivalent efficiency.4 Same as above. Same as above. 3. Thermal Destruction: Treatment in an incinerator operating in accordance with Section 015 of Chapters 21 or 22; a boiler or industrial furnace operating in accordance with Chapter 7, 010 of this Title, or other thermal treatment unit operated in accordance with Chapter 21, 018, or Chapter 22, 016, but excluding for purposes of these debris treatment standards Thermal Desorption units. Treated debris must be separated from treatment residuals using simple physical or mechanical means,9 and, prior to further treatment, such residue must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris. Brick, Concrete, Glass, Metal, Pavement, Rock, Metal: Metals other than mercury, except that there are no metal restrictions for vitrification. Debris contaminated with a dioxin-listed waste.6 Obtain an "Equivalent Technology" approval under 40 CFR 268.42(b),8 except that this requirement does not apply to vitrification. C. Immobilization Technologies: 1. Macroencapsulation: Application of surface coating materials such as polymeric organics (e.g., resins and plastics) or use of a jacket of inert inorganic materials to substantially reduce surface exposure to potential leaching media. Encapsulating material must completely encapsulate debris and be resistant to degradation by the debris and its contaminants and materials into which it may come into contact after placement (leachate, other waste, microbes). None. 2. Microencapsulation: Stabilization of the debris with the following reagents (or waste reagents) such that the leachability of the hazardous contaminants is reduced: (1) Portland cement; or (2) lime/ pozzolans (e.g., fly ash and cement kiln dust). Reagents (e.g., iron salts, silicates, and clays) may be added to enhance the set/cure time and/or compressive strength, or to reduce the leachability of the hazardous constituents.5 Leachability of the hazardous contaminants must be reduced. None. 3. Sealing: Application of an appropriate material which adheres tightly to the debris surface to avoid exposure of the surface to potential leaching media. When necessary to effectively seal the surface, sealing entails pretreatment of the debris surface to remove foreign matter and to clean and roughen the surface. Sealing materials include epoxy, silicone, and urethane compounds, but paint may not be used as a sealant. Sealing must avoid exposure of the debris surface to potential leaching media and sealant must be resistant to degradation by the debris and its contaminants and materials into which it may come into contact after placement (leachate, other waste, microbes). None.

Table 12 - Universal Treatment Standards

Regulated constituent/common name CAS1 number Wastewater standard Nonwastewater standard Concentration in mg/l2 Concentration in mg/kg3 unless noted as "mg/l TCLP" I. Organic Constituents: Acenaphthylene 208-96-8 0.059 3.4 Acenaphthene 83-32-9 0.059 3.4 Acetone 67-64-1 0.28 160 Acetonitrile 75-05-8 5.6 38 Acetophenone 96-86-2 0.010 9.7 2-Acetylaminofluorene 53-96-3 0.059 140 Acrolein 107-02-8 0.29 NA Acrylamide 79-06-1 19 23 Acrylonitrile 107-13-1 0.24 84 Aldicarb sulfone6 1646-88-4 0.056 0.28 Aldrin 309-00-2 0.021 0.066 4-Aminobiphenyl 92-67-1 0.13 NA Aniline 62-53-3 0.81 14 o-Anisidine (2—methoxyaniline) 90-04-0 0.010 0.66 Anthracene 120-12-7 0.059 3.4 Aramite 140-57-8 0.36 NA alpha-BHC 319-84-6 0.00014 0.066 beta-BHC 319-85-7 0.00014 0.066 delta-BHC 319-86-8 0.023 0.066 gamma-BHC 58-89-9 0.0017 0.066 Barban6 101-27-9 0.056 1.4 Bendiocarb6 22781-23-3 0.056 1.4 Benomyl6 17804-35-2 0.056 1.4 Benzene 71-43-2 0.14 10 Benz(a)anthracene 56-55-3 0.059 3.4 Benzal chloride 98-87-3 0.055 6.0 Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) 205-99-2 0.11 6.8 Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) 207-08-9 0.11 6.8 Benzo(g,h,i)perylene 191-24-2 0.0055 1.8 Benzo(a)pyrene 50-32-8 0.061 3.4 Bromodichloromethane 75-27-4 0.35 15 Bromomethane/Methyl bromide 74-83-9 0.11 15 4-Bromophenyl phenyl ether 101-55-3 0.055 15 n-Butyl alcohol 71-36-3 5.6 2.6 Butylate6 2008-41-5 0.042 1.4 Butyl benzyl phthalate 85-68-7 0.017 28 2-sec-Butyl-4,6-dinitrophenol/Dinoseb 88-85-7 0.066 2.5 Carbaryl6 63-25-2 0.006 0.14 Carbenzadim6 10605-21-7 0.056 1.4 Carbofuran6 1563-66-2 0.006 0.14 Carbofuran phenol6 1563-38-8 0.056 1.4 Carbon disulfide 75-15-0 3.8 4.8 mg/l TCLP Carbon tetrachloride 56-23-5 0.057 6.0 Carbosulfan6 55285-14-8 0.028 1.4 Chlordane (alpha and gamma isomers) 57-74-9 0.0033 0.26 p-Chloroaniline 106-47-8 0.46 16 Chlorobenzene 108-90-7 0.057 6.0 Chlorobenzilate 510-15-6 0.10 NA 2-Chloro-1,3-butadiene 126-99-8 0.057 0.28 Chlorodibromomethane 124-48-1 0.057 15 Chloroethane 75-00-3 0.27 6.0 bis(2-Chloroethoxy)methane 111-91-1 0.036 7.2 bis(2-Chloroethyl)ether 111-44-4 0.033 6.0 Chloroform 67-66-3 0.046 6.0 bis(2-Chloroisopropyl)ether 39638-32-9 0.055 7.2 p-Chloro-m-cresol 59-50-7 0.018 14 2-Chloroethyl vinyl ether 110-75-8 0.062 NA Chloromethane/Methyl chloride 74-87-3 0.19 30 2-Chloronaphthalene 91-58-7 0.055 5.6 2-Chlorophenol 95-57-8 0.044 5.7 3-Chloropropylene 107-05-1 0.036 30 Chrysene 218-01-9 0.059 3.4 p-Cresidine 120-71-8 0.010 0.66 o-Cresol 95-48-7 0.11 5.6 m-Cresol (difficult to distinguish from p-cresol) 108-39-4 0.77 5.6 p-Cresol (difficult to distinguish from m-cresol) 106-44-5 0.77 5.6 m-Cumenyl methylcarbamate6 64-00-6 0.056 1.4 Cyclohexanone 108-94-1 0.36 0.75 mg/l TCLP o,p'-DDD 53-19-0 0.023 0.087 p,p'-DDD 72-54-8 0.023 0.087 o,p'-DDE 3424-82-6 0.031 0.087 p,p'-DDE 72-55-9 0.031 0.087 o,p'-DDT 789-02-6 0.0039 0.087 p,p'-DDT 50-29-3 0.0039 0.087 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 Dibenz(a,e)pyrene 192-65-4 0.061 NA 1,2-Dibromo-3-chloropropane 96-12-8 0.11 15 1,2-Dibromoethane/Ethylene dibromide 106-93-4 0.028 15 Dibromomethane 74-95-3 0.11 15 m-Dichlorobenzene 541-73-1 0.036 6.0 o-Dichlorobenzene 95-50-1 0.088 6.0 p-Dichlorobenzene 106-46-7 0.090 6.0 Dichlorodifluoromethane 75-71-8 0.23 7.2 1,1-Dichloroethane 75-34-3 0.059 6.0 1,2-Dichloroethane 107-06-2 0.21 6.0 1,1-Dichloroethylene 75-35-4 0.025 6.0 trans-1,2-Dichloroethylene 156-60-5 0.054 30 2,4-Dichlorophenol 120-83-2 0.044 14 2,6-Dichlorophenol 87-65-0 0.044 14 2,4-Dichlorophenoxyacetic acid/2,4-D 94-75-7 0.72 10 1,2-Dichloropropane 78-87-5 0.85 18 cis-1,3-Dichloropropylene 10061-01-5 0.036 18 trans-1,3-Dichloropropylene 10061-02-6 0.036 18 Dieldrin 60-57-1 0.017 0.13 Diethyl phthalate 84-66-2 0.20 28 p-Dimethylaminoazobenzene 60-11-7 0.13 NA 2,4-Dimethylaniline (2,4-xylidine) 95-68-1 0.010 0.66 2-4-Dimethyl phenol 105-67-9 0.036 14 Dimethyl phthalate 131-11-3 0.047 28 Di-n-butyl phthalate 84-74-2 0.057 28 1,4-Dinitrobenzene 100-25-4 0.32 2.3 4,6-Dinitro-o-cresol 534-52-1 0.28 160 2,4-Dinitrophenol 51-28-5 0.12 160 2,4-Dinitrotoluene 121-14-2 0.32 140 2,6-Dinitrotoluene 606-20-2 0.55 28 Di-n-octyl phthalate 117-84-0 0.017 28 Di-n-propylnitrosamine 621-64-7 0.40 14 1,4-Dioxane 123-91-1 12.0 170 Diphenylamine (difficult to distinguish from diphenylnitrosamine) 122-39-4 0.92 13 Diphenylnitrosamine (difficult to distinguish from diphenylamine) 86-30-6 0.92 13 1,2-Diphenylhydrazine 122-66-7 0.087 NA Disulfoton 298-04-4 0.017 6.2 Dithiocarbamates6 (total) NA 0.028 28 Endosulfan I 959-98-8 0.023 0.066 Endosulfan II 33213-65-9 0.029 0.13 Endosulfan sulfate 1031-07-8 0.029 0.13 Endrin 72-20-8 0.0028 0.13 Endrin aldehyde 7421-93-4 0.025 0.13 EPTC6 759-94-4 0.042 1.4 Ethyl acetate 141-78-6 0.34 33 Ethyl benzene 100-41-4 0.057 10 Ethyl cyanide/Propanenitrile 107-12-0 0.24 360 Ethyl ether 60-29-7 0.12 160 bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28 Ethyl methacrylate 97-63-2 0.14 160 Ethylene oxide 75-21-8 0.12 NA Famphur 52-85-7 0.017 15 Fluoranthene 206-44-0 0.068 3.4 Fluorene 86-73-7 0.059 3.4 Formetanate hydrochloride6 23422-53-9 0.056 1.4 Heptachlor 76-44-8 0.0012 0.066 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD) 35822-46-9 0.000035 0.0025 1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF) 67562-39-4 0.000035 0.0025 1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF) 55673-89-7 0.000035 0.0025 Heptachlor epoxide 1024-57-3 0.016 0.066 Hexachlorobenzene 118-74-1 0.055 10 Hexachlorobutadiene 87-68-3 0.055 5.6 Hexachlorocyclopentadiene 77-47-4 0.057 2.4 HxCDDs (All Hexachlorodibenzo-p-dioxins) NA 0.000063 0.001 HxCDFs (All Hexachlorodibenzofurans) NA 0.000063 0.001 Hexachloroethane 67-72-1 0.055 30 Hexachloropropylene 1888-71-7 0.035 30 Indeno (1,2,3-c,d) pyrene 193-39-5 0.0055 3.4 Iodomethane 74-88-4 0.19 65 Isobutyl alcohol 78-83-1 5.6 170 Isodrin 465-73-6 0.021 0.066 Isosafrole 120-58-1 0.081 2.6 Kepone 143-50-0 0.0011 0.13 Methacrylonitrile 126-98-7 0.24 84 Methanol 67-56-1 5.6 0.75 mg/l TCLP Methapyrilene 91-80-5 0.081 1.5 Methiocarb6 2032-65-7 0.056 1.4 Methomyl6 16752-77-5 0.028 0.14 Methoxychlor 72-43-5 0.25 0.18 3-Methylcholanthrene 56-49-5 0.0055 15 4,4-Methylene bis(2-chloroaniline) 101-14-4 0.50 30 Methylene chloride 75-09-2 0.089 30 Methyl ethyl ketone 78-93-3 0.28 36 Methyl isobutyl ketone 108-10-1 0.14 33 Methyl methacrylate 80-62-6 0.14 160 Methyl methansulfonate 66-27-3 0.018 NA Methyl parathion 298-00-0 0.014 4.6 Metolcarb6 1129-41-5 0.056 1.4 Mexacarbate6 315-18-4 0.056 1.4 Molinate6 2212-67-1 0.042 1.4 Naphthalene 91-20-3 0.059 5.6 2-Naphthylamine 91-59-8 0.52 NA o-Nitroaniline 88-74-4 0.27 14 p-Nitroaniline 100-01-6 0.028 28 Nitrobenzene 98-95-3 0.068 14 5-Nitro-o-toluidine 99-55-8 0.32 28 o-Nitrophenol 88-75-5 0.028 13 p-Nitrophenol 100-02-7 0.12 29 N-Nitrosodiethylamine 55-18-5 0.40 28 N-Nitrosodimethylamine 62-75-9 0.40 2.3 N-Nitroso-di-n-butylamine 924-16-3 0.40 17 N-Nitrosomethylethylamine 10595-95-6 0.40 2.3 N-Nitrosomorpholine 59-89-2 0.40 2.3 N-Nitrosopiperidine 100-75-4 0.013 35 N-Nitrosopyrrolidine 930-55-2 0.013 35 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (OCDD) 3268-87-9 0.000063 0.005 1,2,3,4,6,7,8,9-Octachlorodibenzofuran (OCDF) 39001-02-0 0.000063 0.005 Oxamyl6 23135-22-0 0.056 0.28 Parathion 56-38-2 0.014 4.6 Total PCBs (sum of all PCB isomers, or all Aroclors)8 1336-36-3 0.10 10 Pebulate6 1114-71-2 0.042 1.4 Pentachlorobenzene 608-93-5 0.055 10 PeCDDs (All Pentachlorodibenzo-p-dioxins) NA 0.000063 0.001 PeCDFs (All Pentachlorodibenzofurans) NA 0.000035 0.001 Pentachloroethane 76-01-7 0.055 6.0 Pentachloronitrobenzene 82-68-8 0.055 4.8 Pentachlorophenol 87-86-5 0.089 7.4 Phenacetin 62-44-2 0.081 16 Phenanthrene 85-01-8 0.059 5.6 1,3-Phenylenediamine 108-45-2 0.010 0.66 Phenol 108-95-2 0.039 6.2 Phorate 298-02-2 0.021 4.6 Phthalic acid 100-21-0 0.055 28 Phthalic anhydride 85-44-9 0.055 28 Physostigmine6 57-47-6 0.056 1.4 Physostigmine salicylate6 57-64-7 0.056 1.4 Promecarb6 2631-37-0 0.056 1.4 Pronamide 23950-58-5 0.093 1.5 Propham6 122-42-9 0.056 1.4 Propoxur6 114-26-1 0.056 1.4 Prosulfocarb6 52888-80-9 0.042 1.4 Pyrene 129-00-0 0.067 8.2 Pyridine 110-86-1 0.014 16 Safrole 94-59-7 0.081 22 Silvex/2,4,5-TP 93-72-1 0.72 7.9 1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14 TCDDs (All Tetrachlorodibenzo-p-dioxins) NA 0.000063 0.001 TCDFs (All Tetrachlorodibenzofurans) NA 0.000063 0.001 1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0 1,1,2,2-Tetrachloroethane 79-34-5 0.057 6.0 Tetrachloroethylene 127-18-4 0.056 6.0 2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4 Thiodicarb6 59669-26-0 0.019 1.4 Thiophanate-methyl6 23564-05-8 0.056 1.4 Toluene 108-88-3 0.080 10 Toxaphene 8001-35-2 0.0095 2.6 Triallate6 2303-17-5 0.042 1.4 Tribromomethane/Bromoform 75-25-2 0.63 15 1,2,4-Trichlorobenzene 120-82-1 0.055 19 1,1,1-Trichloroethane 71-55-6 0.054 6.0 1,1,2-Trichloroethane 79-00-5 0.054 6.0 Trichloroethylene 79-01-6 0.054 6.0 Trichloromonofluoromethane 75-69-4 0.020 30 2,4,5-Trichlorophenol 95-95-4 0.18 7.4 2,4,6-Trichlorophenol 88-06-2 0.035 7.4 2,4,5-Trichlorophenoxyacetic acid/2,4,5-T 93-76-5 0.72 7.9 1,2,3-Trichloropropane 96-18-4 0.85 30 1,1,2-Trichloro-1,2,2-trifluoroethane 76-13-1 0.057 30 Triethylamine6 121-44-8 0.081 1.5 tris-(2,3-Dibromopropyl) phosphate 126-72-7 0.11 0.10 Vernolate6 1929-77-7 0.042 1.4 Vinyl chloride 75-01-4 0.27 6.0 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 II. Inorganic Constituents: Antimony 7440-36-0 1.9 1.15 mg/l TCLP Arsenic 7440-38-2 1.4 5.0 mg/l TCLP Barium 7440-39-3 1.2 21 mg/l TCLP Beryllium 7440-41-7 0.82 1.22 mg/l TCLP Cadmium 7440-43-9 0.69 0.11 mg/l TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/l TCLP Cyanides (Total)4 57-12-5 1.2 590 Cyanides (Amenable)4 57-12-5 0.86 30 Fluoride5 16984-48-8 35 NA Lead 7439-92-1 0.69 0.75 mg/l TCLP Mercury - Nonwastewater from Retort 7439-97-6 NA 0.20 mg/l TCLP Mercury - All Others 7439-97-6 0.15 0.025 mg/l TCLP Nickel 7440-02-0 3.98 11 mg/l TCLP Selenium7 7782-49-2 0.82 5.7 mg/l TCLP Silver 7440-22-4 0.43 0.14 mg/l TCLP Sulfide5 18496-25-8 14 NA Thallium 7440-28-0 1.4 0.20 mg/l TCLP Vanadium5 7440-62-2 4.3 1.6 mg/l TCLP Zinc5 7440-66-6 2.61 4.3 mg/l TCLP

If LDRs And if LDRs And if Then you Applied to the listed waste when it contaminated the soil* Apply to the listed waste now ___ Must comply with LDRs Didn’t apply to the listed waste when it contaminated the soil* Apply to the listed waste now The soil is determined to contain the listed waste when the soil is first generated Must comply with LDRs Didn’t apply to the listed waste when it contaminated the soil* Apply to the listed waste now The soil is determined not to contain the listed waste when the soil is first generated Needn’t comply with the LDRs Didn’t apply to the listed waste when it contaminated the soil* Don’t apply to the listed waste now ___ Needn’t comply with the LDRs