010 Treatment standards expressed as specified technologies.

Table 10 - Technology Codes and Description of Technology-Based Standards
Technology code
Description of technology-based standards
Organic Constituents
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.

Note 1: When a combination of these technologies (i.e., a treatment train) is specified as a single treatment standard, the order of application is specified in Table 10, Technology codes and Description of Technology-Based Standards, of this Title, by indicating the five letter technology code that must be applied first, then the designation "fb." (an abbreviation for "followed by"), then the five letter technology code for the technology that must be applied next, and so on.

Note 2: When more than one technology (or treatment train) are specified as alternative treatment standards, the five letter technology codes (or the treatment trains) are separated by a semicolon (;) with the last technology preceded by the word "OR". This indicates that any one of these BDAT technologies or treatment trains can be used for compliance with the standard.

011 Treatment standards for hazardous debris.
1Hazardous debris must be treated by either these standards or the waste-specific treatment standards for the waste contaminating the debris. The treatment standards must be met for each type of debris contained in a mixture of debris types, unless the debris is converted into treatment residue as a result of the treatment process. Debris treatment residuals are subject to the waste-specific treatment standards for the waste contaminating the debris.
2Contaminant restriction means that the technology is not BDAT for that contaminant. If debris containing a restricted contaminant is treated by the technology, the contaminant must be subsequently treated by a technology for which it is not restricted in order to be land disposed (and excluded from Subtitle C regulation).
3"Clean debris surface" means the surface, when viewed without magnification, shall be free of all visible contaminated soil and hazardous waste except that residual staining from soil and waste consisting of light shadows, slight streaks, or minor discolorations, and soil and waste in cracks, crevices, and pits may be present provided that such staining and waste and soil in cracks, crevices, and pits shall be limited to no more than 5% of each square inch of surface area.
4Acids, solvents, and chemical reagents may react with some debris and contaminants to form hazardous compounds. For example, acid washing of cyanide-contaminated debris could result in the formation of hydrogen cyanide. Some acids may also react violently with some debris and contaminants, depending on the concentration of the acid and the type of debris and contaminants. Debris treaters should refer to the safety precautions specified in Material Safety Data Sheets for various acids to avoid applying an incompatible acid to a particular debris/contaminant combination. For example, concentrated sulfuric acid may react violently with certain organic compounds, such as acrylonitrile.
5If reducing the particle size of debris to meet the treatment standards results in material that no longer meets the 60 mm minimum particle size limit for debris, such material is subject to the waste-specific treatment standards for the waste contaminating the material, unless the debris has been cleaned and separated from contaminated soil and waste prior to size reduction. At a minimum, simple physical or mechanical means must be used to provide such cleaning and separation of nondebris materials to ensure that the debris surface is free of caked soil, waste, or other nondebris material.
6Dioxin-listed wastes are EPA Hazardous Waste numbers FO20, FO21, FO22, FO23, FO26, and FO27.
7Thermal desorption is distinguished from Thermal Destruction in that the primary purpose of Thermal Desorption is to volatilize contaminants and to remove them from the treatment chamber for subsequent destruction or other treatment.
8The demonstration "Equivalent Technology" under 40 CFR 268.42(b) as incorporated by reference in Section 009.02, must document that the technology treats contaminants subject to treatment to a level equivalent to that required by the performance and design and operating standards for other technologies in this table such that residual levels of hazardous contaminants will not pose a hazard to human health and the environment absent management controls.
9Any soil, waste, and other nondebris material that remains on the debris surface (or remains mixed with the debris) after treatment is considered a treatment residual that must be separated from the debris using, at a minimum, simple physical or mechanical means. Examples of simple physical or mechanical means are vibratory or trommel screening or water washing. The debris surface need not be cleaned to a "clean debris surface" as defined in note 3 when separating treated debris from residue; rather, the surface must be free of caked soil, waste, or other nondebris material. Treatment residuals are subject to the waste-specific treatment standards for the waste contaminating the debris.

012 Universal Treatment Standards

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
0.0593.4
Acenaphthene
83-32-9
0.0593.4
Acetone
67-64-1
0.28160
Acetonitrile
75-05-8
5.638
Acetophenone
96-86-2
0.0109.7
2-Acetylaminofluorene
53-96-3
0.059140
Acrolein
107-02-8
0.29NA
Acrylamide
79-06-1
1923
Acrylonitrile
107-13-1
0.2484
Aldicarb sulfone6
1646-88-4
0.0560.28
Aldrin
309-00-2
0.0210.066
4-Aminobiphenyl
92-67-1
0.13NA
Aniline
62-53-3
0.8114
Anisidine (2—methoxyaniline)
90-04-0
0.0100.66
Anthracene
120-12-7
0.0593.4
Aramite
140-57-8
0.36NA
alpha-BHC
319-84-6
0.000140.066
beta-BHC
319-85-7
0.000140.066
delta-BHC
319-86-8
0.0230.066
gamma-BHC
58-89-9
0.00170.066
Barban6
101-27-9
0.0561.4
Bendiocarb6
22781-23-3
0.0561.4
Benomyl6
17804-35-2
0.0561.4
Benzene
71-43-2
0.1410
Benz(a)anthracene
56-55-3
0.0593.4
Benzal chloride
98-87-3
0.0556.0
Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)
205-99-2
0.116.8
Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)
207-08-9
0.116.8
Benzo(g,h,i)perylene
191-24-2
0.00551.8
Benzo(a)pyrene
50-32-8
0.0613.4
Bromodichloromethane
75-27-4
0.3515
Bromomethane/Methyl bromide
74-83-9
0.1115
4-Bromophenyl phenyl ether
101-55-3
0.05515
n-Butyl alcohol
71-36-3
5.62.6
Butylate6
2008-41-5
0.0421.4
Butyl benzyl phthalate
85-68-7
0.01728
2-sec-Butyl-4,6-dinitrophenol/Dinoseb
88-85-7
0.0662.5
Carbaryl6
63-25-2
0.0060.14
Carbenzadim6
10605-21-7
0.0561.4
Carbofuran6
1563-66-2
0.0060.14
Carbofuran phenol6
1563-38-8
0.0561.4
Carbon disulfide
75-15-0
3.84.8 mg/l TCLP
Carbon tetrachloride
56-23-5
0.0576.0
Carbosulfan6
55285-14-8
0.0281.4
Chlordane (alpha and gamma isomers)
57-74-9
0.00330.26
p-Chloroaniline
106-47-8
0.4616
Chlorobenzene
108-90-7
0.0576.0
Chlorobenzilate
510-15-6
0.10NA
2-Chloro-1,3-butadiene
126-99-8
0.0570.28
Chlorodibromomethane
124-48-1
0.05715
Chloroethane
75-00-3
0.276.0
bis(2-Chloroethoxy)methane
111-91-1
0.0367.2
bis(2-Chloroethyl)ether
111-44-4
0.0336.0
Chloroform
67-66-3
0.0466.0
bis(2-Chloroisopropyl)ether
39638-32-9
0.0557.2
p-Chloro-m-cresol
59-50-7
0.01814
2-Chloroethyl vinyl ether
110-75-8
0.062NA
Chloromethane/Methyl chloride
74-87-3
0.1930
2-Chloronaphthalene
91-58-7
0.0555.6
2-Chlorophenol
95-57-8
0.0445.7
3-Chloropropylene
107-05-1
0.03630
Chrysene
218-01-9
0.0593.4
p-Cresidine
120-71-8
0.0100.66
o-Cresol
95-48-7
0.115.6
m-Cresol (difficult to distinguish from p-cresol)
108-39-4
0.775.6
p-Cresol (difficult to distinguish from m-cresol)
106-44-5
0.775.6
m-Cumenyl methylcarbamate6
64-00-6
0.0561.4
Cyclohexanone
108-94-1
0.360.75 mg/l TCLP
o,p'-DDD
53-19-0
0.0230.087
p,p'-DDD
72-54-8
0.0230.087
o,p'-DDE
3424-82-6
0.0310.087
p,p'-DDE
72-55-9
0.0310.087
o,p'-DDT
789-02-6
0.00390.087
p,p'-DDT
50-29-3
0.00390.087
Dibenz(a,h)anthracene
53-70-3
0.0558.2
Dibenz(a,e)pyrene
192-65-4
0.061NA
1,2-Dibromo-3-chloropropane
96-12-8
0.1115
1,2-Dibromoethane/Ethylene dibromide
106-93-4
0.02815
Dibromomethane
74-95-3
0.1115
m-Dichlorobenzene
541-73-1
0.0366.0
o-Dichlorobenzene
95-50-1
0.0886.0
p-Dichlorobenzene
106-46-7
0.0906.0
Dichlorodifluoromethane
75-71-8
0.237.2
1,1-Dichloroethane
75-34-3
0.0596.0
1,2-Dichloroethane
107-06-2
0.216.0
1,1-Dichloroethylene
75-35-4
0.0256.0
trans-1,2-Dichloroethylene
156-60-5
0.05430
2,4-Dichlorophenol
120-83-2
0.04414
2,6-Dichlorophenol
87-65-0
0.04414
2,4-Dichlorophenoxyacetic acid/2,4-D
94-75-7
0.7210
1,2-Dichloropropane
78-87-5
0.8518
cis-1,3-Dichloropropylene
10061-01-5
0.03618
trans-1,3-Dichloropropylene
10061-02-6
0.03618
Dieldrin
60-57-1
0.0170.13
Diethyl phthalate
84-66-2
0.2028
p-Dimethylaminoazobenzene
60-11-7
0.13NA
2,4-Dimethylaniline (2,4-xylidine)
95-68-1
0.0100.66
2-4-Dimethyl phenol
105-67-9
0.03614
Dimethyl phthalate
131-11-3
0.04728
Di-n-butyl phthalate
84-74-2
0.05728
1,4-Dinitrobenzene
100-25-4
0.322.3
4,6-Dinitro-o-cresol
534-52-1
0.28160
2,4-Dinitrophenol
51-28-5
0.12160
2,4-Dinitrotoluene
121-14-2
0.32140
2,6-Dinitrotoluene
606-20-2
0.5528
Di-n-octyl phthalate
117-84-0
0.01728
Di-n-propylnitrosamine
621-64-7
0.4014
1,4-Dioxane
123-91-1
12.0170
Diphenylamine (difficult to distinguish from diphenylnitrosamine)
122-39-4
0.9213
Diphenylnitrosamine (difficult to distinguish from diphenylamine)
86-30-6
0.9213
1,2-Diphenylhydrazine
122-66-7
0.087NA
Disulfoton
298-04-4
0.0176.2
Dithiocarbamates6 (total)
NA
0.02828
Endosulfan I
959-98-8
0.0230.066
Endosulfan II
33213-65-9
0.0290.13
Endosulfan sulfate
1031-07-8
0.0290.13
Endrin
72-20-8
0.00280.13
Endrin aldehyde
7421-93-4
0.0250.13
EPTC6
759-94-4
0.0421.4
Ethyl acetate
141-78-6
0.3433
Ethyl benzene
100-41-4
0.05710
Ethyl cyanide/Propanenitrile
107-12-0
0.24360
Ethyl ether
60-29-7
0.12160
bis(2-Ethylhexyl) phthalate
117-81-7
0.2828
Ethyl methacrylate
97-63-2
0.14160
Ethylene oxide
75-21-8
0.12NA
Famphur
52-85-7
0.01715
Fluoranthene
206-44-0
0.0683.4
Fluorene
86-73-7
0.0593.4
Formetanate hydrochloride6
23422-53-9
0.0561.4
Heptachlor
76-44-8
0.00120.066
1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD)
35822-46-9
0.0000350.0025
1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF)
67562-39-4
0.0000350.0025
1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF)
55673-89-7
0.0000350.0025
Heptachlor epoxide
1024-57-3
0.0160.066
Hexachlorobenzene
118-74-1
0.05510
Hexachlorobutadiene
87-68-3
0.0555.6
Hexachlorocyclopentadiene
77-47-4
0.0572.4
HxCDDs (All Hexachlorodibenzo-p-dioxins)
NA
0.0000630.001
HxCDFs (All Hexachlorodibenzofurans)
NA
0.0000630.001
Hexachloroethane
67-72-1
0.05530
Hexachloropropylene
1888-71-7
0.03530
Indeno (1,2,3-c,d) pyrene
193-39-5
0.00553.4
Iodomethane
74-88-4
0.1965
Isobutyl alcohol
78-83-1
5.6170
Isodrin
465-73-6
0.0210.066
Isosafrole
120-58-1
0.0812.6
Kepone
143-50-0
0.00110.13
Methacrylonitrile
126-98-7
0.2484
Methanol
67-56-1
5.60.75 mg/l TCLP
Methapyrilene
91-80-5
0.0811.5
Methiocarb6
2032-65-7
0.0561.4
Methomyl6
16752-77-5
0.0280.14
Methoxychlor
72-43-5
0.250.18
3-Methylcholanthrene
56-49-5
0.005515
4,4-Methylene bis(2-chloroaniline)
101-14-4
0.5030
Methylene chloride
75-09-2
0.08930
Methyl ethyl ketone
78-93-3
0.2836
Methyl isobutyl ketone
108-10-1
0.1433
Methyl methacrylate
80-62-6
0.14160
Methyl methansulfonate
66-27-3
0.018NA
Methyl parathion
298-00-0
0.0144.6
Metolcarb6
1129-41-5
0.0561.4
Mexacarbate6
315-18-4
0.0561.4
Molinate6
2212-67-1
0.0421.4
Naphthalene
91-20-3
0.0595.6
2-Naphthylamine
91-59-8
0.52NA
o-Nitroaniline
88-74-4
0.2714
p-Nitroaniline
100-01-6
0.02828
Nitrobenzene
98-95-3
0.06814
5-Nitro-o-toluidine
99-55-8
0.3228
o-Nitrophenol
88-75-5
0.02813
p-Nitrophenol
100-02-7
0.1229
N-Nitrosodiethylamine
55-18-5
0.4028
N-Nitrosodimethylamine
62-75-9
0.402.3
N-Nitroso-di-n-butylamine
924-16-3
0.4017
N-Nitrosomethylethylamine
10595-95-6
0.402.3
N-Nitrosomorpholine
59-89-2
0.402.3
N-Nitrosopiperidine
100-75-4
0.01335
N-Nitrosopyrrolidine
930-55-2
0.01335
1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (OCDD)
3268-87-9
0.0000630.005
1,2,3,4,6,7,8,9-Octachlorodibenzofuran (OCDF)
39001-02-0
0.0000630.005
Oxamyl6
23135-22-0
0.0560.28
Parathion
56-38-2
0.0144.6
Total PCBs (sum of all PCB isomers, or all Aroclors)8
1336-36-3
0.1010
Pebulate6
1114-71-2
0.0421.4
    Pentachlorobenzene
608-93-5
0.05510
PeCDDs (All Pentachlorodibenzo-p-dioxins)
NA
0.0000630.001
PeCDFs (All Pentachlorodibenzofurans)
NA
0.0000350.001
Pentachloroethane
76-01-7
0.0556.0

    Pentachloronitrobenzene
82-68-8
0.0554.8
    Pentachlorophenol
87-86-5
0.0897.4
Phenacetin
62-44-2
0.08116
Phenanthrene
85-01-8
0.0595.6
1,3-Phenylenediamine
108-45-2
0.0100.66
Phenol
108-95-2
0.0396.2
Phorate
298-02-2
0.0214.6
Phthalic acid
100-21-0
0.05528
Phthalic anhydride
85-44-9
0.05528
Physostigmine6
57-47-6
0.0561.4
Physostigmine salicylate6
57-64-7
0.0561.4
Promecarb6
2631-37-0
0.0561.4
Pronamide
23950-58-5
0.0931.5
Propham6
122-42-9
0.0561.4
Propoxur6
114-26-1
0.0561.4
Prosulfocarb6
52888-80-9
0.0421.4
Pyrene
129-00-0
0.0678.2
Pyridine
110-86-1
0.01416
Safrole
94-59-7
0.08122
Silvex/2,4,5-TP
93-72-1
0.727.9
1,2,4,5-Tetrachlorobenzene
95-94-3
0.05514
TCDDs (All Tetrachlorodibenzo-p-dioxins)
NA
0.0000630.001
TCDFs (All Tetrachlorodibenzofurans)
NA
0.0000630.001
1,1,1,2-Tetrachloroethane
630-20-6
0.0576.0
1,1,2,2-Tetrachloroethane
79-34-5
0.0576.0
Tetrachloroethylene
127-18-4
0.0566.0
2,3,4,6-Tetrachlorophenol
58-90-2
0.0307.4
Thiodicarb6
59669-26-0
0.0191.4
Thiophanate-methyl6
23564-05-8
0.0561.4
Toluene
108-88-3
0.08010
Toxaphene
8001-35-2
0.00952.6
Triallate6
2303-17-5
0.0421.4
Tribromomethane/Bromoform
75-25-2
0.6315
1,2,4-Trichlorobenzene
120-82-1
0.05519
1,1,1-Trichloroethane
71-55-6
0.0546.0
1,1,2-Trichloroethane
79-00-5
0.0546.0
Trichloroethylene
79-01-6
0.0546.0
Trichloromonofluoromethane
75-69-4
0.02030
2,4,5-Trichlorophenol
95-95-4
0.187.4
2,4,6-Trichlorophenol
88-06-2
0.0357.4
2,4,5-Trichlorophenoxyacetic acid/2,4,5-T
93-76-5
0.727.9
1,2,3-Trichloropropane
96-18-4
0.8530
1,1,2-Trichloro-1,2,2-trifluoroethane
76-13-1
0.05730
Triethylamine6
101-44-8
0.0811.5
tris-(2,3-Dibromopropyl) phosphate
126-72-7
0.110.10
Vernolate6
1929-77-7
0.0421.4
Vinyl chloride
75-01-4
0.276.0
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)
1330-20-7
0.3230
II. Inorganic Constituents:
    Antimony
7440-36-0
1.91.15 mg/l TCLP
Arsenic
7440-38-2
1.45.0 mg/l TCLP
Barium
7440-39-3
1.221 mg/l TCLP
Beryllium
7440-41-7
0.821.22 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
1.2590
Cyanides (Amenable)4
57-12-5
0.8630
Fluoride5
16984-48-8
35NA
Lead
7439-92-1
0.690.75 mg/l TCLP
Mercury - Nonwastewater from Retort
7439-97-6
NA0.20 mg/l TCLP
Mercury - All Others
7439-97-6
0.150.025 mg/l TCLP
Nickel
7440-02-0
3.9811 mg/l TCLP
Selenium7
7782-49-2
0.825.7 mg/l TCLP
Silver
7440-22-4
0.430.14 mg/l TCLP
Sulfide5
18496-25-8
14NA
Thallium
7440-28-0
1.40.20 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

Footnotes to Universal Treatment Standards Table:
NA means Not Applicable
1 CAS means Chemical Abstract Services. When the waste code and/or regulated constituents are described as a combination of a chemical with its salts and/or esters, the CAS number is given for the parent compound only.
2 Concentration standards for wastewaters are expressed in mg/l and are based on analysis of composite samples.
3 Except for Metals (EP or TCLP) and Cyanides (Total and Amenable) the nonwastewater treatment standards expressed as a concentration were established, in part, based upon incineration in units operated in accordance with the technical requirements of Chapter 21, 015 or Chapter 22, 015, or based upon combustion in fuel substitution units operating in accordance with applicable technical requirements. A facility may comply with these treatment standards according to provisions in Section 009. All concentration standards for nonwastewaters are based on analysis of grab samples.
4 Both Cyanides (Total) and Cyanides (Amenable) for nonwastewaters are to be analyzed using Method 9010C or 9012B, found in "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods", EPA Publication SW-846, as incorporated by reference in Chapter 1, with a sample size of 10 grams and a distillation time of one hour and 15 minutes.
5 These constituents are not "underlying hazardous constituents" in characteristic wastes, according to the definition at Section 002.09.
6 Between August 26, 1996, and March 4, 1998, these constituents are not “underlying hazardous constituents” as defined in Section 002.09.
7 This constituent is not an underlying hazardous constituent as defined in Section 002.09 because its UTS level is greater than its TC level, thus a treated selenium waste would always be characteristically hazardous, unless it is treated to below its characteristic level.
8 This standard is temporarily deferred for soil exhibiting a hazardous characteristic due to D004-D011 only.

013 Alternative LDR treatment standards for contaminated soil.

013.01 Applicability. You must comply with LDRs prior to placing soil that exhibits a characteristic of hazardous waste, or exhibited
a characteristic of hazardous waste at the time it was generated, into a land disposal unit. The following chart describes whether you must comply with LDRs prior to placing soil contaminated by listed hazardous waste into a land disposal unit:
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 nowThe soil is determined to contain the listed waste when the soil is first generatedMust comply with LDRs
Didn’t apply to the listed waste when it contaminated the soil*Apply to the listed waste nowThe soil is determined not to contain the listed waste when the soil is first generatedNeedn’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
*For dates of LDR applicability, see 40 CFR Part 268 Appendix VII. To determine the date any given listed hazardous waste contaminated any given volume of soil, use the last date any given listed hazardous waste was placed into any given land disposal unit or, in the case of an accidental spill, the date of the spill.

013.02 Prior to land disposal, contaminated soil identified by paragraph 013.01 of this section as needing to comply with LDRs must be treated according to the applicable treatment standards specified in paragraph 013.03 of this section or according to the Universal Treatment Standards specified in Section 012 applicable to the contaminating listed hazardous waste and/or the applicable characteristic of hazardous waste if the soil is characteristic. The treatment standards specified in paragraph 013.03 of this section and the Universal Treatment Standards may be modified through a treatment variance approved in accordance with Chapter 5, 006.

013.03 Treatment standards for contaminated soils. Prior to land disposal, contaminated soil identified by paragraph 013.01 of this section as needing to comply with LDRs must be treated according to all the standards specified in this paragraph or according to the Universal Treatment Standards specified in Section 012.
013.04 Constituents subject to treatment. When applying the soil treatment standards in paragraph 013.03 of this section, constituents subject to treatment are any constituents listed in Section 012, Table 12, Universal Treatment Standards that are reasonably expected to be present in any given volume of contaminated soil, except fluoride, selenium, sulfides, vanadium, zinc, and are present at concentrations greater than ten times the universal treatment standard. PCBs are not a constituent subject to treatment in any given volume of soil which exhibits the toxicity characteristic solely because of the presence of metals.

013.05A Soil residuals are subject to treatment standards of this section;

013.05B Non-soil residuals are subject to:

013.05B1 For soils contaminated by a listed hazardous waste, the RCRA Subtitle C standards applicable to the listed hazardous waste; and

013.05B2 For soils that exhibit a characteristic of hazardous waste, if the non-soil residual also exhibits a characteristic of hazardous waste, the treatment standards applicable to the characteristic hazardous waste.

014 Prohibitions on storage of restricted wastes.

015 The conditions and requirements of 40 CFR Part 268, Appendix III, pertaining to the list of halogenated organic compounds regulated under 40 CFR 268.32 (as incorporated by reference in Section 008 of this Chapter), are hereby adopted and incorporated herein by reference.

016 The conditions and requirements of 40 CFR Part 268, Appendix IV, pertaining to wastes excluded from lab packs under the alternative treatment standards of Chapter 20, Section 010.02, are hereby adopted and incorporated herein by reference.

017 The conditions and requirements of 40 CFR Part 268, Appendix VI, pertaining to recommended technologies to achieve deactivation of characteristics in Chapter 20, Section 010, are hereby adopted and incorporated herein by reference.

018 The conditions and requirements of 40 CFR Part 268, Appendix VII, pertaining to the effective dates of surface disposed wastes regulated in the land disposal restrictions, are hereby adopted and incorporated herein by reference.

019 The conditions and requirements of 40 CFR Part 268, Appendix VIII, pertaining to the national capacity land disposal restrictions for underground injection control wastes comprehensive list, are hereby adopted and incorporated herein by reference.

020 The conditions and requirements of 40 CFR Part 268, Appendix IX pertaining to extraction procedures (EP) toxicity test method and structural integrity test (method 1310), are hereby adopted and incorporated herein by reference.

021 The conditions and requirements of 40 CFR Part 268, Appendix XI pertaining to metal bearing wastes prohibited from dilution in a combustion unit according to 40 CFR 268.3(3), are hereby adopted and incorporated herein by reference.


Enabling Legislation: Neb. Rev. Stat. §81-1505(13)

Legal Citation: Title 128, Chapter 20, Nebraska Department of Environmental Quality




Nebraska Department of Environmental Quality
1200 "N" Street, Suite 400
P.O. Box 98922
Lincoln, Nebraska 68509
(402) 471-2186