6 CRR-NY 376.4NY-CRR
6 CRR-NY 376.4
6 CRR-NY 376.4
376.4 Treatment standards.
(a) Applicability of treatment standards.
(1) A prohibited waste identified in the table “Treatment Standards for Hazardous Wastes” may be land disposed only if it meets the requirements found in the table. For each waste, the table identifies one of three types of treatment standard requirements:
(i) all hazardous constituents in the waste or in the treatment residue must be at or below the values found in the table for that waste (“total waste standards”); or
(ii) the hazardous constituents in the extract of the waste or in the extract of the treatment residue must be at or below the values found in the table (“waste extract standards”); or
(iii) the waste must be treated using the technology specified in the table (“technology standard”), which are described in detail in subdivision (c) of this section, Table 1-Technology Codes and Description of Technology-Based Standards.
(2) For wastewaters, compliance with concentration level standards is based on maximums for any one day, except for D004 through D011 wastes for which the previously promulgated treatment standards based on grab samples remain in effect. For all nonwastewaters, compliance with concentration level standards is based on grab sampling. For wastes covered by the waste extract standards, the test method 1311, the toxicity characteristic leaching procedure found in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” EPA Publication SW-846, as incorporated by reference in section 370.1(e) of this Title, must be used to measure compliance. An exception is made for D004 and D008, for which either of two test methods may be used: method 1311, or method 1310B, the extraction procedure toxicity test. For wastes covered by a technology standard, the wastes may be land disposed after being treated using that specified technology or an equivalent treatment technology approved by the department under the procedures set forth in paragraph (c)(2) of this section.
(3) When wastes with differing treatment standards for a constituent of concern are combined for purposes of treatment, the treatment residue must meet the lowest treatment standard for the constituent of concern.
(4) Notwithstanding the prohibitions specified in paragraph (1) of this subdivision, treatment and disposal facilities may demonstrate (and certify pursuant to section 376.1[g][2][iv] of this Part) compliance with the treatment standards for organic constituents specified by a footnote in the table “Treatment Standards for Hazardous Wastes” in this subdivision, provided the following conditions are satisfied:
(i) the treatment standards for the organic constituents were established based on incineration in units operated in accordance with the technical requirements of section 373-2.15 of this Title, or based on combustion in fuel substitution units operating in accordance with applicable technical requirements;
(ii) the treatment or disposal facility has used the methods referenced in subparagraph (i) of this paragraph to treat the organic constituents; and
(iii) the treatment or disposal facility may demonstrate compliance with organic constituents if good-faith analytical efforts achieve detection limits for the regulated organic constituents that do not exceed the treatment standards specified in this subdivision by an order of magnitude.
(5) For characteristic wastes (D001 through D043) that are subject to treatment standards in the following table “Treatment Standards for Hazardous Wastes,” and are not managed in a wastewater treatment system that is regulated under the Clean Water Act (CWA), that is CWA- equivalent, or that is injected into a Class I nonhazardous deep injection well, all underlying hazardous constituents (as defined in section 376.1[b][1] of this Part) must meet universal treatment standards, found in subdivision (j) of this section, Table Universal Treatment Standards (UTS), prior to land disposal as defined in section 376.1(b)(1) of this Part.
(6) The treatment standards for F001-F005 nonwastewater constituents carbon disulfide, cyclohexanone, and/or methanol apply to wastes which contain only one, two, or three of these constituents. Compliance is measured for these constituents in the waste extract from test method 1311, the toxicity characteristic leaching procedure found in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” EPA Publication SW-846, as incorporated by reference in section 370.1(e) of this Title. If the waste contains any of these three constituents along with any of the other 25 constituents found in F001-F005, then compliance with treatment standards for carbon disulfide, cyclohexanone, and/or methanol are not required.
(7) Between August 26, 1996 and March 4, 1999 the treatment standards for listed carbamate wastes specified in section 371.4(c) of this Title as EPA hazardous waste numbers K156-K161, and section in 371.4(d) of this Title as EPA hazardous waste numbers P127, P128, P185, P188-P192, P194, P196-P199, P201-P205, U271, U277-U280, U364-U367, U372-U373, U375-U379, U381-U387, U389-U396, U400-U404, U407, and U409-U411; and soil contaminated with these wastes; may be satisfied by either meeting the constituent concentrations presented in the table “Treatment Standards for Hazardous Wastes” in this section, or by treating the waste by the following technologies: combustion, as defined by the technology code CMBST in subdivision (c) Table 1 of this section, for nonwastewaters; and, biodegradation as defined by the technology code BIODG, carbon adsorption as defined by the technology code, CARBN, chemical oxidation as defined by the technology code CHOXD, or combustion as defined as technology code CMBST in subdivision (c) Table 1 of this section, for wastewaters.
(8) Prohibited D004-D011 mixed radioactive wastes and mixed radioactive listed wastes containing metal constituents, that were previously treated by stabilization to the treatment standards in effect at that time and then put into storage, do not have to be retreated to meet treatment standards in this section prior to land disposal.
(9) [Reserved]
(10) The treatment standards for the wastes specified in section 371.4(d) of this Title as EPA Hazardous Waste numbers P185, P191, P192, P197, U364, U394 and U395 may be satisfied by either meeting the constituent concentrations presented in the table "Treatment Standards for Hazardous Wastes" in this subdivision, or by treating the waste by the following technologies: combustion, as defined by the technology code CMBST at subdivision (c) Table 1 of this section, for nonwastewaters; and, biodegradation as defined by the technology code BIODG, carbon adsorption as defined by the technology code CARBN, chemical oxidation as defined by the technology code CHOXD, or combustion as defined as technology code CMBST at subdivision (c) Table 1 of this section, for wastewaters.
Treatment Standards for Hazardous Wastes
Note:
The treatment standards that heretofore appeared in tables in subdivisions (b), (c) and (d) of this section have been consolidated into the table “Treatment Standards for Hazardous Wastes” in this subdivision.
(b) Treatment standards expressed as concentrations in waste extract:
(1) For the requirements previously found in this paragraph and for treatment standards in Table CCWE-Constituent Concentrations in Waste extracts, refer to subdivision (a) of this section.
| Waste Code | Waste Description and Treatment/Regulatory Subcategory1 | REGULATED HAZARDOUS CONSTITUENT | WASTE- WATERS | NONWASTE- WATERS | |
|---|---|---|---|---|---|
| Common Name | CAS2 Number | Wastewaters (Concentration3 in mg/l; or Technology Code4) | Nonwastewaters (Concentration5 in mg/kg unless noted as “mg/l TCLP”; or Technology Code4) | ||
| D0019 | Ignitable Characteristic Wastes, except for the 371.3(b)(1)(i) High TOC Subcategory. | NA | NA | DEACT and meet 376.4(j) standards8;or RORGS; or CMBST | DEACT and meet 376.4(j) standards8; or RORGS; or CMBST |
| High TOC Ignitable Characteristic Liquids Subcategory based on subparagraph 371.3(b)(1)(i)-Greater than or equal to 10% total organic carbon. (Note: This subcategory consists of nonwastewaters only.) | NA | NA | NA | RORGS; CMBST; or POLYM | |
| D0029 | Corrosive Characteristic Wastes. | NA | NA | DEACT and meet 376.4(j) standards8 | DEACT and meet 376.4(j) standards8 |
| D002, D004, D005, D006, D007, D008, D009, D010, D011 | Radioactive High level wastes generated during the reprocessing of fuel rods. (Note: This subcategory consists of nonwastewaters only.) | Corrosivity (pH) Arsenic Barium Cadmium Chromium (Total) Lead Mercury Selenium Silver | NA 7440-38-2 7440-39-3 7440-43-9 7440-47-3 7439-92-1 7439-97-6 7782-49-2 7440-22-4 | NA NA NA NA NA NA NA NA NA | HLVIT HLVIT HLVIT HLVIT HLVIT HLVIT HLVIT HLVIT HLVIT |
| D0039 | Reactive Sulfides Subcategory based on subparagraph 371.3(d)(1)(v). | NA | NA | DEACT | DEACT |
| Explosives Subcategory based on subparagraphs 371.3(d)(1)(vi), (vii), (viii) of this Title. | NA | NA | DEACT and meet 376.4(j) standards8 | DEACT and meet 376.4(j) standards8 | |
| Unexploded ordnance and other explosive devices which have been the subject of an emergency response. | NA | NA | DEACT | DEACT | |
| Other Reactives Subcategory based on 371.3(d)(1)(i). | NA | NA | DEACT and meet 376.4(j) standards8 | DEACT and meet 376.4(j) standards8 | |
| Water Reactive Subcategory based on 371.3(b)(1)(ii),(iii),(iv) of this Title. (Note: This subcategory consists of nonwastewaters only.) | NA | NA | NA | DEACT and meet 376.4(j) standards 8 | |
| Reactive Cyanides Subcategory based on 371.3(d)(1)(v) of this Title. | Cyanides (Total)7 Cyanides (Amenable)7 | 57-12-5 57-12-5 | Reserved 0.86 | 590. 30. | |
| D0049 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for arsenic based on the toxicity characteristic leaching procedure (TCLP) in SW846. | Arsenic | 7440-38-2 | 1.4 and meet 376.4(j) standards8 | 5.0 mg/l TCLP and meet 376.4(j) standards8 |
| D0059 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for barium based on the toxicity characteristic leaching procedure (TCLP) in SW846 | Barium | 7440-39-3 | 1.2 and meet 376.4(j) standards8 | 21 mg/l TCLP and meet 376.4(j) standards8 |
| D0069 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for cadmium based on the toxicity characteristic leaching procedure (TCLP) in SW846 (see section 370.1[e] of this Title). | Cadmium | 7440-43-9 | .69 and meet 376.4(j) standards | 0.11 mg/l TCLP and meet 376.4(j) standards8 |
| Cadmium Containing Batteries Subcategory. (Note: This subcategory consists of nonwastewaters only.) | Cadmium | 7440-43-9 | NA | RTHRM | |
| Radioactively contaminated cadmium containing batteries. (Note: This subcategory consists of nonwastewaters only). | Cadmium | 7440-43-9 | NA | Macroencapsulation in accordance with subdivision 376.4(g) of this Part. | |
| D0079 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for chromium based on the toxicity characteristic leaching procedure (TCLP) in SW846. | Chromium (Total) | 7440-47-3 | 2.77 and meet 376.4(j) standards8 | 0.60 mg/l TCLP and meet 376.4(j) standards8 |
| D0089 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for lead based on the toxicity characteristic leaching procedure (TCLP) in SW846. | Lead | 7439-92-1 | 0.69 and meet 376.4(j) standards8 | 0.75 mg/l TCLP and meet 376.4(j) standards8 |
| Lead Acid Batteries Subcategory (Note: This standard only applies to lead acid batteries that are identified as RCRA hazardous wastes and that are not excluded elsewhere from regulation under the land disposal restrictions of 376 of this Title or exempted under other State regulations (see subdivision 374-1.7(a) of this Title). This subcategory consists of nonwastewaters only.) | Lead | 7439-92-1 | NA | RLEAD | |
| Radioactive Lead Solids Subcategory (Note: these lead solids include, but are not limited to, all forms of lead shielding and other elemental forms of lead. These lead solids do not include treatment residuals such as hydroxide sludges, other wastewater treatment residuals, or incinerator ashes that can undergo conventional pozzolanic stabilization, nor do they include organo-lead materials that can be incinerated and stabilized as ash. This subcategory consists of nonwastewaters only.) | Lead | 7439-92-1 | NA | MACRO | |
| D0099 | Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the toxicity characteristic leaching procedure (TCLP) in SW846 (see section 370.1[e] of this Title); 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) | Mercury | 7439-97-6 | NA | IMERC; OR RMERC |
| Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the toxicity characteristic leaching procedure (TCLP) in SW846 (see section 370.1[e] of this Title); and contain greater than or equal to 260 mg/kg total mercury that are inorganic, including incinerator residues and residues from RMERC. (High Mercury-Inorganic Subcategory) | Mercury | 7439-97-6 | NA | RMERC | |
| Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the toxicity characteristic leaching procedure (TCLP) in SW846 (see section 370.1[e] of this Title); and contain less than 260 mg/kg total mercury and that are residues from RMERC only. (Low Mercury Subcategory) | Mercury | 7439-97-6 | NA | 0.20 mg/l TCLP and meet 376.4(j) standards8 | |
| All other nonwastewates that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the toxicity characteristic leaching procedure (TCLP) in SW846 (see section 370.1[e] of this Title); and contain less than 260 mg/kg total mercury and that are not residues from RMERC. (Low Mercury Subcategory) | Mercury | 7439-97-6 | NA | 0.025 mg/l TCLP and meet 376.4(j) standards8 | |
| All D009 wastewaters. | Mercury | 7439-97-6 | 0.15 and meet 376.4(j) standards8 | NA | |
| Elemental mercury contaminated with radioactive materials. (Note: This subcategory consists of nonwastewaters only.) | Mercury | 7439-97-6 | NA | AMLGM | |
| Hydraulic oil contaminated with Mercury Radioactive Materials Subcategory. (Note: This subcategory consists of nonwastewaters only.) | Mercury | 7439-97-6 | NA | IMERC | |
| Radioactively contaminated mercury containing batteries. (Note: This subcategory consists of nonwastewaters only). | Mercury | 7439-97-6 | NA | Macroencapsulation in accordance with section 376.4(g) of this Part. | |
| D0109 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for selenium based on the toxicity characteristic leaching procedure (TCLP) in SW846. | Selenium | 7782-49-2 | 0.82 and meet 376.4(j) standards8 | 5.7 mg/l TCLP and meet 376.4(j) standards8 |
| D0119 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for silver based on the toxicity characteristic leaching procedure (TCLP) in SW846 (see section 370.1[e] of this Title). | Silver | 7440-22-4 | 0.43 and meet 376.4(j) standards8 | 0.14 mg/l TCLP and meet 376.4(j) standards8 |
| Radioactively contaminated silver containing batteries. (Note: This subcategory consists of nonwastewaters only). | Silver | 7440-22-4 | NA | Macroencapsulation in accordance with section 376.4(g) of this Part. | |
| D0129 | Wastes that are TC for Endrin based on the TCLP in SW846 Method 1311. | Endrin | 72-20-8 | BIODG; or CMBST | 0.13 and meet 376.4(j) standards8 |
| Endrin aldehyde | 7421-93-4 | BIODG; or CMBST | 0.13 and meet 376.4(j) standards8 | ||
| D0139 | Wastes that are TC for Lindane based on the TCLP in SW846 Method 1311. | alpha-BHC | 319-84-6 | CARBN; or CMBST | 0.066 and meet 376.4(j) standards8 |
| beta-BHC | 319-85-7 | CARBN; or CMBST | 0.066 and meet 376.4(j) standards8 | ||
| delta-BHC | 319-86-8 | CARBN; or CMBST | 0.066 and meet 376.4(j) standards8 | ||
| gamma-BHC (Lindane) | 58-89-9 | CARBN; or CMBST | 0.066 and meet 376.4(j) standards8 | ||
| D0149 | Wastes that are TC for Methoxychlor based on the TCLP in SW846 Method 1311. | Methoxychlor | 72-43-5 | WETOX or CMBST | 0.18 and meet 376.4(j) standards8 |
| D0159 | Wastes that are TC for Toxaphene based on theTCLP in SW846 Method 1311. | Toxaphene | 8001-35-2 | BIODG or CMBST | 2.6 and meet 376.4(j) standards8 |
| D0169 | Wastes that are TC for 2,4-D (2,4-Dichlorophenoxyacetic acid) based on the TCLP in SW846 Method 1311. | 2,4-D (2,4-Dichlorophen-oxyacetic acid) | 94-75-7 | CHOXD, BIODG, or CMBST | 10 and meet 376.4(j) standards8 |
| D0179 | Wastes that are TC for 2,4,5-TP (Silvex) based on the TCLP in SW846 Method 1311. | 2,4,5-TP (Silvex) | 93-72-1 | CHOXD or CMBST | 7.9 and meet 376.4(j) standards8 |
| D0189 | Wastes that are TC for Benzene based on the TCLP in SW846 Method 1311. | Benzene | 71-43-2 | 0.14 and meet 376.4(j) standards8 | 10 and meet 376.4(j) standards8 |
| D0199 | Wastes that are TC for Carbon tetrachloride based on the TCLP in SW846 Method 1311. | Carbon tetrachloride | 56-23-5 | 0.057 and meet 376.4(j) standards8 | 6.0 and meet 376.4(j) standards8 |
| D0209 | Wastes that are TC for Chlordane based on the TCLP in SW846 Method 1311. | Chlordane (alpha and gamma isomers) | 57-74-9 | 0.0033 and meet 376.4(j) standards8 | 0.26 and meet 376.4(j) standards8 |
| D0219 | Wastes that are TC for Chlorobenzene based on the TCLP in SW846 Method 1311. | Chlorobenzene | 108-90-7 | 0.057 and meet 376.4(j) standards8 | 6.0 and meet 376.4(j) standards8 |
| D0229 | Wastes that are TC for Chloroform based on the TCLP in SW846 Method 1311. | Chloroform | 67-66-3 | 0.046 and meet 376.4(j) standards8 | 6.0 and meet 376.4(j) standards8 |
| D0239 | Wastes that are TC for o-Cresol based on the TCLP in SW846 Method 1311. | o-Cresol | 95-48-7 | 0.11 and meet 376.4(j) standards8 | 5.6 and meet 376.4(j) standards8 |
| D0249 | Wastes that are TC for m-Cresol based on the TCLP in SW846 Method 1311. | m-Cresol (difficult to distinguish from p-cresol) | 108-39-4 | 0.77 and meet 376.4(j) standards8 | 5.6 and meet 376.4(j) standards8 |
| D0259 | Wastes that are TC for p-Cresol based on the TCLP in SW846 Method 1311. | p-Cresol (difficult to distinguish from m-cresol) | 106-44-5 | 0.77 and meet 376.4(j) standards8 | 5.6 and meet 376.4(j) standards8 |
| D0269 | Wastes that are TC for Cresols (Total) based on the TCLP in SW846 Method 1311. | Cresol-mixed isomers (Cresylic acid)(sum of o-, m-, and p-cresol concentrations) | 1319-77-3 | 0.88 and meet 376.4(j) standards8 | 11.2 and meet 376.4(j) standards8 |
| D0279 | Wastes that are TC for p-Dichlorobenzene based on the TCLP in SW846 Method 1311. | p-Dichlorobenzene (1,4-Dichlorobenzene) | 106-46-7 | 0.090 and meet 376.4(j) standards8 | 6.0 and meet 376.4(j) standards8 |
| D0289 | Wastes that are TC for 1,2-Dichloroethane based on the TCLP in SW846 Method 1311. | 1,2-Dichloroethane | 107-06-2 | 0.21 and meet 376.4(j) standards8 | 6.0 and meet 376.4(j) standards8 |
| D0299 | Wastes that are TC for 1,1-Dichloroethylene based on the TCLP in SW846 Method 1311. | 1,1-Dichloroethylene | 75-35-4 | 0.025 and meet 376.4(j) standards8 | 6.0 and meet 376.4(j) standards8 |
| D0309 | Wastes that are TC for 2,4-Dinitrotoluene based on the TCLP in SW846 Method 1311. | 2,4-Dinitrotoluene | 121-14-2 | 0.32 and meet 376.4(j) standards8 | 140 and meet 376.4(j) standards8 |
| D0319 | Wastes that are TC for Heptachlor based on the TCLP in SW846 Method 1311. | Heptachlor | 76-44-8 | 0.0012 and meet 376.4(j) standards8 | 0.066 and meet 376.4(j) standards8 |
| Heptachlor epoxide | 1024-57-3 | 0.016 and meet 376.4(j) standards8 | 0.066 and meet 376.4(j) standards8 | ||
| D0329 | Wastes that are TC for Hexachlorobenzene based on the TCLP in SW846 Method 1311. | Hexachlorobenzene | 118-74-1 | 0.055 and meet 376.4(j) standards8 | 10 and meet 376.4(j) standards8 |
| D0339 | Wastes that are TC for Hexachlorobutadiene based on the TCLP in SW846 Method 1311. | Hexachlorobutadiene | 87-68-3 | 0.055 and meet 376.4(j) standards8 | 5.6 and meet 376.4(j) standards8 |
| D0349 | Wastes that are TC for Hexachloroethane based on the TCLP in SW846 Method 1311. | Hexachloroethane | 67-72-1 | 0.055 and meet 376.4(j) standards8 | 30 and meet 376.4(j) standards8 |
| D0359 | Wastes that are TC for Methyl ethyl ketone based on the TCLP in SW846 Method 1311. | Methyl ethyl ketone | 78-93-3 | 0.28 and meet 376.4(j) standards8 | 36 and meet 376.4(j) standards8 |
| D0369 | Wastes that are TC for Nitrobenzene based on the TCLP in SW846 Method 1311. | Nitrobenzene | 98-95-3 | 0.068 and meet 376.4(j) standards8 | 14 and meet 376.4(j) standards8 |
| D0379 | Wastes that are TC for Pentachlorophenol based on the TCLP in SW846 Method 1311. | Pentachlorophenol | 87-86-5 | 0.089 and meet 376.4(j) standards8 | 7.4 and meet 376.4(j) standards8 |
| D0389 | Wastes that are TC for Pyridine based on the TCLP in SW846 Method 1311. | Pyridine | 110-86-1 | 0.014 and meet 376.4(j) standards8 | 16 and meet 376.4(j) standards8 |
| D0399 | Wastes that are TC for Tetrachloroethylene based on the TCLP in SW846 Method 1311. | Tetrachloroethylene | 127-18-4 | 0.056 and meet 376.4(j) standards8 | 6.0 and meet 376.4(j) standards8 |
| D0409 | Wastes that are TC for Trichloroethylene based on the TCLP in SW846 Method 1311. | Trichloroethylene | 79-01-6 | 0.054 and meet 376.4(j) standards8 | 6.0 and meet 376.4(j) standards8 |
| D0419 | Wastes that are TC for 2,4,5-Trichlorophenol based on the TCLP in SW846 Method 1311. | 2,4,5-Trichlorophenol | 95-95-4 | 0.18 and meet 376.4(j) standards8 | 7.4 and meet 376.4(j) standards8 |
| D0429 | Wastes that are TC for 2,4,6-Trichlorophenol based on the TCLP in SW846 Method 1311. | 2,4,6-Trichlorophenol | 88-06-2 | 0.035 and meet 376.4(j) standards8 | 7.4 and meet 376.4(j) standards8 |
| D0439 | Wastes that are TC for Vinyl chloride based on the TCLP in SW846 Method 1311. | Vinyl chloride | 75-01-4 | 0.27 and meet 376.4(j) standards8 | 6.0 and meet 376.4(j) standards8 |
| 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-trifluoroethane, trichloroethylene, trichloromonofluoromethane, and/or xylenes (except as specifically noted in other subcategories). See further details of these listings in section 371.4(b) of this Title. | Acetone Benzene n-Butyl alcohol Carbon disulfide Carbon tetrachloride Chlorobenzene o-Cresol m-Cresol (difficult to distinguish from p-cresol) p-Cresol (difficult to distinguish from m-cresol) Cresol-mixed isomers (Cresylc acid) (sum of o-, m-, and p- cresol concentrations) Cyclohexanone o-Dichlorobenzene Ethyl acetate Ethyl benzene Ethyl ether Isobutyl alcohol Methanol Methylene chloride Methyl ethyl ketone Methyl isobutyl ketone Nitrobenzene Pyridine Tetrachloroethylene Toluene 1,1,1-Trichloroethane 1,1,2-Trichloroethane 1,1,2-Trichloro-1,2,2-tri- fluoroethane | 67-64-1 71-43-2 71-36-3 75-15-0 56-23-5 108-90-7 95-48-7 108-39-4 106-44-5 1319-77-3 108-94-1 95-50-1 141-78-6 100-41-4 60-29-7 78-83-1 67-56-1 75-9-2 78-93-3 108-10-1 98-95-3 110-86-1 127-18-4 108-88-3 71-55-6 79-00-5 76-13-1 | 0.28 0.14 5.6 3.8 0.057 0.057 0.11 0.77 0.77 0.88 0.36 0.088 0.34 0.057 0.12 5.6 5.6 0.089 0.28 0.14 0.068 0.014 0.056 0.080 0.054 0.054 0.057 | 160 10 2.6 NA 6.0 6.0 5.6 5.6 5.6 11.2 NA 6.0 33 10 160 170 NA 30 36 33 14 16 6.0 10 6.0 6.0 30 |
| Trichloroethylene | 79-01-6 | 0.054 | 6.0 | ||
| Trichloromonofluoro- methane | 75-69-4 | 0.020 | 30 | ||
| Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30 | ||
| F003 and/or F005 solvent wastes that contain any combination of one or more of the following three solvents as the only listed F001-5 solvents: carbon disulfide, cyclohexanone, and/ or methanol. (formerly 376.4(b)(3)) | Carbon disulfide Cyclohexanone Methanol | 75-15-0 108-94-1 67-56-1 | 3.8 0.36 5.6 | 4.8 mg/l TCLP 0.75 mg/l TCLP 0.75 mg/l TCLP | |
| F005 solvent waste containing 2-Nitropropane as the only listed F001-5 solvent. | 2-Nitropropane | 79-46-9 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST | |
| F005 solvent waste containing 2-Ethoxyethanol as the only listed F001-5 solvent | 2-Ethoxyethanol | 110-80-5 | BIODG: or CMBST | CMBST | |
| 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. | Cadmium Chromium (Total) Cyanides (Total)7 Cyanides (Amenable)7 Lead Nickel Silver | 7440-43-9 7440-47-3 57-12-5 57-12-5 7439-92-1 7440-02-0 7440-22-4 | 0.69 2.77 1.2 0.86 0.69 3.98 NA | 0.11 mg/l TCLP 0.60 mg/l TCLP 590 30 0.75 mg/l TCLP 11 mg/l TCLP 0.14 mg/l TCLP |
| F007 | Spent cyanide plating bath solutions from electroplating operations. | Cadmium Chromium (Total) Cyanides (Total)7 Cyanides (Amenable)7 Lead Nickel Silver | 7440-43-9 7440-47-3 57-12-5 57-12-5 7439-92-1 7440-02-0 7440-22-4 | NA 2.77 1.2 0.86 0.69 3.98 NA | 0.11 mg/l TCLP 0.60 mg/l TCLP 590 30 0.75 mg/l TCLP 11 mg/l TCLP 0.14 mg/l TCLP |
| F008 | Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process. | Cadmium Chromium (Total) Cyanides (Total)7 Cyanides (Amenable)7 Lead Nickel Silver | 7440-43-9 7440-47-3 57-12-5 57-12-5 7439-92-1 7440-02-0 7440-22-4 | NA 2.77 1.2 0.86 0.69 3.98 NA | 0.11 mg/l TCLP 0.60 mg/l TCLP 590 30 0.75 mg/l TCLP 11 mg/l TCLP 0.14 mg/l TCLP |
| F009 | Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process. | Cadmium Chromium (Total) Cyanides (Total)7 Cyanides (Amenable)7 Lead Nickel Silver | 7440-43-9 7440-47-3 57-12-5 57-12-5 7439-92-1 7440-02-0 7440-22-4 | NA 2.77 1.2 0.86 0.69 3.98 NA | 0.11 mg/l TCLP 0.60 mg/l TCLP 590 30 0.75 mg/l TCLP 11 mg/l TCLP 0.14 mg/l TCLP |
| F010 | Quenching bath residues from oil baths from metal heat treating operations where cyanides are used in the process. | Cyanides (Total)7 | 57-12-5 | 1.2 | 590 |
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | NA | ||
| F011 | Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations. | Cadmium Chromium (Total) Cyanides (Total)7 Cyanides (Amenable)7 Lead Nickel Silver | 7440-43-9 7440-47-3 57-12-5 57-12-5 7439-92-1 7440-02-0 7440-22-4 | NA 2.77 1.2 0.86 0.69 3.98 NA | 0.11 mg/l TCLP 0.60 mg/l TCLP 590 30 0.75 mg/l TCLP 11 mg/l TCLP 0.14 mg/l TCLP |
| F012 | Quenching wastewater treatment sludges from metal heat treating operations where cyanides are used in the process. | Cadmium Chromium (Total) Cyanides (Total)7 Cyanides (Amenable)7 Lead Nickel Silver | 7440-43-9 7440-47-3 57-12-5 57-12-5 7439-92-1 7440-02-0 7440-22-4 | NA 2.77 1.2 0.86 0.69 3.98 NA | 0.11 mg/l TCLP 0.60 mg/l TCLP 590 30 0.75 mg/l TCLP 11 mg/l TCLP 0.14 mg/l TCLP |
| 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. | Chromium (Total) Cyanides (Total)7 Cyanides (Amenable)7 | 7440-47-3 57-12-5 57-12-5 | 2.77 1.2 0.86 | 0.60 mg/l TCLP 590 30 |
| F020, F021, F022, F023, F026 | 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 (F020); (2) pentachlorophenol, or of intermediates used to produce its derivatives (i.e., F021); (3) tetra-, penta-, or hexachlorobenzenes under alkaline conditions (i.e., F022); and from the production of materials on equipment previously used for the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of: (1) tri- or tetrachlorophenols, excluding wastes from equipment used only for the production of Hexachlorophene from highly purified 2,4,5-trichlorophenol (F023); (2) tetra-, penta-, or hexachlorobenzenes under alkaline conditions (i.e., F026). | HxCDDs (All Hexachlorodibenzo-p-dioxins) HxCDFs (All Hexachlorodibenzofurans) PeCDDs (All Pentachlorodibenzo-p-dioxins) PeCDFs (All Pentachlorodibenzofurans) Pentachlorophenol TCDDs (All Tetrachlorodibenzo-p-dioxins) TCDFs (All Tetrachlorodibenzofurans) 2,4,5-Trichlorophenol 2,4,6-Trichlorophenol 2,3,4,6-Tetrachlorophenol | NA NA NA NA 87-86-5 NA NA 95-95-4 88-06-2 58-90-2 | 0.000063 0.000063 0.000063 0.000035 0.089 0.000063 0.000063 0.18 0.035 0.030 | 0.001 0.001 0.001 0.001 7.4 0.001 0.001 7.4 7.4 7.4 |
| 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 section 371.4[b] or 371.34[c] of this Title.) | All F024 wastes 2-Chloro-1,3-butadiene 3-Chloropropylene 1,1-Dichloroethane 1,2-Dichloroethane 1,2-Dichloropropane cis-1,3-Dichloropropylene trans-1,3-Dichloropropylene bis(2-Ethylhexyl) phthalate Hexachloroethane Chromium (Total) Nickel | NA 126-99-8 107-05-1 75-34-3 107-06-2 78-87-5 10061-01-5 10061-02-6 117-81-7 67-72-1 7440-47-3 7440-02-0 | CMBST11 0.057 0.036 0.059 0.21 0.85 0.036 0.036 0.28 0.055 2.77 3.98 | CMBST11 0.28 30 6.0 6.0 18 18 18 28 30 0.60 mg/l TCLP 11 mg/l TCLP |
| F025 | Condensed light ends 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. F025-Light Ends Subcategory | Carbon tetrachloride Chloroform 1,2-Dichloroethane 1,1-Dichloroethylene Methylene chloride 1,1,2-Trichloroethane Trichloroethylene Vinyl chloride | 56-23-5 67-66-3 107-06-2 75-35-4 75-9-2 79-00-5 79-01-6 75-01-4 | 0.057 0.046 0.21 0.025 0.089 0.054 0.054 0.27 | 6.0 6.0 6.0 6.0 30 6.0 6.0 6.0 |
| 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. F025-Spent Filters/Aids and Desiccants Subcategory | Carbon tetrachloride Chloroform Hexachlorobenzene Hexachlorobutadiene Hexachloroethane Methylene chloride 1,1,2-Trichloroethane Trichloroethylene Vinyl chloride | 56-23-5 67-66-3 118-74-1 87-68-3 67-72-1 75-9-2 79-00-5 79-01-6 75-01-4 | 0.057 0.046 0.055 0.055 0.055 0.089 0.054 0.054 0.27 | 6.0 6.0 10 5.6 30 30 6.0 6.0 6.0 | |
| 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.) | HxCDDs (All Hexachlorodibenzo-p-dioxins) HxCDFs (All Hexachlorodibenzofurans) PeCDDs (All Pentachlorodibenzo-p-dioxins) PeCDFs (All Pentachlorodibenzofurans) Pentachlorophenol TCDDs (All Tetrachlorodibenzo-p-dioxins) TCDFs (All Tetrachlorodibenzofurans) 2,4,5-Trichlorophenol 2,4,6-Trichlorophenol 2,3,4,6-Tetrachlorophenol | NA NA NA NA 87-86-5 NA NA 95-95-4 88-06-2 58-90-2 | 0.000063 0.000063 0.000063 0.000035 0.089 0.000063 0.000063 0.18 0.035 0.030 | 0.001 0.001 0.001 0.001 7.4 0.001 0.001 7.4 7.4 7.4 |
| F028 | Residues resulting from the incineration or thermal treatment of soil contaminated with EPA Hazardous Wastes Nos. F020, F021, F023, F026, and F027. | HxCDDs (All Hexachlorodibenzo-p-dioxins) HxCDFs (All Hexachlorodibenzofurans) PeCDDs (All Pentachlorodibenzo-p-dioxins) PeCDFs (All Pentachlorodibenzofurans) Pentachlorophenol TCDDs (All Tetrachlorodibenzo-p-dioxins) TCDFs (All Tetrachlorodibenzofurans) 2,4,5-Trichlorophenol 2,4,6-Trichlorophenol 2,3,4,6-Tetrachlorophenol | NA NA NA NA 87-86-5 NA NA 95-95-4 88-06-2 58-90-2 | 0.000063 0.000063 0.000063 0.000035 0.089 0.000063 0.000063 0.18 0.035 0.030 | 0.001 0.001 0.001 0.001 7.4 0.001 0.001 7.4 7.4 7.4 |
| 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 chlorophenolic formulations (except potentially cross-contaminated wastes that have had the F032 waste code deleted in accordance with section 371.4(f) of this Title or potentially cross-contaminated wastes that are otherwise currently regulated as hazardous wastes (i.e., F034 or F035), and where the generator does not resume or initiate use of chlorophenolic formulations). This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or penta-chlorophenol. | Acenaphthene Anthracene Benz(a)anthracene Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) Benzo(a)pyrene Chrysene Dibenz(a,h)anthracene 2-4-Dimethylphenol Fluorene Hexachlorodibenzo-p-dioxins Hexachlorodibenzofurans Indeno (1,2,3-c,d) pyrene Naphthalene Pentachlorodibenzo-p-dioxins Pentachlorodibenzofurans Pentachlorophenol Phenanthrene Phenol Pyrene Tetrachlorodibenzo-p-dioxins Tetrachlorodibenzofurans 2,3,4,6-Tetrachlorophenol | 83-32-9 120-12-7 56-55-3 205-99-2 207-08-9 50-32-8 218-01-9 53-70-3 105-67-9 86-73-7 NA NA 193-39-5 91-20-3 NA NA 87-86-5 85-01-8 108-95-2 129-00-0 NA NA 58-90-2 | 0.059 0.059 0.059 0.11 0.11 0.061 0.059 0.055 0.036 0.059 0.000063 or CMBST 11 0.000063 or CMBST 11 0.0055 0.059 0.000063 or CMBST 11 0.000035 or CMBST 11 0.089 0.059 0.039 0.067 0.000063 or CMBST 11 0.000063 or CMBST 11 0.030 | 3.4 3.4 3.4 6.8 6.8 3.4 3.4 8.2 14 3.4 0.001 or CMBST 11 0.001 or CMBST 11 3.4 5.6 0.001 or CMBST 11 0.001 or CMBST 11 7.4 5.6 6.2 8.2 0.001 or CMBST 11 0.001 or CMBST 11 7.4 |
| 2,4,6-Trichlorophenol | 88-06-2 | 0.035 | 7.4 | ||
| Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP | ||
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP | ||
| F034 | 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 use creosote 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. | Acenaphthene Anthracene Benz(a)anthracene Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) Benzo(a)pyrene Chrysene Dibenz(a,h)anthracene Fluorene Indeno (1,2,3-c,d) pyrene Naphthalene Phenanthrene Pyrene Arsenic Chromium (Total) | 83-32-9 120-12-7 56-55-3 205-99-2 207-08-9 50-32-8 218-01-9 53-70-3 86-73-7 193-39-5 91-20-3 85-01-8 129-00-0 7440-38-2 7440-47-3 | 0.059 0.059 0.059 0.11 0.11 0.061 0.059 0.055 0.059 0.0055 0.059 0.059 0.067 1.4 2.77 | 3.4 3.4 3.4 6.8 6.8 3.4 3.4 8.2 3.4 3.4 5.6 5.6 8.2 5.0 mg/l TCLP 0.60 mg/l TCLP |
| F035 | Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes processes generated at plants that use inorganic preservatives containing arsenic or chromium. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol. | Arsenic Chromium (Total) | 7440-38-2 7440-47-3 | 1.4 2.77 | 5.0 mg/l TCLP 0.60 mg/l TCLP |
| F037 | Petroleum refinery primary oil/water/solids separation sludge-Any sludge generated from the gravitational separation of oil/water/solids during the storage or treatment of process wastewaters and oily cooling wastewaters from petroleum refineries. Such sludges include, but are not limited to, those generated in: oil/water/ solids separators; tanks and impoundments; ditches and other conveyances; sumps; and stormwater units receiving dry weather flow. Sludge generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges generated in aggressive biological treatment units as defined in section 371.4(b)(2)(ii) of this Title (including sludges generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and K051 wastes are not included in this listing. | Acenaphthene Anthracene Benzene Benz(a)anthracene Benzo(a)pyrene bis(2-Ethylhexyl) phthalate Chrysene Di-n-butyl phthalate Ethylbenzene Fluorene Naphthalene Phenanthrene Phenol Pyrene Toluene Xylenes-mixed isomers(sum of o-, m-, and p-xylene concentrations) Chromium (Total) Cyanides (Total)7 Lead Nickel | 83-32-9 120-12-7 71-43-2 56-55-3 50-32-8 117-81-7 218-01-9 84-74-2 100-41-4 86-73-7 91-20-3 85-01-8 108-95-2 129-00-0 108-88-3 1330-20-7 7440-47-3 57-12-5 7439-92-1 7440-02-0 | 0.059 0.059 0.14 0.059 0.061 0.28 0.059 0.057 0.057 0.059 0.059 0.059 0.039 0.067 0.080 .32 2.77 1.2 0.69 NA | NA 3.4 10 3.4 3.4 28 3.4 28 10 NA 5.6 5.6 6.2 8.2 10 30 0.60 mg/l TCLP 590 NA 11 mg/l TCLP |
| F038 | Petroleum refinery secondary (emulsified) oil/ water/solids separation sludge and/or float generated from the physical and/or chemical separation of oil/water/solids in process wastewaters and oily cooling wastewaters from petroleum refineries. Such wastes include, but are not limited to, all sludges and floats generated in: induced air flotation (IAF) units, tanks and impoundments, and all sludges generated in DAF units. Sludges generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges and floats generated in aggressive biological treatment units as defined in section 371.4 (b)(2)(ii) (including sludges and floats generated in one or more additional units after wastewaters have been treated in aggressive biological units) and F037, K048, and K051 are not included in this listing. | Benzene Benzo(a)pyrene bis(2-Ethylhexyl) phthalate Chrysene Di-n butyl phthalate Ethylbenzene Fluorene Naphthalene Phenanthrene Phenol | 71-43-2 50-32-8 117-81-7 218-01-9 84-74-2 100-41-4 86-73-7 91-20-3 85-01-8 108-95-2 | 0.14 0.061 0.28 0.059 0.057 0.057 0.059 0.059 0.059 0.039 | 10 3.4 28 3.4 28 10 NA 5.6 5.6 6.2 |
| Pyrene | 129-00-0 | 0.067 | 8.2 | ||
| Toluene | 108-88-3 | 0.080 | 10 | ||
| Xylenes-mixed isomers (sum of o-m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30 | ||
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP | ||
| Cyanides (Total)7 | 57-12-5 | 1.2 | 590 | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Nickel | 7440-02-0 | NA | 11.0 mg/l TCLP | ||
| F039 | Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one restricted waste classified as hazardous under this section. (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.) | Acenaphthylene Acenaphthene Acetone Acetonitrile Acetophenone 2-Acetylaminofluorene Acrolein Acrylonitrile Aldrin 4-Aminobiphenyl Aniline o-Anisidine (2-methoxyaniline) Anthracene Aramite alpha-BHC beta-BHC delta-BHC gamma-BHC Benzene | 208-96-8 83-32-9 67-64-1 75-05-8 96-86-2 53-96-3 107-02-8 107-13-1 309-00-2 92-67-1 62-53-3 90-04-0 120-12-7 140-57-8 319-84-6 319-85-7 319-86-8 58-89-9 71-43-2 | 0.059 0.059 0.28 5.6 0.010 0.059 0.29 0.24 0.021 0.13 0.81 0.010 0.059 0.36 0.00014 0.00014 0.023 0.0017 0.14 | 3.4 3.4 160 NA 9.7 140 NA 84 0.066 NA 14 0.66 3.4 NA 0.066 0.066 0.066 0.066 10 |
| Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 | ||
| 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 | ||
| 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 | ||
| 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 | ||
| Methyl bromide (Bromomethane) | 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 | ||
| Butyl benzyl phthalate | 85-68-7 | 0.017 | 28 | ||
| 2-sec-Butyl-4,6-dinitrophenol (Dinoseb) | 88-85-7 | 0.066 | 2.5 | ||
| Carbon disulfide | 75-15-0 | 3.8 | NA | ||
| Carbon tetrachloride | 56-23-5 | 0.057 | 6.0 | ||
| 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 | NA | ||
| 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 | ||
| 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 | ||
| Cyclohexanone | 108-94-1 | 0.36 | NA | ||
| 1,2-Dibromo-3-Chloro- propane | 96-12-8 | 0.11 | 15 | ||
| Ethylene dibromide (1,2-Dibromoethane) | 106-93-4 | 0.028 | 15 | ||
| Dibromomethane | 74-95-3 | 0.11 | 15 | ||
| 2,4-D (2,4-Dichlorophenoxy- acetic acid) | 94-75-7 | 0.72 | 10 | ||
| 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 | ||
| 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 | ||
| 1,2-Dichloropropane | 78-87-5 | 0.85 | 18 | ||
| cis-1,3-Dichloropropylene | 10061-01-5 | 0.036 | 18 | ||
| trans-1,3-Dichloro- propylene | 10061-02-6 | 0.036 | 18 | ||
| Dieldrin | 60-57-1 | 0.017 | 0.13 | ||
| 2,4-Dimethylaniline (2,4-xylidine) | 95-68-1 | 0.010 | 0.66 | ||
| Diethyl phthalate | 84-66-2 | 0.20 | 28 | ||
| 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 diphenynitrosamine) | 122-39-4 | 0.92 | NA | ||
| Diphenylnitrosamine (difficult to distinguish from diphenylamine) | 86-30-6 | 0.92 | NA | ||
| 1,2-Diphenylhydrazine | 122-66-7 | 0.087 | NA | ||
| Disulfoton | 298-04-4 | 0.017 | 6.2 | ||
| Endosulfan I | 939-98-8 | 0.023 | 0.066 | ||
| Endosulfan II | 33213-6-5 | 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 | ||
| Ethyl acetate | 141-78-6 | 0.34 | 33 | ||
| Ethyl cyanide (Propanenitrile) | 107-12-0 | 0.24 | 360 | ||
| Ethyl benzene | 100-41-4 | 0.057 | 10 | ||
| Ethyl ether | 60-29-7 | 0.12 | 160 | ||
| bis(2-Ethyhexyl) 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 | ||
| Heptachlor | 76-44-8 | 0.0012 | 0.066 | ||
| Heptachlor epoxide | 1024-57-3 | 0.016 | 0.066 | ||
| Hexachlorobenzene | 118-74-1 | 0.055 | 10 | ||
| Hexachlorobutadiene | 87-68-3 | 0.055 | 5.6 | ||
| Hexachlorocyclo- pentadiene | 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 | 143-50-8 | 0.0011 | 0.13 | ||
| Methacrylonitrile | 126-98-7 | 0.24 | 84 | ||
| Methanol | 67-56-1 | 5.6 | NA | ||
| Methapyrilene | 91-80-5 | 0.081 | 1.5 | ||
| 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 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| 2-Naphthylamine | 91-59-8 | 0.52 | NA | ||
| 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 | ||
| p-Nitrophenol | 100-02-7 | 0.12 | 29 | ||
| N-Nitrosodiethylamine | 55-18-5 | 0.40 | 28 | ||
| N-Nitrosodimethylamine | 62-75-9 | 0.40 | NA | ||
| 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 | ||
| Parathion | 56-38-2 | 0.014 | 4.6 | ||
| Total PCBs (sum of all PCB isomers, or all Aroclors) | 1336-36-3 | 0.10 | 10 | ||
| 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 | ||
| 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 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| 2,4-Dimehtylaniline (2,4-xylidine) | 108-45-2 | 0.010 | 0.66 | ||
| Phorate | 298-02-2 | 0.021 | 4.6 | ||
| Phthalic anhydride | 85-44-9 | 0.055 | NA | ||
| Pronamide | 23950-58-5 | 0.093 | 1.5 | ||
| 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 | ||
| 2,4,5-T | 93-76-5 | 0.72 | 7.9 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14 | ||
| TCDDs (All Tetrachlorodibezeno-p-dioxins) | NA | 0.000063 | 0.001 | ||
| TCDFs (All Tetrachloro- dibenzofurans) | NA | 0.000063 | 0.001 | ||
| 1,1,1,2-Tetrachloroethane | 630-20-6 | 0.057 | 6.0 | ||
| 1,1,2,2-Tetrachloroethane | 79-34-6 | 0.057 | 6.0 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| 2,3,4,6-Tetrachlorophenol | 58-90-2 | 0.030 | 7.4 | ||
| Toluene | 108-88-3 | 0.080 | 10 | ||
| Toxaphene | 8001-35-2 | 0.0095 | 2.6 | ||
| Bromoform (Tribromomethane) | 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 | ||
| Trichloromonofluoro- methane | 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 | ||
| 1,2,3-Trichloropropane | 96-18-4 | 0.85 | 30 | ||
| 1,1,2-Trichloro-1,2,2- trifluoroethane | 76-13-1 | 0.057 | 30 | ||
| tris(2,3-Dibromopropyl) phosphate | 126-72-7 | 0.11 | NA | ||
| 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 | ||
| 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 | NA | ||
| 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)7 | 57-12-5 | 1.2 | 590 | ||
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | NA | ||
| Fluoride | 16964-48-8 | 35 | NA | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Mercury | 7439-97-6 | 0.15 | 0.025 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11 mg/l TCLP | ||
| Selenium | 7782-49-2 | 0.82 | 5.7 mg/l TCLP | ||
| Silver | 7440-22-4 | 0.43 | 0.14 mg/l TCLP | ||
| Sulfide | 8496-25-8 | 14 | NA | ||
| Thallium | 7440-28-0 | 1.4 | NA | ||
| Vanadium | 7440-62-2 | 4.3 | NA | ||
| K001 | Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote and/or pentachlorophenol. | Naphthalene Pentachlorophenol Phenanthrene Pyrene Toluene Xylenes-mixed isomers(sum of o-, m-, and p-xylene concentrations) Lead | 91-20-3 87-86-5 85-01-8 129-00-0 108-88-3 1330-20-7 7439-92-1 | 0.059 0.089 0.059 0.067 0.080 0.32 0.69 | 5.6 7.4 5.6 8.2 10 30 0.75 mg/l TCLP |
| K002 | Wastewater treatment sludge from the production of chrome yellow and orange pigments. | Chromium (Total) Lead | 7440-47-3 7439-92-1 | 2.77 0.69 | 0.60 mg/l TCLP 0.75 mg/l TCLP |
| K003 | Wastewater treatment sludge from the production of molybdate orange pigments. | Chromium (Total) Lead | 7440-47-3 7439-92-1 | 2.77 0.69 | 0.60 mg/l TCLP 0.75 mg/l TCLP |
| K004 | Wastewater treatment sludge from the production of zinc yellow pigments. | Chromium (Total) Lead | 7440-47-3 7439-92-1 | 2.77 0.69 | 0.60 mg/l TCLP 0.75 mg/l TCLP |
| K005 | Wastewater treatment sludge from the production of chrome green pigments. | Chromium (Total) Lead Cyanides (Total)7 | 7440-47-3 7439-92-1 57-12-5 | 2.77 0.69 1.2 | 0.60 mg/l TCLP 0.75 mg/l TCLP 590 |
| K006 | Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous). | Chromium (Total) Lead | 7440-47-3 7439-92-1 | 2.77 0.69 | 0.60 mg/l TCLP 0.75 mg/l TCLP |
| Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated). | Chromium (Total) Lead | 7440-47-3 7439-92-1 | 2.77 0.69 | 0.60 mg/l TCLP NA | |
| K007 | Wastewater treatment sludge from the production of iron blue pigments. | Chromium (Total) Lead Cyanides (Total)7 | 7440-47-3 7439-92-1 57-12-5 | 2.77 0.69 1.2 | 0.60 mg/l TCLP 0.75 mg/l TCLP 590 |
| K008 | Oven residue from the production of chrome oxide green pigments. | Chromium (Total) Lead | 7440-47-3 7439-92-1 | 2.77 0.69 | 0.60 mg/l TCLP 0.75 mg/l TCLP |
| K009 | Distillation bottoms from the production of acetaldehyde from ethylene. | Chloroform | 67-66-3 | 0.046 | 6.0 |
| K010 | Distillation side cuts from the production of acetaldehyde from ethylene. | Chloroform | 67-66-3 | 0.046 | 6.0 |
| K011 | Bottom stream from the wastewater stripper in the production of acrylonitrile. | Acetonitrile Acrylonitrile Acrylamide Benzene Cyanide (Total) | 75-05-8 107-13-1 79-06-1 71-43-2 57-12-5 | 5.6 0.24 19 0.14 1.2 | 38 84 23 10 590 |
| K013 | Bottom stream from the acetonitrile column in the production of acrylonitrile. | Acetonitrile Acrylonitrile Acrylamide Benzene Cyanide (Total) | 75-05-8 107-13-1 79-06-1 71-43-2 57-12-5 | 5.6 0.24 19 0.14 1.2 | 38 84 23 10 590 |
| K014 | Bottoms from the acetonitrile purification column in the production of acrylonitrile. | Acetonitrile Acrylonitrile Acrylamide Benzene Cyanide (Total) | 75-05-8 107-13-1 79-06-1 71-43-2 57-12-5 | 5.6 0.24 19 0.14 1.2 | 38 84 23 10 590 |
| K015 | Still bottoms from the distillation of benzyl chloride. | Anthracene | 120-12-7 | 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 | ||
| Phenanthrene | 85-01-8 | 0.059 | 5.6 | ||
| Toluene | 108-88-3 | 0.080 | 10 | ||
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11 mg/l TCLP | ||
| K016 | Heavy ends or distillation residues from the production of carbon tetrachloride. | Hexachlorobenzene Hexachlorobutadiene Hexachlorocyclopentadiene Hexachloroethane Tetrachloroethylene | 118-74-1 87-68-3 77-47-4 67-72-1 127-18-4 | 0.055 0.055 0.057 0.055 0.056 | 10 5.6 2.4 30 6.0 |
| K017 | Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin. | bis(2-Chloroethyl)ether 1,2-Dichloropropane 1,2,3-Trichloropropane | 111-44-4 78-87-5 96-18-4 | 0.033 0.85 0.85 | 6.0 18 30 |
| K018 | Heavy ends from the fractionation column in ethyl chloride production. | Chloroethane Chloromethane | 75-00-3 74-87-3 | 0.27 0.19 | 6.0 NA |
| 1,1-Dichloroethane | 75-34-3 | 0.059 | 6.0 | ||
| 1,2-Dichloroethane | 107-06-2 | 0.21 | 6.0 | ||
| Hexachlorobenzene | 118-74-1 | 0.055 | 10 | ||
| Hexachlorobutadiene | 87-68-3 | 0.055 | 5.6 | ||
| Hexachloroethane | 67-72-1 | 0.055 | 30 | ||
| Pentachloroethane | 76-01-7 | NA | 6.0 | ||
| 1,1,1-Trichloroethane | 71-55-6 | 0.054 | 6.0 | ||
| K019 | Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production. | bis(2-Chloroethyl)ether Chlorobenzene | 111-44-4 108-90-7 | 0.033 0.057 | 6.0 6.0 |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| p-Dichlorobenzene | 106-46-7 | 0.090 | NA | ||
| 1,2-Dichloroethane | 107-06-2 | 0.21 | 6.0 | ||
| Fluorene | 86-73-7 | 0.059 | NA | ||
| Hexachloroethane | 67-72-1 | 0.055 | 30 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenanthrene | 85-01-8 | 0.059 | 5.6 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | NA | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| 1,2,4-Trichlorobenzene | 120-82-1 | 0.055 | 19 | ||
| 1,1,1-Trichloroethane | 71-55-6 | 0.054 | 6.0 | ||
| K020 | Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production. | 1,2-Dichloroethane | 107-06-2 | 0.21 | 6.0 |
| 1,1,2,2-Tetrachloroethane | 79-34-6 | 0.057 | 6.0 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| K021 | Aqueous spent antimony catalyst waste from fluoromethanes production. | Carbon tetrachloride Chloroform Antimony | 56-23-5 67-66-3 7440-36-0 | 0.057 0.046 1.9 | 6.0 6.0 1.15 mg/l TCLP |
| K022 | Distillation bottom tars from the production of phenol/acetone from cumene. | Toluene Acetophenone | 108-88-3 96-86-2 | 0.080 0.010 | 10 9.7 |
| Diphenylamine (difficult to distinguish from diphenylnitrosamine) | 122-39-4 | 0.92 | 13 | ||
| Diphenylnitrosamine (difficult to distinguish from diphenylamine) | 86-30-6 | 0.92 | 13 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11 mg/l TCLP | ||
| K023 | Distillation light ends from the production of phthalic anhydride from naphthalene. | Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) | 100-21-0 | 0.055 | 28 |
| Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) | 85-44-9 | 0.055 | 28 | ||
| K024 | Distillation bottoms from the production of phthalic anhydride from naphthalene. | Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) | 100-21-0 | 0.055 | 28 |
| Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) | 85-44-9 | 0.055 | 28 | ||
| K025 | Distillation bottoms from the production of nitrobenzene by the nitration of benzene. | NA | NA | LLEXT fb SSTRP fb CARBN; or CMBST | CMBST |
| K026 | Stripping still tails from the production of methyl ethyl pyridines. | NA | NA | CMBST | CMBST |
| K027 | Centrifuge and distillation residues from toluene diisocyanate production. | NA | NA | CARBN; or CMBST | CMBST |
| K028 | Spent catalyst from the hydrochlorinator reactor in the production of 1,1,1-trichloroethane. | 1,1-Dichloroethane trans-1,2-Dichloroethylene | 75-34-3 156-60-5 | 0.059 0.054 | 6.0 30 |
| Hexachlorobutadiene | 87-68-3 | 0.055 | 5.6 | ||
| Hexachloroethane | 67-72-1 | 0.055 | 30 | ||
| Pentachloroethane | 76-01-7 | NA | 6.0 | ||
| 1,1,1,2-Tetrachloroethane | 630-20-6 | 0.057 | 6.0 | ||
| 1,1,2,2-Tetrachloroethane | 79-34-6 | 0.057 | 6.0 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| 1,1,1-Trichloroethane | 71-55-6 | 0.054 | 6.0 | ||
| 1,1,2-Trichloroethane | 79-00-5 | 0.054 | 6.0 | ||
| Cadmium | 7440-43-9 | 0.69 | NA | ||
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11 mg/l TCLP | ||
| K029 | Waste from the product steam stripper in the production of 1,1,1-trichloroethane. | Chloroform | 67-66-3 | 0.046 | 6.0 |
| 1,2-Dichloroethane | 107-06-2 | 0.21 | 6.0 | ||
| 1,1-Dichloroethylene | 75-35-4 | 0.025 | 6.0 | ||
| 1,1,1-Trichloroethane | 71-55-6 | 0.054 | 6.0 | ||
| Vinyl chloride | 75-01-4 | 0.27 | 6.0 | ||
| K030 | Column bodies or heavy ends from the combined production of trichloroethylene and perchloroethylene. | o-Dichlorobenzene | 95-50-1 | 0.088 | NA |
| p-Dichlorobenzene | 106-46-7 | 0.090 | NA | ||
| Hexachlorobutadiene | 87-68-3 | 0.055 | 5.6 | ||
| Hexachloroethane | 67-72-1 | 0.055 | 30 | ||
| Hexachloropropylene | 1888-71-7 | NA | 30 | ||
| Pentachlorobenzene | 608-93-5 | NA | 10 | ||
| Pentachloroethane | 76-01-7 | NA | 6.0 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| 1,2,4-Trichlorobenzene | 120-82-1 | 0.055 | 19 | ||
| K031 | By-product salts generated in the production of MSMA and cacodylic acid. | Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP |
| K032 | Wastewater treatment sludge from the production of chlordane. | Hexachlorocyclopentadiene | 77-47-4 | 0.057 | 2.4 |
| Chlordane (alpha and gamma isomers) | 57-74-9 | 0.0033 | 0.26 | ||
| Heptachlor | 76-44-8 | 0.0012 | 0.066 | ||
| Heptachlor epoxide | 1024-57-3 | 0.016 | 0.066 | ||
| K033 | Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane. | Hexachlorocyclopentadiene | 77-47-4 | 0.057 | 2.4 |
| K034 | Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane. | Hexachlorocyclopentadiene | 77-47-4 | 0.057 | 2.4 |
| K035 | Wastewater treatment sludges generated in the production of creosote. | Acenaphthene | 83-32-9 | NA | 3.4 |
| Anthracene | 120-12-7 | NA | 3.4 | ||
| Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 | ||
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| 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 | ||
| Dibenz(a,h)anthracene | 53-70-3 | NA | 8.2 | ||
| Fluoranthene | 206-44-0 | 0.068 | 3.4 | ||
| Fluorene | 86-73-7 | NA | 3.4 | ||
| Indeno(1,2,3-cd)pyrene | 193-39-5 | NA | 3.4 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenanthrene | 85-01-8 | 0.059 | 5.6 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Pyrene | 129-00-0 | 0.067 | 8.2 | ||
| K036 | Still bottoms from toluene reclamation distillation in the production of disulfoton. | Disulfoton | 298-04-4 | 0.017 | 6.2 |
| K037 | Wastewater treatment sludges from the production of disulfoton. | Disulfoton | 298-04-4 | 0.017 | 6.2 |
| Toluene | 108-88-3 | 0.080 | 10 | ||
| K038 | Wastewater from the washing and stripping of phorate production. | Phorate | 298-02-2 | 0.021 | 4.6 |
| K039 | Filter cake from the filtration of diethylphosphorodithioc acid in the production of phorate. | NA | NA | CARBN; or CMBST | CMBST |
| K040 | Wastewater treatment sludge from the production of phorate. | Phorate | 298-02-2 | 0.021 | 4.6 |
| K041 | Wastewater treatment sludge from the production of toxaphene. | Toxaphene | 8001-35-2 | 0.0095 | 2.6 |
| K042 | Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5-T. | o-Dichlorobenzene | 95-50-1 | 0.088 | 6.0 |
| p-Dichlorobenzene | 106-46-7 | 0.090 | 6.0 | ||
| Pentachlorobenzene | 608-93-5 | 0.055 | 10 | ||
| 1,2,4,5-Tetrachlor- obenzene | 95-94-3 | 0.055 | 14 | ||
| 1,2,4-Trichlorobenzene | 120-82-1 | 0.055 | 19 | ||
| K043 | 2,6-Dichlorophenol waste from the production of 2,4-D. | 2,4-Dichlorophenol | 120-83-2 | 0.044 | 14 |
| 2,6-Dichlorophenol | 187-65-0 | 0.044 | 14 | ||
| 2,4,5-Trichlorophenol | 95-95-4 | 0.18 | 7.4 | ||
| 2,4,6-Trichlorophenol | 88-06-2 | 0.035 | 7.4 | ||
| 2,3,4,6-Tetrachlorophenol | 58-90-2 | 0.030 | 7.4 | ||
| Pentachlorophenol | 87-86-5 | 0.089 | 7.4 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| HxCDDs (All Hexachlorodibenzo-p-dioxins) | NA | 0.000063 | 0.001 | ||
| HxCDFs (All Hexachlorodibenzofurans) | NA | 0.000063 | 0.001 | ||
| PeCDDs (All Penta- chlorodibenzo-p-dioxins) | NA | 0.000063 | 0.001 | ||
| PeCDFs (All Pentachlorodibenzofurans) | NA | 0.000035 | 0.001 | ||
| TCDDs (All Tetrachlorodibenzo-p-dioxins) | NA | 0.000063 | 0.001 | ||
| TCDFs (All Tetrachlorodibenzofurans) | NA | 0.000063 | 0.001 | ||
| K044 | Wastewater treatment sludges from the manufacturing and processing of explosives. | NA | NA | DEACT | DEACT |
| K045 | Spent carbon from the treatment of wastewater containing explosives. | NA | NA | DEACT | DEACT |
| K046 | Wastewater treatment sludges from the manufacturing, formulation and loading of lead- based initiating compounds. | Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP |
| K047 | Pink/red water from TNT operations | NA | NA | DEACT | DEACT |
| K048 | Dissolved air flotation (DAF) float from the petroleum refining industry. | Benzene | 71-43-2 | 0.14 | 10 |
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Di-n-butyl phthalate | 84-74-2 | 0.057 | 28 | ||
| Ethylbenzene | 100-41-4 | 0.057 | 10 | ||
| Fluorene | 86-73-7 | 0.059 | NA | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenanthrene | 85-01-8 | 0.059 | 5.6 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Pyrene | 129-00-0 | 0.067 | 8.2 | ||
| Toluene | 108-88-33 | 0.080 | 10 | ||
| Xylenes-mixed isomers(sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30 | ||
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP | ||
| Cyanides (Total)7 | 57-12-5 | 1.2 | 590 | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Nickel | 7440-02-0 | NA | 11 mg/l TCLP | ||
| K049 | Slop oil emulsion solids from the petroleum refining industry. | Anthracene | 120-12-7 | 0.059 | 3.4 |
| Benzene | 71-43-2 | 0.14 | 10 | ||
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28 | ||
| Carbon disulfide | 75-15-0 | 3.8 | NA | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| 2,4-Dimethylphenol | 105-67-9 | 0.036 | NA | ||
| Ethylbenzene | 100-41-4 | 0.057 | 10 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenanthrene | 85-01-8 | 0.059 | 5.6 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Pyrene | 129-00-0 | 0.067 | 8.2 | ||
| Toluene | 108-88-3 | 0.080 | 10 | ||
| Xylenes-mixed isomers(sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30 | ||
| Cyanides (Total)7 | 57-12-5 | 1.2 | 590 | ||
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Nickel | 7440-02-0 | NA | 11 mg/l TCLP | ||
| K050 | Heat exchanger bundle cleaning sludge from the petroleum refining industry. | Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 |
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Cyanides (Total)7 | 57-12-5 | 1.2 | 590 | ||
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Nickel | 7440-02-0 | NA | 11 mg/l TCLP | ||
| K051 | API separator sludge from the petroleum refining industry. | Acenaphthene | 83-32-9 | 0.059 | NA |
| Anthracene | 120-12-7 | 0.059 | 3.4 | ||
| Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 | ||
| Benzene | 71-43-2 | 0.14 | 10 | ||
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Di-n-butyl phthalate | 105-67-9 | 0.057 | 28 | ||
| Ethylbenzene | 100-41-4 | 0.057 | 10 | ||
| Fluorene | 86-73-7 | 0.059 | NA | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenanthrene | 85-01-8 | 0.059 | 5.6 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Pyrene | 129-00-0 | 0.067 | 8.2 | ||
| Toluene | 108-88-3 | 0.08 | 10 | ||
| Xylenes-mixed isomers(sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30 | ||
| Cyanides (Total)7 | 57-12-5 | 1.2 | 590 | ||
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Nickel | 7440-02-0 | NA | 11 mg/l TCLP | ||
| K052 | Tank bottoms (leaded) from the petroleum refining industry. | Benzene | 71-43-2 | 0.14 | 10 |
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| 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 | ||
| 2,4-Dimethylphenol | 105-67-9 | 0.036 | NA | ||
| Ethylbenzene | 100-41-4 | 0.057 | 10 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenanthrene | 85-01-8 | 0.059 | 5.6 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Toluene | 108-88-3 | 0.08 | 10 | ||
| Xylenes-mixed isomers(sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30 | ||
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP | ||
| Cyanides (Total)7 | 57-12-5 | 1.2 | 590 | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Nickel | 7440-02-0 | NA | 11 mg/l TCLP | ||
| K060 | Ammonia still lime sludge from coking operations. | Benzene | 71-43-2 | 0.14 | 10 |
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Cyanides (Total)7 | 57-12-5 | 1.2 | 590 | ||
| K061 | Emission control dust/sludge from the primary production of steel in electric furnaces. | Antimony | 7440-36-0 | NA | 1.15 mg/l TCLP |
| Arsenic | 7440-38-2 | NA | 5.0 mg/l TCLP | ||
| Barium | 7440-39-3 | NA | 21 mg/l TCLP | ||
| Beryllium | 7440-41-7 | NA | 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 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Mercury | 7439-97-6 | NA | 0.025 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11 mg/l TCLP | ||
| Selenium | 7782-49-2 | NA | 5.7 mg/l TCLP | ||
| Silver | 7440-22-4 | NA | 0.14 mg/l TCLP | ||
| Thallium | 7440-28-0 | NA | 0.20 mg/l TCLP | ||
| Zinc | 7440-66-6 | NA | 4.3 mg/l TCLP | ||
| K062 | Spent pickle liquor generated by steel finishing operations of facilities within the iron and steel industry (SIC Codes 331 and 332). | Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP |
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | NA | ||
| K069 | Emission control dust/sludge from secondary lead smelting. - Calcium Sulfate (Low Lead) Subcategory | Cadmium | 7440-43-9 | 0.69 | 0.11 mg/l TCLP |
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Emission control dust/sludge from secondary lead smelting. - Non-Calcium Sulfate (High Lead) Subcategory | NA | NA | NA | RLEAD | |
| K071 | K071 (Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used) nonwastewaters that are residues from RMERC. | Mercury | 7439-97-6 | NA | 0.20 mg/l TCLP |
| K071 (Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used.) nonwastewaters that are not residues from RMERC. | Mercury | 7439-97-6 | NA | 0.025 mg/l TCLP | |
| All K071 wastewaters. | Mercury | 7439-97-6 | 0.15 | NA | |
| K073 | Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production. | Carbon tetrachloride | 56-23-5 | 0.057 | 6.0 |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Hexachloroethane | 67-72-1 | 0.055 | 30 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| 1,1,1-Trichloroethane | 71-55-6 | 0.054 | 6.0 | ||
| K083 | Distillation bottoms from aniline production. | Aniline | 62-53-3 | 0.81 | 14 |
| Benzene | 71-43-2 | 0.14 | 10 | ||
| Cyclohexanone | 108-94-1 | 0.36 | NA | ||
| Diphenylamine (difficult to distinguish from diphenylnitrosamine) | 122-39-4 | 0.92 | 13 | ||
| Diphenylnitrosamine (difficult to distinguish from diphenylamine) | 86-30-6 | 0.92 | 13 | ||
| Nitrobenzene | 98-95-3 | 0.068 | 14 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Nickel | 7440-02-0 | 3.98 | 11 mg/l TCLP | ||
| K084 | Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds. | Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP |
| K085 | Distillation or fractionation column bottoms from the production of chlorobenzenes. | Benzene | 71-43-2 | 0.14 | 10 |
| Chlorobenzene | 108-90-7 | 0.057 | 6.0 | ||
| 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 | ||
| Hexachlorobenzene | 118-74-1 | 0.055 | 10 | ||
| Total PCBs(sum of all PCB isomers, or all Aroclors) | 1336-36-3 | 0.10 | 10 | ||
| Pentachlorobenzene | 608-93-5 | 0.055 | 10 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14 | ||
| 1,2,4-Trichlorobenzene | 120-82-1 | 0.055 | 19 | ||
| K086 | Solvent wastes and sludges, caustic washes and sludges, or water washes and sludges from cleaning tubs and equipment used in the formulation of ink from pigments, driers, soaps, and stabilizers containing chromium and lead. | Acetone | 67-64-1 | 0.28 | 160 |
| Acetophenone | 96-86-2 | 0.010 | 9.7 | ||
| bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28 | ||
| n-Butyl alcohol | 71-36-3 | 5.6 | 2.6 | ||
| Butylbenzyl phthalate | 85-68-7 | 0.017 | 28 | ||
| Cyclohexanone | 108-94-1 | 0.36 | NA | ||
| o-Dichlorobenzene | 95-50-1 | 0.088 | 6.0 | ||
| Diethyl phthalate | 84-66-2 | 0.20 | 28 | ||
| Dimethyl phthalate | 131-11-3 | 0.047 | 28 | ||
| Di-n-butyl phthalate | 84-74-2 | 0.057 | 28 | ||
| Di-n-octyl phthalate | 117-84-0 | 0.017 | 28 | ||
| Ethyl acetate | 141-78-6 | 0.34 | 33 | ||
| Ethylbenzene | 100-41-4 | 0.057 | 10 | ||
| Methanol | 67-56-1 | 5.6 | NA | ||
| Methyl ethyl ketone | 78-93-3 | 0.28 | 36 | ||
| Methyl isobutyl ketone | 108-10-1 | 0.14 | 33 | ||
| Methylene chloride | 75-09-2 | 0.089 | 30 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Nitrobenzene | 98-95-3 | 0.068 | 14 | ||
| Toluene | 108-88-3 | 0.080 | 10 | ||
| 1,1,1-Trichloroethane | 71-55-6 | 0.054 | 6.0 | ||
| Trichloroethylene | 79-01-6 | 0.054 | 6.0 | ||
| Xylenes-mixed isomers(sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30 | ||
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP | ||
| Cyanides (Total)7 | 57-12-5 | 1.2 | 590 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| K087 | Decanter tank tar sludge from coking operations. | Acenaphthylene | 208-96-8 | 0.059 | 3.4 |
| Benzene | 71-43-2 | 0.14 | 10 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Fluoranthene | 206-44-0 | 0.068 | 3.4 | ||
| Indeno(1,2,3-cd)pyrene | 193-39-5 | 0.0055 | 3.4 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenanthrene | 85-01-8 | 0.059 | 5.6 | ||
| Toluene | 108-88-3 | 0.080 | 10 | ||
| Xylenes-mixed isomers(sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| K088 | Spent potliners from primary aluminum reduction. | Acenaphthalene | 83-32-9 | 0.059 | 3.4 |
| Anthracene | 120-12-7 | 0.059 | 3.4 | ||
| Benzo(a)anthracene | 56-55-3 | 0.059 | 3.4 | ||
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| Benzo(b)fluoranthene | 205-99-2 | 0.11 | 6.8 | ||
| Benzo(k)fluoranthene | 207-08-9 | 0.11 | 6.8 | ||
| Benzo(g,h,i)perylene | 191-24-2 | 0.0055 | 1.8 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Dibenz(a,h)anthracene | 53-70-3 | 0.055 | 8.2 | ||
| Fluoranthene | 206-44-0 | 0.068 | 3.4 | ||
| Indeno(1,2,3,-cd)pyrene | 193-39-5 | 0.0055 | 3.4 | ||
| Phenanthrene | 85-01-8 | 0.059 | 5.6 | ||
| Pyrene | 129-00-0 | 0.067 | 8.2 | ||
| Antimony | 7440-36-0 | 1.9 | 1.15 mg/l TCLP | ||
| Arsenic | 7440-38-2 | 1.4 | 26.1mg/kg | ||
| 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 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Mercury | 7439-97-6 | 0.15 | 0.025 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11 mg/l TCLP | ||
| Selenium | 7782-49-2 | 0.82 | 5.7 mg/l TCLP | ||
| Silver | 7440-22-4 | 0.43 | 0.14 mg/l TCLP | ||
| Cyanide (Total)7 | 57-12-5 | 1.2 | 590 | ||
| Cyanide (Amenable)7 | 57-12-5 | 0.86 | 30 | ||
| Fluoride | 16984-48-8 | 35 | NA | ||
| K093 | Distillation light ends from the production of phthalic anhydride from ortho-xylene. | Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) | 100-21-0 | 0.055 | 28 |
| Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) | 85-44-9 | 0.055 | 28 | ||
| K094 | Distillation bottoms from the production of phthalic anhydride from ortho-xylene. | Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) | 100-21-0 | 0.055 | 28 |
| Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) | 85-44-9 | 0.055 | 28 | ||
| K095 | Distillation bottoms from the production of 1,1,1-trichloroethane. | Hexachloroethane | 67-72-1 | 0.055 | 30 |
| Pentachloroethane | 76-01-7 | 0.055 | 6.0 | ||
| 1,1,1,2-Tetrachloroethane | 630-20-6 | 0.057 | 6.0 | ||
| 1,1,2,2-Tetrachloroethane | 79-34-6 | 0.057 | 6.0 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| 1,1,2-Trichloroethane | 79-00-5 | 0.054 | 6.0 | ||
| Trichloroethylene | 79-01-6 | 0.054 | 6.0 | ||
| K096 | Heavy ends from the heavy ends column from the production of 1,1,1-trichloroethane. | m-Dichlorobenzene | 541-73-1 | 0.036 | 6.0 |
| Pentachloroethane | 76-01-7 | 0.055 | 6.0 | ||
| 1,1,1,2-Tetrachloroethane | 630-20-6 | 0.057 | 6.0 | ||
| 1,1,2,2-Tetrachloroethane | 79-34-6 | 0.057 | 6.0 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| 1,2,4-Trichlorobenzene | 120-82-1 | 0.055 | 19 | ||
| 1,1,2-Trichloroethane | 79-00-5 | 0.054 | 6.0 | ||
| Trichloroethylene | 79-01-6 | 0.054 | 6.0 | ||
| K097 | Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane. | Chlordane (alpha and gamma isomers) | 57-74-9 | 0.0033 | 0.26 |
| Heptachlor | 76-44-8 | 0.0012 | 0.066 | ||
| Heptachlor epoxide | 1024-57-3 | 0.016 | 0.066 | ||
| Hexachlorocyclopentadiene | 77-47-4 | 0.057 | 2.4 | ||
| K098 | Untreated process wastewater from the production of toxaphene. | Toxaphene | 8001-35-2 | 0.0095 | 2.6 |
| K099 | Untreated wastewater from the production of 2,4-D. | 2,4-Dichlorophenoxyacetic acid | 94-75-7 | 0.72 | 10 |
| HxCDDs (All Hexachlorodibenzo-p-dioxins) | NA | 0.000063 | 0.001 | ||
| HxCDFs (All Hexachlorodibenzofurans) | NA | 0.000063 | 0.001 | ||
| PeCDDs (All Pentachlorodibenzo-p-dioxins) | NA | 0.000063 | 0.001 | ||
| PeCDFs (All Pentachlorodibenzofurans) | NA | 0.000035 | 0.001 | ||
| TCDDs (All Tetrachlorodibenzo-p-dioxins) | NA | 0.000063 | 0.001 | ||
| TCDFs (All Tetrachlorodibenzofurans) | NA | 0.000063 | 0.001 | ||
| K100 | Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting. | Cadmium | 7440-43-9 | 0.69 | 0.11mg/l TCLP |
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60mg/l TCLP | ||
| Lead | 7439-92-1 | 0.69 | 0.75mg/l TCLP | ||
| K101 | Distillation tar residues from the distillation of aniline-based compounds in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds. | o-Nitroaniline | 88-74-4 | 0.27 | 14 |
| Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP | ||
| Cadmium | 7440-43-9 | 0.69 | NA | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Mercury | 7439-97-6 | 0.15 | NA | ||
| K102 | Residue from the use of activated carbon for decolorization in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds. | o-Nitrophenol | 88-75-5 | 0.028 | 13 |
| Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP | ||
| Cadmium | 7440-43-9 | 0.69 | NA | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Mercury | 7439-97-6 | 0.15 | NA | ||
| K103 | Process residues from aniline extraction from the production of aniline. | Aniline | 62-53-3 | 0.81 | 14 |
| Benzene | 71-43-2 | 0.14 | 10 | ||
| 2,4-Dinitrophenol | 51-28-5 | 0.12 | 160 | ||
| Nitrobenzene | 98-95-3 | 0.068 | 14 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| K104 | Combined wastewater streams generated from nitrobenzene/ aniline production. | Aniline | 62-53-3 | 0.81 | 14 |
| Benzene | 71-43-2 | 0.14 | 10 | ||
| 2,4-Dinitrophenol | 51-28-5 | 0.12 | 160 | ||
| Nitrobenzene | 98-95-3 | 0.068 | 14 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Cyanides (Total)7 | 57-12-5 | 1.2 | 590 | ||
| K105 | Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes. | Benzene | 71-43-2 | 0.14 | 10 |
| Chlorobenzene | 108-90-7 | 0.057 | 6.0 | ||
| 2-Chlorophenol | 95-57-8 | 0.044 | 5.7 | ||
| o-Dichlorobenzene | 95-50-1 | 0.088 | 6.0 | ||
| p-Dichlorobenzene | 106-46-7 | 0.090 | 6.0 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| 2,4,5-Trichlorophenol | 95-95-4 | 0.18 | 7.4 | ||
| 2,4,6-Trichlorophenol | 88-06-2 | 0.035 | 7.4 | ||
| K106 | K106 (wastewater treatment sludge from the mercury cell process in chlorine production) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury. | Mercury | 7439-97-6 | NA | RMERC |
| K106 (wastewater treatment sludge from the mercury cell process in chlorine production) nonwastewaters that contain less than 260 mg/kg total mercury that are residues from RMERC. | Mercury | 7439-97-6 | NA | 0.20 mg/l TCLP | |
| Other K106 nonwastewaters that contain less than 260 mg/kg total mercury and are not residues from RMERC. | Mercury | 7439-97-6 | NA | 0.025 mg/l TCLP | |
| All K106 wastewaters. | Mercury | 7439-97-6 | 0.15 | NA | |
| K107 | Column bottoms from product separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. | NA | NA | CMBST; or CHOXD fb CARBN; or BIODG fb CARBN | CMBST |
| K108 | Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. | NA | NA | CMBST; or CHOXD fb CARBN; or BIODG fb CARBN | CMBST |
| K109 | Spent filter cartridges from product purification from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. | NA | NA | CMBST; or CHOXD fb CARBN; or BIODG fb CARBN | CMBST |
| K110 | Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. | NA | NA | CMBST; or CHOXD fb CARBN; or BIODG fb CARBN | CMBST |
| K111 | Product washwaters from the production of dinitrotoluene via nitration of toluene | 2,4-Dinitrotoluene 2,6-Dinitrotoluene | 121-14-2 606-20-2 | 0.32 0.55 | 140 28 |
| K112 | Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene. | NA | NA | CMBST; or CHOXD fb CARBN; or BIODG fb CARBN | CMBST |
| K113 | Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. | NA | NA | CARBN; OR CMBST | CMBST |
| K114 | Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. | NA | NA | CARBN; or CMBST | CMBST |
| K115 | Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. | Nickel | 7440-02-0 | 3.98 | 11 mg/l TCLP |
| NA | NA | CARBN; or CMBST | CMBST | ||
| K116 | Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine. | NA | NA | CARBN; or CMBST | CMBST |
| K117 | Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene. | Methyl bromide (Bromomethane) | 74-83-9 | 0.11 | 15 |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Ethylene dibromide (1,2-Dibromoethane) | 106-93-4 | 0.028 | 15 | ||
| K118 | Spent absorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene. | Methyl bromide (Bromomethane) | 74-83-9 | 0.11 | 15 |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Ethylene dibromide (1,2-Dibromoethane) | 106-93-4 | 0.028 | 15 | ||
| K123 | Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salts. | NA | NA | CMBST; or CHOXD fb (BIODG or CARBN) | CMBST |
| K124 | Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts. | NA | NA | CMBST; or CHOXD fb (BIODG or CARBN) | CMBST |
| K125 | Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts. | NA | NA | CMBST; or CHOXD fb (BIODG or CARBN) | CMBST |
| K126 | Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts. | NA | NA | CMBST; or CHOXD fb (BIODG or CARBN) | CMBST |
| K131 | Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide. | Methyl bromide (Bromomethane) | 74-83-9 | 0.11 | 15 |
| K132 | Spent absorbent and wastewater separator solids from the production of methyl bromide. | Methyl bromide (Bromomethane) | 74-83-9 | 0.11 | 15 |
| K136 | Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene. | Chloroform Ethylene dibromide (1,2-Dibromoethane) | 67-66-3 106-93-4 | 0.046 0.028 | 6.0 15 |
| K141 | Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the production of coke or the recovery of coke by-products produced from coal. This listing does not include K087 (decanter tank tar sludge from coking operations). | Benzene | 71-43-2 | 0.14 | 10 |
| Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 | ||
| Benzo(a)pyrene | 50-2-8 | 0.061 | 3.4 | ||
| 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 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Dibenz(a,h)anthracene | 53-70-3 | 0.055 | 8.2 | ||
| Indeno(1,2,3-cd)pyrene | 193-39-5 | 0.0055 | 3.4 | ||
| K142 | Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal. | Benzene | 71-43-2 | 0.14 | 10 |
| Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 | ||
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| 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 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Dibenz(a,h)anthracene | 53-70-3 | 0.055 | 8.2 | ||
| Indeno(1,2,3-cd)pyrene | 193-39-5 | 0.0055 | 3.4 | ||
| K143 | Process residues from the recovery of light oil, including, but not limited to, those generated in stills, decanters, and wash oil recovery units from the recovery of coke by-products produced from coal. | Benzene | 71-43-2 | 0.14 | 10 |
| Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 | ||
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) | 205-99-2 | 0.11 | 6.8 | ||
| Benzo(k)flouranthene (difficult to distinguish from benzo(b)fluoranthene) | 207-08-9 | 0.11 | 6.8 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| K144 | Wastewater sump residues from light oil refining, including, but not limited to, intercepting or contamination sump sludges from the recovery of coke by-products produced from coal. | Benzene | 71-43-2 | 0.14 | 10 |
| Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 | ||
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| 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 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Dibenz(a,h)anthracene | 53-70-3 | 0.055 | 8.2 | ||
| K145 | Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal. | Benzene | 71-43-2 | 0.14 | 10 |
| Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 | ||
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Dibenz(a,h)anthracene | 53-70-3 | 0.055 | 8.2 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| K147 | Tar storage tank residues from coal tar refining. | Benzene | 71-43-2 | 0.14 | 10 |
| Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 | ||
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| 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 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Dibenz(a,h)anthracene | 53-70-3 | 0.055 | 8.2 | ||
| Indeno(1,2,3-cd)pyrene | 193-39-5 | 0.0055 | 3.4 | ||
| K148 | Residues from coal tar distillation, including, but not limited to, still bottoms. | Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 |
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| 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 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Dibenz(a,h)anthracene | 53-70-3 | 0.055 | 8.2 | ||
| Indeno(1,2,3-cd)pyrene | 193-39-5 | 0.0055 | 3.4 | ||
| K149 | Distillation bottoms from the production of alpha- (or methyl-) chlorinated toluenes, ring- chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. (This waste does not include still bottoms from the distillations of benzyl chloride.) | Chlorobenzene | 108-90-7 | 0.057 | 6.0 |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Chloromethane | 74-87-3 | 0.19 | 30 | ||
| p-Dichlorobenzene | 106-46-7 | 0.090 | 6.0 | ||
| Hexachlorobenzene | 118-74-1 | 0.055 | 10 | ||
| Pentachlorobenzene | 608-93-5 | 0.055 | 10 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14 | ||
| Toluene | 108-88-3 | 0.080 | 10 | ||
| K150 | Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydrochloric acid recovery processes associated with the production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. | Carbon tetrachloride | 56-23-5 | 0.057 | 6.0 |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Chloromethane | 74-87-3 | 0.19 | 30 | ||
| p-Dichlorobenzene | 106-46-7 | 0.090 | 6.0 | ||
| Hexachlorobenzene | 118-74-1 | 0.055 | 10 | ||
| Pentachlorobenzene | 608-93-5 | 0.055 | 10 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14 | ||
| 1,1,2,2-Tetrachloroethane | 79-34-5 | 0.057 | 6.0 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| 1,2,4-Trichlorobenzene | 120-82-1 | 0.055 | 19 | ||
| K151 | Wastewater treatment sludges, excluding neutralization and biological sludges, generated during the treatment of wastewaters from the production of alpha-(or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. | Benzene | 71-43-2 | 0.14 | 10 |
| Carbon tetrachloride | 56-23-5 | 0.057 | 6.0 | ||
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Hexachlorobenzene | 118-74-1 | 0.055 | 10 | ||
| Pentachlorobenzene | 608-93-5 | 0.055 | 10 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| Toluene | 108-88-3 | 0.080 | 10 | ||
| K156 | Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes. | Acetonitrile | 75-05-8 | 5.6 | 1.8 |
| Acetophenone | 98-86-2 | 0.010 | 9.7 | ||
| Aniline | 62-53-3 | 0.81 | 14 | ||
| Benomyl10 | 17804-35-2 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST | ||
| Benzene | 71-43-2 | 0.14 | 10 | ||
| Carbaryl10 | 63-25-2 | 0.006; or CMBST, CHOXD, BIODG or CARBN | 0.14; or CMBST | ||
| Carbenzadim10 | 10605-21-7 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST | ||
| Carbofuran10 | 1563-66-2 | 0.006; or CMBST, CHOXD, BIODG or CARBN | 0.14; or CMBST | ||
| Carbosulfan10 | 55285-14-8 | 0.028; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST | ||
| Chlorobenzene | 108-90-7 | 0.057 | 6.0 | ||
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| o-Dichlorobenzene | 95-50-1 | 0.088 | 6.0 | ||
| Methomyl10 | 16752-77-5 | 0.028; or CMBST, CHOXD, BIODG or CARBN | 0.14; or CMBST | ||
| Methylene chloride | 75-09-2 | 0.089 | 30 | ||
| Methyl ethyl ketone | 78-93-3 | 0.28 | 36 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Pyridine | 110-86-1 | 0.014 | 16 | ||
| Toluene | 108-88-3 | 0.080 | 10 | ||
| Triethylamine | 121-44-8 | 0.081; or CMBST, CHOXD, BIODG or CARBN | 1.5; or CMBST | ||
| K157 | Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes. | Carbon tetrachloride | 56-23-5 | 0.057 | 6.0 |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Chloromethane | 74-87-3 | 0.19 | 30 | ||
| Methomyl10 | 16752-77-5 | 0.028; or CMBST, CHOXD, BIODG or CARBN | 0.14; or CMBST | ||
| Methylene chloride | 75-09-2 | 0.089 | 30 | ||
| Methyl ethyl ketone | 78-93-3 | 0.28 | 36 | ||
| Pyridine | 110-86-1 | 0.014 | 16 | ||
| Triethylamine | 121-44-8; or CMBST, CHOXD, BIODG or CARBN | 0.081 | 1.5; or CMBST | ||
| K158 | Bag house dusts and filter/separation solids from the production of carbamates and carbamoyl oximes. | Benomyl | 17804-35-2 | 0.056 | 1.4 |
| Benzene | 71-43-2 | 0.14 | 10 | ||
| Carbenzadim10 | 10605-21-7 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST | ||
| Carbofuran10 | 1563-66-2 | 0.006; or CMBST, CHOXD, BIODG or CARBN | 0.14; or CMBST | ||
| Carbosulfan10 | 55285-14-8 | 0.028; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST | ||
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Methylene chloride | 75-09-2 | 0.089 | 30 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| K159 | Organics from the treatment of thiocarbamate wastes. | Benzene | 71-43-2 | 0.14 | 10 |
| Butylate10 | 2008-41-5 | 0.042; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST | ||
| EPTC (Eptam)10 | 759-94-4 | 0.042; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST | ||
| Molinate10 | 2212-67-1 | 0.042; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST | ||
| Pebulate10 | 1114-71-2 | 0.042; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST | ||
| Vernolate10 | 1929-77-7 | 0.042; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST | ||
| K161 | Purification solids (including filtration, evaporation, and centrifugation solids), baghouse dust and floor sweepings from the production of dithiocarbamate acids and their salts. | Antimony | 7440-36-0 | 1.9 | 1.15 mg/l TCLP |
| Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP | ||
| Carbon disulfide | 75-15-0 | 3.8 | 4.8 mg/l TCLP | ||
| Dithiocarbamates (total)10 | NA | 0.028; or CMBST, CHOXD, BIODG or CARBN | 28; or CMBST | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11 mg/l TCLP | ||
| Selenium | 7782-49-2 | 0.82 | 5.7 mg/l TCLP | ||
| K169 | Crude oil tank sediment from petroleum refining operations. | Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 |
| Benzene | 71-43-2 | 0.14 | 10 | ||
| Benzo(g, h, i)perylene | 191-24-2 | 0.0055 | 1.8 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Ethyl benzene | 100-41-4 | 0.057 | 10 | ||
| Fluorene | 86-73-7 | 0.059 | 3.4 | ||
| Napthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenanthrene | 81-05-8 | 0.059 | 5.6 | ||
| Pyrene | 129-00-0 | 0.067 | 8.2 | ||
| Toluene (Methyl Benzene) | 108-88-3 | 0.080 | 10 | ||
| Xylene(s) (Total) | 1330-20-7 | 0.32 | 0 | ||
| K170 | Clarified slurry oil sediment from petroleum refining operations. | Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 |
| Benzene | 71-43-2 | 0.14 | 10 | ||
| Benzo(g,h,i)perylene | 191-24-2 | 0.0055 | 1.8 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Dibenz(a,h)anthracene | 53-70-3 | 0.055 | 8.2 | ||
| Ethyl benzene | 100-41-4 | 0.057 | 10 | ||
| Fluorene | 86-73-7 | 0.059 | 3.4 | ||
| Indeno(1,2,3,-cd)pyrene | 193-39-5 | 0.0055 | 3.4 | ||
| Napthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenanthrene | 81-05-8 | 0.059 | 5.6 | ||
| Pyrene | 129-00-0 | 0.067 | 8.2 | ||
| Toluene (Methyl Benzene) | 108-88-3 | 0.080 | 10 | ||
| Xylene(s) Total | 1330-20-7 | 0.32 | 30 | ||
| K171 | Spend hydrotreating catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media). | Benz(a)anthracene Benzene Chrysene Ethyl benzene Napthalene Phenanthrene Pyrene Toluene (Methyl Benzene) Xylene(s) (Total) Arsenic Nickel Vanadium Reactive Sulfides | 56-55-3 71-43-2 218-01-9 100-41-4 91-20-3 81-05-8 129-00-0 108-88-3 1330-20-7 7740-38-2 7440-02-0 7440-62-2 NA | 0.059 0.14 0.059 0.057 0.059 0.059 0.067 0.080 0.32 1.4 3.98 4.3 DEACT | 3.4 10 3.4 10 5.6 5.6 8.2 10 30 5 mg/l TCLP 11.0 mg/l TCLP 1.6 mg/l TCLP DEACT |
| K172 | Spent dydroerefining catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media). | Benzene Ethyl benzene Toluene (Methyl Benzene) Xylene(s) (Total) Antimony Arsenic Nickel Vanadium Reactive Sulfides | 71-43-2 100-41-4 108-88-3 1330-20-7 7740-36-0 7740-38-2 7440-02-0 7440-62-2 NA | 0.14 0.057 0.080 0.32 1.9 1.4 3.98 4.3 DEACT | 10 10 10 30 1.15 mg/l TCLP 5 mg/l TCLP 11.0 mg/l TCLP 1.6 mg/l TCLP DEACT |
| K174 | Wastewater treatment sludges from the production of ethylene dichloride or vinyl chloride monomer. | 1,2,3,4,6,7,8- Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD) | 35822-46-9 | 0.000035 or CMBST11 | 0.0025 or CMBST11 |
| 1,2,3,4,6,7,8- Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF) | 67562-39-4 | 0.000035 or CMBST11 | 0.0025 or CMBST11 | ||
| 1,2,3,4,7,8,9- Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpDCF) | 55673-89-7 | 0.000035 or CMBST11 | 0.0025 or CMBST11 | ||
| HxCDDs (all Hexachlorodibenzo-p-dioxins) | 34465-46-8 | 0.000063 or CMBST11 | 0.001 or CMBST11 | ||
| HxCDFs (all Hexachlorodibenzofurans) | 55684-94-1 | 0.000063 or CMBST11 | 0.001 or CMBST11 | ||
| 1,2,3,4,6,7,8,9- Octachlorodibenzo-p-dioxin (OCDD) | 3268-87-9 | 0.000063 or CMBST11 | 0.005 or CMBST11 | ||
| 1,2,3,4,6,7,8,9- Octachlorodibenzofuran (OCDF) | 39001-02-0 | 0.000063 or CMBST11 | 0.005 or CMBST11 | ||
| PeCDDs (all Pentachlorodibenzo-p-dioxins) | 36088-22-9 | 0.000063 or CMBST11 | 0.001 or CMBST11 | ||
| PeCDFs (all Pentachlorodibenzofurans) | 30402-15-4 | 0.000035 or CMBST11 | 0.001 or CMBST11 | ||
| TCDDs (all tetrachlorodibenzo-p-dioxins) | 41903-27-5 | 0.000063 or CMBST11 | 0.001 or CMBST11 | ||
| TCDFs (all tetrachlorodibenzofurans) | 55722-27-5 | 0.000063 or CMBST11 | 0.001 or CMBST11 | ||
| Arsenic | 7440-36-0 | 1.4 | 5.0 mg/L TCLP | ||
| K175 | Wastewater treatment sludge from the production of vinyl chloride monomer using mercuric chloride catalyst in an acetylene-based process. | Mercury12 pH12 | 7438-97-6 | NA NA | 0.025 mg/L TCLP pH ≤ 6.0 |
| All K175 wastewaters | Mercury | 7438-97-6 | 0.15 | NA | |
| K176 | Baghouse filters from the production of anitmony oxide, including filters from the production of intermediates (e.g., antimony metal or crude antimony oxide). | Antimony Arsenic Cadmium Lead Mercury | 7440-36-0 7440-38-2 7440-43-9 7439-92-1 7439-97-6 | 1.9 1.4 0.69 0.69 0.15 | 1.15 mg/L TCLP 5.0 mg/L TCLP 0.11 mg/L TCLP 0.75 mg/L TCLP 0.025 mg/L TCLP |
| K177 | Slag from the production of antimony oxide that is speculatively accumulated or disposed, including slag from the production of intermediates (e.g., antimony metal or crude antimony oxide). | Antimony Arsenic Lead | 7440-36-0 7440-38-2 7439-92-1 | 1.9 1.4 0.69 | 1.15 mg/L TCLP 5.0 mg/L TCLP 0.75 mg/L TCLP |
| K178 | Residues from manufacturing and manufacturing-site storage of ferric chloride from acids formed during the production of titanium dioxide using the chloride-ilmenite process. | 1,2,3,4,6,7,8- Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD) | 35822-39-4 | 0.000035 or CMBST11 | 0.0025 or CMBST11 |
| 1,2,3,4,6,7,8- Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF) | 67562-39-4 | 0.000035 or CMBST11 | 0.0025 or CMBST11 | ||
| 1,2,3,4,7,8,9- Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpDCF) | 55673-89-7 | 0.000035 or CMBST11 | 0.0025 or CMBST11 | ||
| HxCDDs (all Hexachlorodibenzo-p-dioxins) | 34465-46-8 | 0.000063 or CMBST11 | 0.001 or CMBST11 | ||
| HxCDFs (all Hexachlorodibenzofurans) | 55684-94-1 | 0.000063 or CMBST11 | 0.001 or CMBST11 | ||
| 1,2,3,4,6,7,8,9- Octachlorodibenzo-p-dioxin (OCDD) | 3268-87-9 | 0.000063 or CMBST11 | 0.005 or CMBST11 | ||
| 1,2,3,4,6,7,8,9- Octachlorodibenzofuran (OCDF) | 39001-02-0 | 0.000063 or CMBST11 | 0.005 or CMBST11 | ||
| PeCDDs (all Pentachlorodibenzo-p-dioxins) | 36088-22-9 | 0.000063 or CMBST11 | 0.001 or CMBST11 | ||
| PeCDFs (all Pentachlorodibenzofurans) | 30402-15-4 | 0.000035 or CMBST11 | 0.001 or CMBST11 | ||
| TCDDs (all tetrachlorodibenzo-p-dioxins) | 41903-57-5 | 0.000063 or CMBST11 | 0.001 or CMBST11 | ||
| TCDFs (all tetrachlorodibenzofurans) | 55722-27-5 | 0.000063 or CMBST11 | 0.001 or CMBST11 | ||
| Thallium | 7440-28-0 | 1.4 | 0.20 mg/L TCLP | ||
| K181 | Nonwastewaters from the production of dyes and/or pigments (including nonwastewaters commingled at the point of generation with nonwastewaters from other processes) that, at the point of generation, contain mass loadings of any of the constituents identified in paragraph 371.4(c)(1) of this Title, that are equal to or greater than the corresponding paragraph 371.4(c)(1) levels, as determined on a calendar year basis. | Aniline | 62-53-3 | 0.81 | 14 |
| o-Anisidine (2 methoxyaniline) | 90-04-0 | 0.010 | 0.66 | ||
| 4-Chloroaniline | 106-47-8 | 0.46 | 16 | ||
| p-Cresidine | 120-71-8 | 0.010 | 0.66 | ||
| 2,4-Dimethylaniline (2,4-xylidine) | 95-68-1 | 0.010 | 0.66 | ||
| 1,2-Phenylenediamine | 95-54-5 | CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN | CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN | ||
| 1,3 Phenylenediamine | 108-45-2 | 0.010 | 0.66 | ||
| P001 | Warfarin, & salts, when present at concentrations greater than 0.3% | Warfarin | 81-81-2 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P002 | 1-Acetyl-2-thiourea | 1-Acetyl-2-thiourea | 591-08-2 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P003 | Acrolein | Acrolein | 107-02-8 | 0.29 | CMBST |
| P004 | Aldrin | Aldrin | 309-00-2 | 0.021 | 0.066 |
| P005 | Allyl alcohol | Allyl alcohol | 107-18-6 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P006 | Aluminum phosphide | Aluminum phosphide | 20859-73-8 | CHOXD; CHRED; or CMBST | CHOXD; CHRED; or CMBST |
| P007 | 5-Aminomethyl 3-isoxazolol | 5-Aminomethyl 3-isoxazolol | 2763-96-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P008 | 4-Aminopyridine | 4-Aminopyridine | 504-24-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P009 | Ammonium picrate | Ammonium picrate | 131-74-8 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| P010 | Arsenic acid | Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP |
| P011 | Arsenic pentoxide | Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP |
| P012 | Arsenic trioxide | Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP |
| P013 | Barium cyanide | Barium | 7440-39-3 | NA | 21 mg/l TCLP |
| Cyanides (Total)7 | 57-12-5 | 1.2 | 590 | ||
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | 30 | ||
| P014 | Thiophenol (Benzene thiol) | Thiophenol (Benzene thiol) | 108-98-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P015 | Beryllium powder | Beryllium | 7440-41-7 | RMETL; or RTHRM | RMETL; or RTHRM |
| P016 | Dichloromethyl ether (Bis(chloromethyl)ether) | Dichloromethyl ether | 542-88-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P017 | Bromoacetone | Bromoacetone | 598-31-2 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P018 | Brucine | Brucine | 357-57-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P020 | 2-sec-Butyl-4,6-dinitrophenol (Dinoseb) | 2-sec-Butyl-4,6-dinitrophenol (Dinoseb) | 88-85-7 | 0.066 | 2.5 |
| P021 | Calcium cyanide | Cyanides (Total)7 | 57-12-5 | 1.2 | 590 |
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | 30 | ||
| P022 | Carbon disulfide | Carbon disulfide | 75-15-0 | 3.8 | CMBST |
| Carbon disulfide; alternate6 standard for nonwastewaters only | 75-15-0 | NA | 4.8 mg/l TCLP | ||
| P023 | Chloroacetaldehyde | Chloroacetaldehyde | 107-20-0 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P024 | p-Chloroaniline | p-Chloroaniline | 106-47-8 | 0.46 | 16 |
| P026 | 1-(o-Chlorophenyl)thiourea | 1-(o-Chlorophenyl)thiourea | 5344-82-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P027 | 3-Chloropropionitrile | 3-Chloropropionitrile | 542-76-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P028 | Benzyl chloride | Benzyl chloride | 100-44-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P029 | Copper cyanide | Cyanides (Total)7 | 57-12-5 | 1.2 | 590 |
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | 30 | ||
| P030 | Cyanides (soluble salts and complexes) | Cyanides (Total)7 | 57-12-5 | 1.2 | 590 |
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | 30 | ||
| P031 | Cyanogen | Cyanogen | 460-19-5 | CHOXD; WETOX; or CMBST | CHOXD; WETOX; or CMBST |
| P033 | Cyanogen chloride | Cyanogen chloride | 506-77-4 | CHOXD; WETOX; or CMBST | CHOXD; WETOX; or CMBST |
| P034 | 2-Cyclohexyl-4,6- dinitrophenol | 2-Cycl- ohexyl-4,6-dinitrophenol | 131-89-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P036 | Dichlorophenylarsine | Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP |
| P037 | Dieldrin | Dieldrin | 60-57-1 | 0.017 | 0.13 |
| P038 | Diethylarsine | Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP |
| P039 | Disulfoton | Disulfoton | 298-04-4 | 0.017 | 6.2 |
| P040 | 0,0-Diethyl O-pyrazinyl phosphorothioate | 0,0-Diethyl O-pyrazinyl phosphorothioate | 297-97-2 | CARBN; or CMBST | CMBST |
| P041 | Diethyl-p-nitrophenyl phosphate | Diethyl-p-nitrophenyl phosphate | 311-45-5 | CARBN; or CMBST | CMBST |
| P042 | Epinephrine | Epinephrine | 51-43-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P043 | Diisopropylfluorophosphate (DFP) | Diisopropylfluorophosphate (DFP) | 55-91-4 | CARBN; or CMBST | CMBST |
| P044 | Dimethoate | Dimethoate | 60-51-5 | CARBN; or CMBST | CMBST |
| P045 | Thiofanox | Thiofanox | 39196-18-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P046 | alpha, alpha-Dimethylphenethylamine | alpha, alpha- Dimethylphenethylamine | 122-09-8 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P047 | 4,6-Dinitro-o-cresol | 4,6-Dinitro-o-cresol | 543-52-1 | 0.28 | 160 |
| 4,6-Dinitro-o-cresol salts | NA | NA | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST | |
| P048 | 2,4-Dinitrophenol | 2,4-Dinitrophenol | 51-28-5 | 0.12 | 160 |
| P049 | Dithiobiuret | Dithiobiuret | 541-53-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P050 | Endosulfan | Endosulfan I | 939-98-8 | 0.023 | 0.066 |
| Endosulfan II | 33213-6-5 | 0.029 | 0.13 | ||
| Endosulfan sulfate | 1031-07-8 | 0.029 | 0.13 | ||
| P051 | Endrin | Endrin | 72-20-8 | 0.0028 | 0.13 |
| Endrin aldehyde | 7421-93-4 | 0.025 | 0.13 | ||
| P054 | Aziridine | Aziridine | 151-56-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P056 | Fluorine | Fluoride (measured in wastewaters only) | 16964-48-8 | 35 | ADGAS fb NEUTR |
| P057 | Fluoroacetamide | Fluoroacetamide | 640-19-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P058 | Fluoroacetic acid, sodium salt | Fluoroacetic acid, sodium salt | 62-74-8 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P059 | Heptachlor | Heptachlor | 76-44-8 | 0.0012 | 0.066 |
| Heptachlor epoxide | 1024-57-3 | 0.016 | 0.066 | ||
| P060 | Isodrin | Isodrin | 465-73-6 | 0.021 | 0.066 |
| P062 | Hexaethyl tetraphosphate | Hexaethyl tetraphosphate | 757-58-4 | CARBN; or CMBST | CMBST |
| P063 | Hydrogen cyanide | Cyanides (Total)7 | 57-12-5 | 1.2 | 590 |
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | 30 | ||
| P064 | Isocyanic acid, ethyl ester | Isocyanic acid, ethyl ester | 624-83-9 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P065 | Mercury fulminate nonwastewaters, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC. | Mercury | 7439-97-6 | NA | IMERC |
| Mercury fulminate nonwastewaters that are either incinerator residues or are residues from RMERC; and contain greater than or equal to 260 mg/kg total mercury. | Mercury | 7439-97-6 | NA | RMERC | |
| Mercury fulminate nonwastewaters that are residues from RMERC and contain less than 260 mg/kg total mercury. | Mercury | 7439-97-6 | NA | 0.20 mg/l TCLP | |
| Mercury fulminate nonwastewaters that are incinerator residues and contain less than 260 mg/kg total mercury. | Mercury | 7439-97-6 | NA | 0.025 mg/l TCLP | |
| All mercury fulminate wastewaters. | Mercury | 7439-97-6 | 0.15 | NA | |
| P066 | Methomyl | Methomyl | 16752-77-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P067 | 2-Methyl-aziridine | 2-Methyl-aziridine | 75-55-8 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P068 | Methyl hydrazine | Methyl hydrazine | 60-34-4 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| P069 | 2-Methyllactonitrile | 2-Methyllactonitrile | 75-86-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P070 | Aldicarb | Aldicarb | 116-06-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P071 | Methyl parathion | Methyl parathion | 298-00-0 | 0.014 | 4.6 |
| P072 | 1-Naphthyl-2-thiourea | 1-Naphthyl-2-thiourea | 86-88-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P073 | Nickel carbonyl | Nickel | 7440-02-0 | 3.98 | 11 mg/l TCLP |
| P074 | Nickel-cyanide | Cyanides (Total)7 | 57-12-5 | 1.2 | 590 |
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | 30 | ||
| Nickel | 7440-02-0 | 3.98 | 11 mg/l TCLP | ||
| P075 | Nicotine and salts | Nicotine and salts | 54-11-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P076 | Nitric oxide | Nitric oxide | 10102-43-9 | ADGAS | ADGAS |
| P077 | p-Nitroaniline | p-Nitroaniline | 100-01-6 | 0.028 | 28 |
| P078 | Nitrogen dioxide | Nitrogen dioxide | 10102-44-0 | ADGAS | ADGAS |
| P081 | Nitroglycerin | Nitroglycerin | 55-63-0 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| P082 | N-Nitrosodimethylamine | N-Nitrosodimethylamine | 62-75-9 | 0.40 | 2.3 |
| P084 | N-Nitrosomethylvinylamine | N-Nitrosomethylvinylamine | 4549-40-0 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P085 | Octamethylpyrophosphoramide | Octamethylpyro- phosphoramide | 152-16-9 | CARBN; or CMBST | CMBST |
| P087 | Osmium tetroxide | Osmium tetroxide | 20816-12-0 | RMETL; or RTHRM | RMETL; or RTHRM |
| P088 | Endothall | Endothall | 145-73-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P089 | Parathion | Parathion | 56-38-2 | 0.014 | 4.6 |
| P092 | Phenyl mercuric acetate nonwastewaters, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC. | Mercury | 7439-97-6 | NA | IMERC; or RMERC |
| Phenyl mercuric acetate nonwastewaters that are either incinerator residues or are residues from RMERC; and still contain greater than or equal to 260 mg/kg total mercury. | Mercury | 7439-97-6 | NA | RMERC | |
| Phenyl mercuric acetate nonwastewaters that are residues from RMERC and contain less than 260 mg/kg total mercury. | Mercury | 7439-97-6 | NA | 0.20 mg/l TCLP | |
| Phenyl mercuric acetate nonwastewaters that are incinerator residues and contain less than 260 mg/kg total mercury. | Mercury | 7439-97-6 | NA | 0.025 mg/l TCLP | |
| All phenyl mercuric acetate wastewaters. | Mercury | 7439-97-6 | 0.15 | NA | |
| P093 | Phenylthiourea | Phenylthiourea | 103-85-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P094 | Phorate | Phorate | 298-02-2 | 0.021 | 4.6 |
| P095 | Phosgene | Phosgene | 75-44-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P096 | Phosphine | Phosphine | 7803-51-2 | CHOXD; CHRED; or CMBST | CHOXD; CHRED; or CMBST |
| P097 | Famphur | Famphur | 52-85-7 | 0.017 | 15 |
| P098 | Potassium cyanide. | Cyanides (Total)7 | 57-12-5 | 1.2 | 590 |
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | 30 | ||
| P099 | Potassium silver cyanide | Cyanides (Total)7 | 57-12-5 | 1.2 | 590 |
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | 30 | ||
| Silver | 7440-22-4 | 0.43 | 0.14 mg/l TCLP | ||
| P101 | Ethyl cyanide (Propanenitrile) | Ethyl cyanide (Propanenitrile) | 107-12-0 | 0.24 | 360 |
| P102 | Propargyl alcohol | Propargyl alcohol | 107-19-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P103 | Selenourea | Selenium | 7782-49-2 | 0.82 | 5.7 mg/l TCLP |
| P104 | Silver cyanide | Cyanides (Total)7 | 57-12-5 | 1.2 | 590 |
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | 30 | ||
| Silver | 7440-22-4 | 0.43 | 0.14 mg/l TCLP | ||
| P105 | Sodium azide | Sodium azide | 26628-22-8 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| P106 | Sodium cyanide | Cyanides (Total)7 | 57-12-5 | 1.2 | 590 |
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | 30 | ||
| P108 | Strychnine and salts | Strychnine and salts | 57-24-9 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P109 | Tetraethyldithiopyrophosphate | Tetraethyldithiopyrophosphate | 3689-24-5 | CARBN; or CMBST | CMBST |
| P110 | Tetraethyl lead | Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP |
| P111 | Tetraethylpyrophosphate | Tetraethylpyrophosphate | 107-49-3 | CARBN; or CMBST | CMBST |
| P112 | Tetranitromethane | Tetranitromethane | 509-14-8 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| P113 | Thallic oxide | Thallium (measured in wastewaters only) | 7440-28-0 | 1.4 | RTHRM; or STABL |
| P114 | Thallium selenite | Selenium | 7782-49-2 | 0.82 | 5.7 mg/l TCLP |
| P115 | Thallium (i) sulfate | Thallium (measured in wastewaters only) | 7440-28-0 | 1.4 | RTHRM; or STABL |
| P116 | Thiosemicarbazide | Thiosemicarbazide | 79-19-6 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P118 | Trichloromethanethiol | Trichloromethanethiol | 75-70-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P119 | Ammonium vanadate | Vanadium (measured in wastewaters only) | 7440-62-2 | 4.3 | STABL |
| P120 | Vanadium pentoxide | Vanadium (measured in wastewaters only) | 7440-62-2 | 4.3 | STABL |
| P121 | Zinc cyanide | Cyanides (Total)7 | 57-12-5 | 1.2 | 590 |
| Cyanides (Amenable)7 | 57-12-5 | 0.86 | 30 | ||
| P122 | Zinc phosphide Zn3P2, when present at concentrations greater than 10% | Zinc Phosphide | 1314-84-7 | CHOXD; CHRED; or CMBST | CHOXD; CHRED; or CMBST |
| P123 | Toxaphene | Toxaphene | 8001-35-2 | 0.0095 | 2.6 |
| P127 | Carbofuran10 | Carbofuran | 1563-66-2 | 0.006; or CMBST, CHOXD, BIODG or CARBN | 0.14; or CMBST |
| P128 | Mexacarbate10 | Mexacarbate | 315-18-4 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| P185 | Tirpate10 | Tirpate | 26419-73-8 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 0.28; or CMBST |
| P188 | Physostigmine salicylate10 | Physostigmine salicylate | 57-64-7 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| P189 | Carbosulfan10 | Carbosulfan | 55285-14-8 | 0.028; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| P190 | Metolcarb10 | Metolcarb | 1129-41-5 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| P191 | Dimetilan10 | Dimetilan | 644-64-4 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| P192 | Isolan10 | Isolan | 119-38-0 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| P194 | Oxamyl10 | Oxamyl | 23135-22-0 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 0.28; or CMBST |
| P196 | Manganese dimethyldithiocarbamate10 | Dithiocarbamates (total) | NA | 0.028; or CMBST, CHOXD, BIODG or CARBN | 28; or CMBST |
| P197 | Formparanate10 | Formparanate | 17702-57-7 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| P198 | Formetanate hydrochloride10 | Formetanate hydrochloride | 23422-53-9 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| P199 | Methiocarb10 | Methiocarb | 2032-65-7 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| P201 | Promecarb10 | Promecarb | 2631-37-0 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| P202 | m-Cumenyl methylcarbamate10 | m-Cumenyl methylcarbamate | 64-00-6 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| P203 | Aldicarb sulfone10 | Aldicarb sulfone | 1646-88-4 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 0.28; or CMBST |
| P204 | Physostigmine10 | Physostigmine | 57-47-6 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| P205 | Ziram10 | Dithiocarbamates (total) | NA | 0.028; or CMBST, CHOXD, BIODG or CARBN | 28; or CMBST |
| U001 | Acetaldehyde | Acetaldehyde | 75-07-0 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U002 | Acetone | Acetone | 67-64-1 | 0.28 | 160 |
| U003 | Acetonitrile | Acetonitrile | 75-05-8 | 5.6 | CMBST |
| Acetonitrile; alternate6standard for nonwastewaters only | 75-05-8 | NA | 38 | ||
| U004 | Acetophenone | Acetophenone | 98-86-2 | 0.010 | 9.7 |
| U005 | 2-Acetylaminofluorene | 2-Acetylaminofluorene | 53-96-3 | 0.059 | 140 |
| U006 | Acetyl chloride | Acetyl Chloride | 75-36-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U007 | Acrylamide | Acrylamide | 79-06-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U008 | Acrylic acid | Acrylic acid | 79-10-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U009 | Acrylonitrile | Acrylonitrile | 107-13-1 | 0.24 | 84 |
| U010 | Mitomycin C | Mitomycin C | 50-07-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U011 | Amitrole | Amitrole | 61-82-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U012 | Aniline | Aniline | 62-53-3 | 0.81 | 14 |
| U014 | Auramine | Auramine | 492-80-8 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U015 | Azaserine | Azaserine | 115-02-6 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U016 | Benz(c)acridine | Benz(c)acridine | 225-51-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U017 | Benzal chloride | Benzal chloride | 98-87-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U018 | Benz(a)anthracene | Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 |
| U019 | Benzene | Benzene | 71-43-2 | 0.14 | 10 |
| U020 | Benzenesulfonyl chloride | Benzenesulfonyl chloride | 98-09-9 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U021 | Benzidine | Benzidine | 92-87-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U022 | Benzo(a)pyrene | Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 |
| U023 | Benzotrichloride | Benzotrichloride | 98-07-7 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| U024 | bis(2-Chloroethoxy)methane | bis(2-Chloroethoxy)methane | 111-91-1 | 0.036 | 7.2 |
| U025 | bis(2-Chloroethyl)ether | bis(2-Chloroethyl)ether | 111-44-4 | 0.033 | 6.0 |
| U026 | Chlornaphazine | Chlornaphazine | 494-03-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U027 | bis(2-Chloroisopropyl)ether | bis(2-Chloroisopropyl)ether | 39638-32-9 | 0.055 | 7.2 |
| U028 | bis(2-Ethylhexyl) phthalate | bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28 |
| U029 | Methyl bromide (Bromomethane) | Methyl bromide (Bromomethane) | 74-83-9 | 0.11 | 15 |
| U030 | 4-Bromophenyl phenyl ether | 4-Bromophenyl phenyl ether | 101-55-3 | 0.055 | 15 |
| U031 | n-Butyl alcohol | n-Butyl alcohol | 71-36-3 | 5.6 | 2.6 |
| U032 | Calcium chromate | Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP |
| U033 | Carbon oxyfluoride | Carbon oxyfluoride | 353-50-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U034 | Trichloroacetaldehyde (Chloral) | Trichloroacetaldehyde (Chloral) | 75-87-6 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U035 | Chlorambucil | Chlorambucil | 305-03-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U036 | Chlordane | Chlordane (alpha and gamma isomers) | 57-74-9 | 0.0033 | 0.26 |
| U037 | Chlorobenzene | Chlorobenzene | 108-90-7 | 0.057 | 6.0 |
| U038 | Chlorobenzilate | Chlorobenzilate | 510-15-6 | 0.10 | CMBST |
| U039 | p-Chloro-m-cresol | p-Chloro-m-cresol | 59-50-7 | 0.018 | 14 |
| U041 | Epichlorohydrin (1-Chloro-2,3-epoxypropane) | Epichlorohydrin (1-Chloro-2,3-epoxypropane) | 106-89-8 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U042 | 2-Chloroethyl vinyl ether | 2-Chloroethyl vinyl ether | 110-75-8 | 0.062 | CMBST |
| U043 | Vinyl chloride | Vinyl chloride | 75-01-4 | 0.27 | 6.0 |
| U044 | Chloroform | Chloroform | 67-66-3 | 0.046 | 6.0 |
| U045 | Chloromethane (Methyl chloride) | Chloromethane (Methyl chloride) | 74-87-3 | 0.19 | 30 |
| U046 | Chloromethyl methyl ether | Chloromethyl methyl ether | 107-30-2 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U047 | 2-Chloronaphthalene | 2-Chloronaphthalene | 91-58-7 | 0.055 | 5.6 |
| U048 | 2-Chlorophenol | 2-Chlorophenol | 95-57-8 | 0.044 | 5.7 |
| U049 | 4-Chloro-o-toluidine hydrochloride | 4-Chloro-o-toluidine hydrochloride | 3165-93-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U050 | Chrysene | Chrysene | 218-01-9 | 0.059 | 3.4 |
| U051 | Creosote | Naphthalene | 91-20-3 | 0.059 | 5.6 |
| Pentachlorophenol | 87-86-5 | 0.089 | 7.4 | ||
| Phenanthrene | 85-01-8 | 0.059 | 5.6 | ||
| Pyrene | 129-00-0 | 0.067 | 8.2 | ||
| Toluene | 108-88-3 | 0.080 | 10 | ||
| Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| U052 | Cresols (Cresylic acid) | 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 | ||
| Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations) | 1319-77-3 | 0.88 | 11.2 | ||
| U053 | Crotonaldehyde | Crotonaldehyde | 4170-30-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U055 | Cumene | Cumene | 98-82-8 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U056 | Cyclohexane | Cyclohexane | 110-82-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U057 | Cyclohexanone | Cyclohexanone | 108-94-1 | 0.36 | CMBST |
| Cyclohexanone; alternate6standard for nonwastewaters only | 108-94-1 | NA | 0.75 mg/l TCLP | ||
| U058 | Cyclophosphamide | Cyclophosphamide | 50-18-0 | CARBN; or CMBST | CMBST |
| U059 | Daunomycin | Daunomycin | 20830-81-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U060 | DDD | o,p'-DDD | 53-19-0 | 0.023 | 0.087 |
| p,p'-DDD | 72-54-8 | 0.023 | 0.087 | ||
| U061 | DDT | o-p'-DDT | 789-02-6 | 0.0039 | 0.087 |
| p,p'-DDT | 50-29-3 | 0.0039 | 0.087 | ||
| 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 | ||
| U062 | Diallate | Diallate | 2303-16-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U063 | Dibenz(a,h)anthracene | Dibenz(a,h)anthracene | 53-70-3 | 0.055 | 8.2 |
| U064 | Dibenz(a,i)pyrene | Dibenz(a,i)pyrene | 189-55-9 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U066 | 1,2-Dibromo-3-chloropropane | 1,2-Dibromo- 3-chloro- propane | 96-12-8 | 0.11 | 15 |
| U067 | Ethylene dibromide (1,2-Dibromoethane) | Ethylene dibromide (1,2-Dibromoethane) | 106-93-4 | 0.028 | 15 |
| U068 | Dibromomethane | Dibromomethane | 74-95-3 | 0.11 | 15 |
| U069 | Di-n-butyl phthalate | Di-n-butyl phthalate | 84-74-2 | 0.057 | 28 |
| U070 | o-Dichlorobenzene | o-Dichlorobenzene | 95-50-1 | 0.088 | 6.0 |
| U071 | m-Dichlorobenzene | m-Dichlorobenzene | 541-73-1 | 0.036 | 6.0 |
| U072 | p-Dichlorobenzene | p-Dichlorobenzene | 106-46-7 | 0.090 | 6.0 |
| U073 | 3,3'-Dichlorobenzidine | 3,3'-Dichlorobenzidine | 91-94-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U074 | 1,4-Dichloro-2-butene | cis-1,4-Dichloro-2-butene | 1476-11-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| trans-1,4-Dichloro-2-butene | 764-41-0 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST | ||
| U075 | Dichlorodifluoromethane | Dichlorodifluoromethane | 75-71-8 | 0.23 | 7.2 |
| U076 | 1,1-Dichloroethane | 1,1-Dichloroethane | 75-34-3 | 0.059 | 6.0 |
| U077 | 1,2-Dichloroethane | 1,2-Dichloroethane | 107-06-2 | 0.21 | 6.0 |
| U078 | 1,1-Dichloroethylene | 1,1-Dichloroethylene | 75-35-4 | 0.025 | 6.0 |
| U079 | 1,2-Dichloroethylene | trans-1,2-Dichloroethylene | 156-60-5 | 0.054 | 30 |
| U080 | Methylene chloride | Methylene chloride | 75-09-2 | 0.089 | 30 |
| U081 | 2,4-Dichlorophenol | 2,4-Dichlorophenol | 120-83-2 | 0.044 | 14 |
| U082 | 2,6-Dichlorophenol | 2,6-Dichlorophenol | 87-65-0 | 0.044 | 14 |
| U083 | 1,2-Dichloropropane | 1,2-Dichloropropane | 78-87-5 | 0.85 | 18 |
| U084 | 1,3-Dichloropropylene | cis-1,3-Dichloropropylene | 10061-01-5 | 0.036 | 18 |
| trans-1,3-Dichloropropylene | 10061-02-6 | 0.036 | 18 | ||
| U085 | 1,2:3,4-Diepoxybutane | 1,2:3,4-Diepoxybutane | 1464-53-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U086 | N,N'-Diethylhydrazine | N,N'-Diethylhydrazine | 1615-80-1 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| U087 | O,O-Diethyl S-methyldithiophosphate | O,O-Diethyl S-methyldithiophosphate | 3288-58-2 | CARBN; or CMBST | CMBST |
| U088 | Diethyl phthalate | Diethyl phthalate | 84-66-2 | 0.20 | 28 |
| U089 | Diethyl stilbestrol | Diethyl stilbestrol | 56-53-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U090 | Dihydrosafrole | Dihydrosafrole | 94-58-6 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U091 | 3,3'-Dimethoxybenzidine | 3,3'-Dimethoxybenzidine | 119-90-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U092 | Dimethylamine | Dimethylamine | 124-40-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U093 | p-Dimethylaminoazobenzene | p-Dimethylaminoazobenzene | 60-11-7 | 0.13 | CMBST |
| U094 | 7,12-Dimethylbenz(a)anthracene | 7,12-Dimethyl- benz(a)anthracene | 57-97-6 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U095 | 3,3'-Dimethylbenzidine | 3,3'-Dimethylbenzidine | 119-93-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U096 | alpha, alpha-Dimethyl benzyl hydroperoxide | alpha, alpha-Dimethyl benzyl hydroperoxide | 80-15-9 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| U097 | Dimethylcarbamoyl chloride | Dimethylcarbamoyl chloride | 79-44-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U098 | 1,1-Dimethylhydrazine | 1,1-Dimethylhydrazine | 57-14-7 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| U099 | 1,2-Dimethylhydrazine | 1,2-Dimethylhydrazine | 540-73-8 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| U101 | 2,4-Dimethylphenol | 2,4-Dimethylphenol | 105-67-9 | 0.036 | 14 |
| U102 | Dimethyl phthalate | Dimethyl phthalate | 131-11-3 | 0.047 | 28 |
| U103 | Dimethyl sulfate | Dimethyl sulfate | 77-78-1 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| U105 | 2,4-Dinitrotoluene | 2,4-Dinitrotoluene | 121-14-2 | 0.32 | 140 |
| U106 | 2,6-Dinitrotoluene | 2,6-Dinitrotoluene | 606-20-2 | 0.55 | 28 |
| U107 | Di-n-octyl phthalate | Di-n-octyl phthalate | 117-84-0 | 0.017 | 28 |
| U108 | 1,4-Dioxane | 1,4-Dioxane | 123-91-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| 1,4-Dioxane; alternate6 standard for nonwastewaters only | 123-91-1 | NA | 170 | ||
| U109 | 1,2-Diphenylhydrazine | 1,2-Diphenylhydrazine | 122-66-7 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| 1,2-Diphenylhydrazine; alternate6 standard for wastewaters only | 122-66-7 | 0.087 | NA | ||
| U110 | Dipropylamine | Dipropylamine | 142-84-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U111 | Di-n-propylnitrosamine | Di-n-propylnitrosamine | 621-64-7 | 0.40 | 14 |
| U112 | Ethyl acetate | Ethyl acetate | 141-78-6 | 0.34 | 33 |
| U113 | Ethyl acrylate | Ethyl acrylate | 140-88-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U114 | Ethylenebisdithiocarbamic acid salts and esters | Ethylenebisdithiocarbamic acid | 111-54-6 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U115 | Ethylene oxide | Ethylene oxide | 75-21-8 | (WETOX or CHOXD) fb CARBN; or CMBST | CHOXD; or CMBST |
| Ethylene oxide; alternate6standard for wastewaters only | 75-21-8 | 0.12 | NA | ||
| U116 | Ethylene thiourea | Ethylene thiourea | 96-45-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U117 | Ethyl ether | Ethyl ether | 60-29-7 | 0.12 | 160 |
| U118 | Ethyl methacrylate | Ethyl methacrylate | 97-63-2 | 0.14 | 160 |
| U119 | Ethyl methane sulfonate | Ethyl methane sulfonate | 62-50-0 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U120 | Fluoranthene | Fluoranthene | 206-44-0 | 0.068 | 3.4 |
| U121 | Trichloromonofluoromethane | Trichloromonofluoromethane | 75-69-4 | 0.020 | 30 |
| U122 | Formaldehyde | Formaldehyde | 50-00-0 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U123 | Formic acid | Formic acid | 64-18-6 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U124 | Furan | Furan | 110-00-9 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U125 | Furfural | Furfural | 98-01-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U126 | Glycidylaldehyde | Glycidylaldehyde | 765-34-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U127 | Hexachlorobenzene | Hexachlorobenzene | 118-74-1 | 0.055 | 10 |
| U128 | Hexachlorobutadiene | Hexachlorobutadiene | 87-68-3 | 0.055 | 5.6 |
| U129 | Lindane | 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 (Lindane) | 58-89-9 | 0.0017 | 0.066 | ||
| U130 | Hexachlorocyclopentadiene | Hexachlorocyclopentadiene | 77-47-4 | 0.057 | 2.4 |
| U131 | Hexachloroethane | Hexachloroethane | 67-72-1 | 0.055 | 30 |
| U132 | Hexachlorophene | Hexachlorophene | 70-30-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U133 | Hydrazine | Hydrazine | 302-01-2 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| U134 | Hydrogen fluoride | Fluoride (measured in wastewaters only) | 7664-39-3 | 35 | ADGAS fb NEUTR; or NEUTR |
| U135 | Hydrogen Sulfide | Hydrogen Sulfide | 7783-06-4 | CHOXD; CHRED, or CMBST | CHOXD; CHRED; or CMBST. |
| U136 | Cacodylic acid | Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP |
| U137 | Indeno(1,2,3-c,d)pyrene | Indeno(1,2,3-cd)pyrene | 193-39-5 | 0.0055 | 3.4 |
| U138 | Iodomethane | Iodomethane | 74-88-4 | 0.19 | 65 |
| U140 | Isobutyl alcohol | Isobutyl alcohol | 78-83-1 | 5.6 | 170 |
| U141 | Isosafrole | Isosafrole | 120-58-1 | 0.081 | 2.6 |
| U142 | Kepone | Kepone | 143-50-8 | 0.0011 | 0.13 |
| U143 | Lasiocarpine | Lasiocarpine | 303-34-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U144 | Lead acetate | Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP |
| U145 | Lead phosphate | Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP |
| U146 | Lead subacetate | Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP |
| U147 | Maleic anhydride | Maleic anhydride | 108-31-6 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U148 | Maleic hydrazide | Maleic hydrazide | 123-33-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U149 | Malononitrile | Malononitrile | 109-77-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U150 | Melphalan | Melphalan | 148-82-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U151 | U151 (mercury) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury. | Mercury | 7439-97-6 | NA | RMERC |
| U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are residues from RMERC only. | Mercury | 7439-97-6 | NA | 0.20 mg/l TCLP | |
| U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are not residues from RMERC. | Mercury | 7439-97-6 | NA | 0.025 mg/l TCLP | |
| All U151 (mercury) wastewaters. | Mercury | 7439-97-6 | 0.15 | NA | |
| Elemental Mercury Contaminated with Radioactive Materials | Mercury | 7439-97-6 | NA | AMLGM | |
| U152 | Methacrylonitrile | Methacrylonitrile | 126-98-7 | 0.24 | 84 |
| U153 | Methanethiol | Methanethiol | 74-93-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U154 | Methanol | Methanol | 67-56-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| Methanol; alternate6set of standards for both wastewaters and nonwastewaters | 67-56-1 | 5.6 | 0.75 mg/l TCLP | ||
| U155 | Methapyrilene | Methapyrilene | 91-80-5 | 0.081 | 1.5 |
| U156 | Methyl chlorocarbonate | Methyl chlorocarbonate | 79-22-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U157 | 3-Methylcholanthrene | 3-Methylcholanthrene | 56-49-5 | 0.0055 | 15 |
| U158 | 4,4'-Methylene bis(2-chloroaniline) | 4,4'-Methylene bis(2-chloroaniline) | 101-14-4 | 0.50 | 30 |
| U159 | Methyl ethyl ketone | Methyl ethyl ketone | 78-93-3 | 0.28 | 36 |
| U160 | Methyl ethyl ketone peroxide | Methyl ethyl ketone peroxide | 1338-23-4 | CHOXD; CHRED; CARBN; BIODG; or CMBST | CHOXD; CHRED; or CMBST |
| U161 | Methyl isobutyl ketone | Methyl isobutyl ketone | 108-10-1 | 0.14 | 33 |
| U162 | Methyl methacrylate | Methyl methacrylate | 80-62-6 | 0.14 | 160 |
| U163 | N-Methyl N'-nitro N-nitrosoguanidine | N-Methyl N'-nitro N-nitrosoguanidine | 70-25-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U164 | Methylthiouracil | Methylthiouracil | 56-04-2 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U165 | Naphthalene | Naphthalene | 91-20-3 | 0.059 | 5.6 |
| U166 | 1,4-Naphthoquinone | 1,4-Naphthoquinone | 130-15-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U167 | 1-Naphthlyamine | 1-Naphthlyamine | 134-32-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U168 | 2-Naphthlyamine | 2-Naphthlyamine | 91-59-8 | 0.52 | CMBST |
| U169 | Nitrobenzene | Nitrobenzene | 98-95-3 | 0.068 | 14 |
| U170 | p-Nitrophenol | p-Nitrophenol | 100-02-7 | 0.12 | 29 |
| U171 | 2-Nitropropane | 2-Nitropropane | 79-46-9 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U172 | N-Nitrosodi-n-butylamine | N-Nitrosodi-n-butylamine | 924-16-3 | 0.40 | 17 |
| U173 | N-Nitrosodiethanolamine | N-Nitrosodiethanolamine | 1116-54-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U174 | N-Nitrosodiethylamine | N-Nitrosodiethylamine | 55-18-5 | 0.40 | 28 |
| U176 | N-Nitroso-N-ethylurea | N-Nitroso-N-ethylurea | 759-73-9 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U177 | N-Nitroso-N-methylurea | N-Nitroso-N-methylurea | 684-93-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U178 | N-Nitroso-N-methylurethane | N-Nitroso-N-methylurethane | 615-53-2 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U179 | N-Nitrosopiperidine | N-Nitrosopiperidine | 100-75-4 | 0.013 | 35 |
| U180 | N-Nitrosopyrrolidine | N-Nitrosopyrrolidine | 930-55-2 | 0.013 | 35 |
| U181 | 5-Nitro-o-toluidine | 5-Nitro-o-toluidine | 99-55-8 | 0.32 | 28 |
| U182 | Paraldehyde | Paraldehyde | 123-63-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U183 | Pentachlorobenzene | Pentachlorobenzene | 608-93-5 | 0.055 | 10 |
| U184 | Pentachloroethane | Pentachloroethane | 76-01-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| Pentachloroethane; alternate6standards for both wastewaters and nonwastewaters | 76-01-7 | 0.055 | 6.0 | ||
| U185 | Pentachloronitrobenzene | Pentachloronitrobenzene | 82-68-8 | 0.055 | 4.8 |
| U186 | 1,3-Pentadiene | 1,3-Pentadiene | 504-60-9 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U187 | Phenacetin | Phenacetin | 62-44-2 | 0.081 | 16 |
| U188 | Phenol | Phenol | 108-95-2 | 0.039 | 6.2 |
| U189 | Phosphorus sulfide | Phosphorus sulfide | 1314-80-3 | CHOXD; CHRED; or CMBST | CHOXD; CHRED; or CMBST |
| U190 | Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) | Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) | 100-21-0 | 0.055 | 28 |
| Phthalic anhydride (measured as phthalic acid or Terephthalic acid) | 85-44-9 | 0.055 | 28 | ||
| U191 | 2-Picoline | 2-Picoline | 109-06-8 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U192 | Pronamide | Pronamide | 23950-58-5 | 0.093 | 1.5 |
| U193 | 1,3-Propane sultone | 1,3-Propane sultone | 1120-71-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U194 | n-Propylamine | n-Propylamine | 107-10-8 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U196 | Pyridine | Pyridine | 110-86-1 | 0.014 | 16 |
| U197 | p-Benzoquinone | p-Benzoquinone | 106-51-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U200 | Reserpine | Reserpine | 50-55-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U201 | Resorcinol | Resorcinol | 108-46-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U203 | Safrole | Safrole | 94-59-7 | 0.081 | 22 |
| U204 | Selenium dioxide | Selenium | 7782-49-2 | 0.82 | 5.7 mg/l TCLP |
| U205 | Selenium sulfide | Selenium | 7782-49-2 | 0.82 | 5.7 mg/l TCLP |
| U206 | Streptozotocin | Streptozotocin | 18883-66-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U207 | 1,2,4,5-Tetrachlorobenzene | 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14 |
| U208 | 1,1,1,2-Tetrachloroethane | 1,1,1,2-Tetrachloroethane | 630-20-6 | 0.057 | 6.0 |
| U209 | 1,1,2,2-Tetrachloroethane | 1,1,2,2-Tetrachloroethane | 79-34-5 | 0.057 | 6.0 |
| U210 | Tetrachloroethylene | Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 |
| U211 | Carbon tetrachloride | Carbon tetrachloride | 56-23-5 | 0.057 | 6.0 |
| U213 | Tetrahydrofuran | Tetrahydrofuran | 109-99-9 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U214 | Thallium (I) acetate | Thallium (measured in wastewaters only) | 7440-28-0 | 1.4 | RTHRM; or STABL |
| U215 | Thallium (I) carbonate | Thallium (measured in wastewaters only) | 7440-28-0 | 1.4 | RTHRM; or STABL |
| U216 | Thallium (I) chloride | Thallium (measured in wastewaters only) | 7440-28-0 | 1.4 | RTHRM; or STABL |
| U217 | Thallium (I) nitrate | Thallium (measured in wastewaters only) | 7440-28-0 | 1.4 | RTHRM; or STABL |
| U218 | Thioacetamide | Thioacetamide | 62-55-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U219 | Thiourea | Thiourea | 62-56-6 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U220 | Toluene | Toluene | 108-88-3 | 0.080 | 10 |
| U221 | Toluenediamine | Toluenediamine | 25376-45-8 | CARBN; or CMBST | CMBST |
| U222 | o-Toluidine hydrochloride | o-Toluidine hydrochloride | 636-21-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U223 | Toluene diisocyanate | Toluene diisocyanate | 26471-62-5 | CARBN; or CMBST | CMBST |
| U225 | Bromoform (Tribromomethane) | Bromoform (Tribromomethane) | 75-25-2 | 0.63 | 15 |
| U226 | 1,1,1-Trichloroethane | 1,1,1-Trichloroethane | 71-55-6 | 0.054 | 6.0 |
| U227 | 1,1,2-Trichloroethane | 1,1,2-Trichloroethane | 79-00-5 | 0.054 | 6.0 |
| U228 | Trichloroethylene | Trichloroethylene | 79-01-6 | 0.054 | 6.0 |
| U234 | 1,3,5-Trinitrobenzene | 1,3,5-Trinitrobenzene | 99-35-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U235 | tris-(2,3-Dibromopropyl)-phosphate | tris-(2,3-Dibromopropyl)- phosphate | 126-72-7 | 0.11 | 0.10 |
| U236 | Trypan Blue | Trypan Blue | 72-57-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U237 | Uracil mustard | Uracil mustard | 66-75-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U238 | Urethane (Ethyl carbamate) | Urethane (Ethyl carbamate) | 51-79-6 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U239 | Xylenes | Xylenes-mixed isomers(sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30 |
| U240 | 2,4-D (2,4-Dichlorophenoxyacetic acid) | 2,4-D (2,4-Dichlorophenoxyacetic acid) | 94-75-7 | 0.72 | 10 |
| 2,4-D (2,4-Dichlorophenoxyacetic acid) salts and esters | NA | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST | ||
| U243 | Hexachloropropylene | Hexachloropropylene | 1888-71-7 | 0.035 | 30 |
| U244 | Thiram | Thiram | 137-26-8 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U246 | Cyanogen bromide | Cyanogen bromide | 506-68-3 | CHOXD; WETOX; or CMBST | CHOXD; WETOX; or CMBST |
| U247 | Methoxychlor | Methoxychlor | 72-43-5 | 0.25 | 0.18 |
| U248 | Warfarin, & salts, when present at concentrations of 0.3% or less | Warfarin | 81-81-2 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U249 | Zinc phosphide, Zn3P2, when present at concentrations of 10% or less | Zinc Phosphide | 1314-84-7 | CHOXD; CHRED; or CMBST | CHOXD; CHRED; or CMBST |
| U271 | Benomyl10 | Benomyl | 17804-35-2 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U278 | Bendiocarb10 | Bendiocarb | 22781-23-3 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U279 | Carbaryl10 | Carbaryl | 63-25-2 | 0.006; or CMBST, CHOXD, BIODG or CARBN | 0.14; or CMBST |
| U280 | Barban10 | Barban | 101-27-9 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U328 | o-Toluidine | o-Toluidine | 95-53-4 | CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN. | CMBST |
| U353 | p-Toluidine | p-Toluidine | 106-49-0 | CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN | CMBST |
| U359 | 2-Ethoxyethanol | 2-Ethoxyethanol | 110-80-5 | CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN | CMBST |
| U364 | Bendiocarb phenol10 | Bendiocarb phenol | 22961-82-6 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U367 | Carbofuran phenol10 | Carbofuran phenol | 1563-38-8 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U372 | Carbendazim10 | Carbendazim | 10605-21-7 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U373 | Propham10 | Propham | 122-42-9 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U387 | Prosulfocarb10 | Prosulfocarb | 52888-80-9 | 0.042; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U389 | Triallate10 | Triallate | 2303-17-5 | 0.042; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U394 | A221310 | A2213 | 30558-43-1 | 0.042; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U395 | Diethylene glycol, dicarbamate10 | Diethylene glycol,dicarbamate | 5952-26-1 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U404 | Triethylamine10 | Triethylamine | 121-44-8 | 0.081; or CMBST, CHOXD, BIODG or CARBN | 1.5; or CMBST |
| U409 | Thiophanate-methyl10 | Thiophanate-methyl | 23564-05-8 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U410 | Thiodicarb10 | Thiodicarb | 59669-26-0 | 0.019; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
| U411 | Propoxur10 | Propoxur | 114-26-1 | 0.056; or CMBST, CHOXD, BIODG or CARBN | 1.4; or CMBST |
1 The waste descriptions provided in this table do not replace waste descriptions in Part 371 of this Title. Descriptions of treatment/regulatory subcategories are provided, as needed, to distinguish between applicability of different standards.
2 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.
3 Concentration standards for wastewaters are expressed in mg/l and are based on analysis of composite samples, except as provided in paragraph (2) of this subdivision for D004 through D011 wastes.
4 All treatment standards expressed as a technology code or combination of technology codes are explained in detail in subdivision (c) of this section, Table 1 - technology codes and descriptions of Technology-Based Standards.
5 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 section 373-2.15 or section 373-3.15 of this Title, 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 paragraph (4) of this subdivision. All concentration standards for nonwastewaters are based on analysis of grab samples.
6 Where an alternate treatment standard or set of alternate standards has been indicated, a facility may comply with this alternate standard, but only for the treatment/regulatory subcategory or physical form (i.e., wastewater and/or nonwastewater) specified for that alternate standard.
7 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 section 370.1(e) of this Title, with a sample size of 10 grams and a distillation time of one hour and 15 minutes.
8 These wastes, when rendered nonhazardous and then subsequently managed in CWA, or CWA equivalent systems are not subject to treatment standards (see section 376.1[a][3][iii] and [iv] of this Part).
9 These wastes, when rendered nonhazardous and then subsequently injected in a title 7 or 8 Class I SDWA well are not subject to treatment standards (see 40 CFR section 148.1[d]).
10 The treatment standard for this waste may be satisfied by either meeting the constituent concentrations in this table or by treating the waste by the specified technologies: combustion, as defined by the technology code CMBST in subdivision (c) Table 1 of this section, for nonwastewaters; and biodegradation as defined by the technology code BIODG, carbon adsorption as defined by the technology code CARBN, chemical oxidation as defined by the technology code CHOXD, or combustion as defined as technology code CMBST at subdivision (c) Table 1 of this section, for wastewaters.
11 For these wastes, the definition of CMBST is limited to: (1) combustion units operating under 6 NYCRR Subpart 374-1, (2) combustion units permitted under section 373-2.15, or (3) of this Title combustion units operating under section 373-3.15 of this Title, which have obtained a determination of equivalent treatment under paragraph (c)(2) of this section. Note: NA means not applicable.
12 Disposal of K175 wastes that have complied with all applicable subdivision (a) of this section treatment standards must also be macroencapsulated in accordance with subdivision (g) Table 1 of this section, unless the waste is placed in: (i) a Part 360 of this Title monofill containing only K175 wastes that meet all applicable subdivision (a) of this section treatment standards; or (ii) a dedicated Part 360 of this Title landfill cell in which all other wastes being co-disposed are at pH ≤ 6.0.
(c) Treatment standards expressed as specified technologies.
Note:
For the requirements previously found in this subdivision in Table 2—Technology-Based Standards by RCRA Waste Code, and Table 3—Technology-Based Standards for Specific Radioactive Hazardous Mixed Waste, refer to subdivision (a) of this section.
(1) The following wastes in the table in subdivision (a) of this section titled “Treatment Standards for Hazardous Waste,” for which standards are expressed as a treatment method rather than a concentration level, must be treated using the technology or technologies specified in the table entitled "Technology Codes and Description of Technology-Based Standards" in this subdivision.
Note:
Regulations in Parts 200, 201, 212, 219, 225, 227 and 257 of this Title may also apply.
Table 1
Five Letter Technology Codes and
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 of 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 applicable requirements of section 373-2.15, 373-3.15 or 374-1.8 of this Title, 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 sections 373-2.15 and 373-3.15. 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 sections 373-2.15 and 373-3.15.
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 section 370.2(b) of this Title.
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 two 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, fluorides, 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 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/crystallization (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 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 section 370.2(b) of this Title.
RZINC: Resmelting for the purpose of recovery of zinc in high temperature metal recovery units.
STABL: Stabilization with the following reagents (or waste reagents) or combinations of raagents: (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 2 of this subdivision, 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.
(2) Any person may submit an application to the EPA administrator, pursuant to 40 CFR section 268.42(b) and the commissioner demonstrating that an alternative treatment method can achieve a measure of performance equivalent to that achieved by methods specified for wastes in paragraphs (1), (3) and (4) of this subdivision or specified for hazardous debris in Table 1 of subdivision (g) of this section. Applicants must submit information demonstrating that their treatment method is in compliance with Federal, State and local requirements and is protective of human health and the environment. On the basis of such information and any other available information, the commissioner may approve the use of the alternative treatment method if the department finds that the alternative treatment method provides a measure of performance equivalent to that achieved by methods specified for wastes in paragraphs (1), (3), and (4) of this subdivision, or specified for hazardous debris in Table 1 of subdivision (g) of this section. Any approval must be stated in writing and may contain such provisions and conditions as the commissioner deems appropriate. The person to whom such approval is issued must comply with all limitations contained in such a determination. Before the approval can take effect, the EPA administrator must also have approved the application pursuant to 40 CFR section 268.42(b).
(3) As an alternative to the otherwise applicable section 376.4 treatment standards, lab packs are eligible for land disposal provided the following requirements are met:
(i) the lab packs comply with the applicable provisions of sections 373-2.14(1) and 373-3.14(i) of this Title;
(ii) the lab pack does not contain any of the wastes listed in Appendix 38 of this Title;
(iii) the lab packs are incinerated in accordance with the requirements of section 373-2.15 or 373-3.15 of this Title; and
(iv) any incinerator residues from lab packs containing D004, D005, D006, D007, D008, D010, and D011 are treated in compliance with the applicable treatment standards specified for such wastes in this section.
(4) Radioactive hazardous mixed wastes are subject to the treatment standards in subdivision (a) of this section. Where treatment standards are specified for radioactive mixed wastes in the Table of Treatment Standards, those treatment standards will govern. Where there is no specific treatment standard for radioactive mixed waste, the treatment standard for the hazardous waste (as designated by EPA waste code) applies. Hazardous debris containing radioactive waste is subject to the treatment standards specified in subdivision (g) of this section.
Note:
Parts 380, 381, 382 and 383 of this Title may apply to final disposition of the treated radioactive hazardous mixed wastes or treated hazardous debris containing radioactive waste.
(d) Treatment standards expressed as waste concentrations.
For the requirements previously found in this subdivision and for treatment standards in Table CCW — Constituent Concentrations in Wastes, refer to subdivision (a) of this section.
(e) Variance from a treatment standard.
(1) Based on a petition filed by a generator or treater of hazardous waste with the EPA administrator, pursuant to 40 CFR section 268.44 and the commissioner, the commissioner may approve a variance from an applicable treatment standard if:
(i) it is not physically possible to treat the waste to the level specified in the treatment standard, or by the method specified as the treatment standard. To show that this is the case, the petitioner must demonstrate that because the physical or chemical properties of the waste differ significantly from waste analyzed in developing the treatment standard, the waste cannot be treated to the specified level or by the specified method; or
(ii) it is in appropriate to require the waste to be treated to the level specified in the treatment standard or by the method specified as the treatment standard, even though such treatment is technically possible. To show that this is the case, the petitioner must either demonstrate that:
(a) treatment to the specified level or by the specified method is technically inappropriate (for example, resulting in combustion of large amounts of mildly contaminated environmental media); or
(b) for remediation waste only, treatment to the specified level or by the specified method is environmentally inappropriate because it would likely discourage aggressive remediation;
(iii) the EPA administrator must also have approved the variance pursuant to 40 CFR section 268.44.
(2) Each petition must be submitted in accordance with the procedures in section 370.3(a) of this Title.
(3) Each petition must include the following statement signed by the petitioner or an authorized representative:
I certify under penalty of law that I have personally examined and am familiar with the information submitted in this petition and all attached documents, and that, based on my inquiry of those individuals immediately responsible for obtaining the information, I believe that the submitted information is true, accurate, and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment.
(4) After receiving a petition for variance from a treatment standard, the commissioner may request any additional information or samples which he may require to evaluate the petition. Additional copies of the complete petition may be requested as needed.
(5) The commissioner will give public notice in the New York State Register of the intent to approve or deny a petition and provide an opportunity for public comment. The final decision on a variance from a treatment standard will be published in the New York State Register.
(6) A generator, treatment facility, or disposal facility that is managing a waste covered by a variance from the treatment standards must comply with the waste analysis requirements for restricted wastes found under section 376.1(g) of this Part.
(7) During the petition review process, the applicant is required to comply with all restrictions on land disposal under this Part.
(8) Based on a petition filed by a generator or treater of hazardous waste with the EPA administrator, pursuant to 40 CFR section 268.44 and the commissioner, the commissioner or his or her delegated representative may approve a site-specific variance from an applicable treatment standard if:
(i) it is not physically possible to treat the waste to the level specified in the treatment standard, or by the method specified as the treatment standard. To show that this is the case, the petitioner must demonstrate that because the physical or chemical properties of the waste differ significantly from waste analyzed in developing the treatment standard, the waste cannot be treated to the specified level or by the specified method; or
(ii) it is inappropriate to require the waste to be treated to the level specified in the treatment standard or by the method specified as the treatment standard, even tough such treatment is technically possible. To show that this is the case, the petitioner must either demonstrate that:
(a) treatment to the specified level or by the specified methods is technically inappropriate (for example, resulting in combustion of large amounts of mildly contaminated environmental media where the treatment standard is not based on combustion of such media); or
(b) for remediation waste only, treatment to the specified level or by the specified method is environmentally inappropriate because it would likely discourage aggressive remediation;
(iii) for contaminated soil only, treatment to the level or by the method specified in the soil treatment standards would result in concentrations of hazardous constituents that are below (i.e., lower than) the concentrations necessary to minimize short- and long-term threats to human health and the environment. Treatment variances approved under this paragraph must:
(a) at a minimum, impose alternative land disposal restriction treatment standards that, using a reasonable maximum exposure scenario:
(1) for carcinogens, achieve constituent concentrations that result in the total excess risk to an individual exposed over a lifetime generally falling within the range from 10-4 to 10-6; and
(2) for constituents with non-carcinogenic effects, achieve constituent concentrations that an individual could be exposed to on a daily basis without appreciable risk of deleterious effect during a lifetime;
(b) not consider post-land-disposal controls;
(iv) for contaminated soil only, treatment to the level or by the method specified in the soil treatment standards would result in concentrations of hazardous constituents that are below (i.e., lower than) natural background concentrations at the site where the contaminated soil will land disposed;
(v) public notice and a reasonable opportunity for public comment must be provided before granting or denying a petition;
(vi) the EPA administrator must also have approved the variance pursuant to 40 CFR section 268.44.
(9) Each application for a site-specific variance from a treatment standard must include the information in section 370.3(a)(2) of this Title.
(10) After receiving an application for a site-specific variance from a treatment standard, the commissioner may request any additional information or samples which may be required to evaluate the application.
(11) A generator, treatment facility, or disposal facility that is managing a waste covered by a site-specific variance from a treatment standard must comply with the waste analysis requirements for restricted wastes found under section 376.1(g) of this Part.
(12) During the application review process, the applicant for a site-specific variance must comply with all restrictions on land disposal under this Part.
(13) For all variances, the petitioner must also demonstrate that compliance with any given treatment variance is sufficient to minimize threats to human health and the environment posed by land disposal of the waste. In evaluating this demonstration, the State may take into account whether a treatment variance should be approved if the subject waste is to be used in a manner constituting disposal pursuant to section 374-1.3 of this Title.
(f) PCB disposal.
(1) PCB wastes regulated as hazardous waste by New York State solely due to the presence of PCBs pursuant to section 371.4(e) of this Title, shall be disposed of in accordance with the provisions of 40 CFR part 761, (as incorporated by reference in section 370.1(e) of this Title), except:
(i) As listed in Part 371, waste B002, from any source other than a spill, may not be stabilized or mixed with any substance to conform with any provision of 40 CFR part 761 regarding land disposal.
(g) Treatment standards for hazardous debris.
(1) Treatment standards. Hazardous debris must be treated, as follows, prior to land disposal, unless DEC determines under section 371.1(d)(5)(ii) of this Title that the debris is no longer contaminated with hazardous waste, or that the debris is treated to the waste-specific treatment standard provided in this section for the waste contaminating the debris.
(i) General. Hazardous debris must be treated for each contaminant subject to treatment defined by paragraph (2) of this subdivision using the technology or technologies identified in Table 1 of this subdivision.
(ii) Characteristic debris. Hazardous debris that exhibits the characteristic of ignitability, corrosivity, or reactivity identified under section 371.3(b), (c), and (d) of this Title, respectively, must be deactivated by treatment using one of the technologies identified in Table 1 of this subdivision.
(iii) Mixtures of debris types. The treatment standards of Table 1 in this subdivision must be achieved for each type of debris contained in a mixture of debris types. If an immobilization technology is used in a treatment train, it must be the last treatment technology used.
(iv) Mixtures of contaminant types. Debris that is contaminated with two or more contaminants subject to treatment identified under paragraph (2) of this subdivision must be treated for each contaminant using one or more applicable treatment technologies identified in Table 1 of this subdivision. If an immobilization technology is used in a treatment train, it must be the last treatment technology used.
(v) PCBs. Hazardous debris that is also a hazardous PCB under Part 371 of this Title or a waste PCB under 40 CFR part 761 (see section 370.1[e] of this Title), is subject to the requirements of subdivision (f) of this section, 40 CFR part 761 (see section 370.1[e] of this Title), or the requirements of this subdivision, whichever are more stringent.
(2) Contaminants subject to treatment. Hazardous debris must be treated for each contaminant subject to treatment. The contaminants subject to treatment must be determined as follows:
(i) Toxicity characteristic debris. The contaminants subject to treatment for debris that exhibits the toxicity characteristic (TC) by section 371.3(e) of this Title are those EP constituents for which the debris exhibits the TC toxicity characteristic.
(ii) Debris contaminated with listed waste. The contaminants subject to treatment for debris that is contaminated with a prohibited listed hazardous waste are those constituents or wastes for which treatment standards are established for the waste under subdivision (a) of this section.
(iii) Cyanide reactive debris. Hazardous debris that is reactive due to the presence of cyanide must be treated for cyanide.
(3) Conditioned exclusion of treated debris. Hazardous debris which has been treated using one of the specified extraction or destruction technologies in Table 1 of this subdivision and which does not exhibit a characteristic of hazardous waste identified under section 371.3 of this Title after treatment is not a hazardous waste and need not be managed in a Part 373 facility. Hazardous debris contaminated with a listed waste that is treated by an immobilization technology specified in Table 1 is a hazardous waste and must be managed in a Part 373 facility.
(4) Treatment residuals:
(i) General requirements. Except as provided by subparagraphs (ii) and (iv) of this paragraph:
(a) residue from the treatment of hazardous debris must be separated from the treated debris using simple physical or mechanical means; and
(b) residue from the treatment of hazardous debris is subject to the waste-specific treatment standards provided by this section for the waste contaminating the debris.
(ii) Nontoxic debris. Residue from the deactivation of ignitable, corrosive, or reactive characteristic hazardous debris (other than cyanide-reactive) that is not contaminated with a contaminant subject to treatment defined by paragraph (2) of this subdivision, must be deactivated prior to land disposal and is not subject to the waste-specific treatment standards of this section.
(iii) Cyanide-reactive debris. Residue from the treatment of debris that is reactive due to presence of cyanide must meet the treatment standards for D003 in "Treatment Standards for Hazardous Wastes" in subdivision (a) of this section.
(iv) Ignitable nonwastewater residue. Ignitable nonwastewater residue containing equal to or greater than 10 percent total organic carbon is subject to the technology specified in the treatment standard for D001: Ignitable Liquids in "Treatment Standards for Hazardous Wastes" in subdivision (a) of this section.
(v) Residue from spalling. Layers of debris removed by spalling are hazardous debris that remain subject to the treatment standards of this section.
Table 1.-Alternative Treatment Standards For Hazardous Debris1
| 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 surf ace.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 (½ inch) in one dimension (i.e., thickness limit,5 except that this thickness limit may be waived under an "Equivalent Technology" approval under 376.4(c)(2);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 376.4(c)(2) must be obtained8. | |
| 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 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 vapor4. | 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:5Obtain an "Equivalent Technology" approval under 376.4(c)(2)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 gas7. | All Debris: Obtain an "Equivalent Technology" approval under 376.4(c)(2);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. | 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 anaerobic conditions. | All Debris: Obtain an "Equivalent Technology" approval under 376.4(c)(2);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 standards for organic compounds in the waste contaminating the debris. | All Debris: Metal contaminants. |
| Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (½ inch) in one dimension (i.e., thickness limit),5 except that this thickness limit may be waived under the "Equivalent Technology" approval. | ||
| 2. Chemical Destruction | ||
| a. Chemical Oxidation: Chemical or electrolytic 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) permanganates; and/or (9) other oxidizing reagents of equivalent destruction efficiency.4Chemical oxidation specifically includes what is referred to as alkaline chlorination. | ||
| All Debris: Obtain an "Equivalent Technology" approval under 376.4(c)(2);8 treated debris must be separated from treatment residuals using simple physical or mechanical means,9and, prior to further treatment, such residue must meet the waste- specific treatment standards for organic compounds in the waste contaminating the debris. | All Debris: Metal contaminants. | |
| Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (½ inch) in one dimension (i.e., thickness limit),5 except that this thickness limit may be waived under the "Equivalent Technology" approval. | ||
| 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. | Same as above. | Same as above. |
| 3. Thermal Destruction: Treatment in an incinerator operating in accordance with sections 373-2.15 and 373-3.15 of this Title; a boiler or industrial furnace operating in accordance with section 374-1.8 of this Title, or other thermal treatment unit operated in accordance with section 373-2.24 of this Title, or section 373-3.16 of this Title, 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,9and, 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.6Obtain an "Equivalent Technology" approval under 376.4(c)(2),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 with 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 constituents5. | 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 with which it may come into contact after placement (leachate, other waste, microbes). | None. |
1 Hazardous 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.
2 Contaminant 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 Title 9, Article 27 (ECL) 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.
4 Acids, 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.
5 If 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.
6 Dioxin-listed wastes are EPA Hazardous Waste numbers F020, F021, F022, F023, F026, and F027.
7 Thermal 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 section 376.4(c)(2) 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.
(h) Alternative treatment standards based on HTMR. For the treatment standards previously found in this subdivision, refer to subdivision (a) of this section.
(i) [Reserved]
(j) Universal treatment standards. Table UTS identifies the hazardous constituents, along with the nonwastewater and wastewater treatment standard levels, that are used to regulate most prohibited hazardous wastes with numerical limits. For determining compliance with treatment standards for underlying hazardous constituents as defined in section 376.1(b)(1)(xii) of this Part, these treatment standards may not be exceeded. Compliance with these treatment standards is measured by an analysis of grab samples, unless otherwise noted in the following Table UTS.
Table-UTS-Universal Treatment Standards
| Note: NA means not applicable. | |||
|---|---|---|---|
| Regulated Constituent-common name | CAS1 | Wastewater standard. Concentration2 in mg/l | Nonwastewater standard. Concentration3 in mg/kg unless noted as “mg/l TCLP” |
| 1. 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 |
| 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 |
| 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 |
| Butyl benzyl phthalate | 85-68-7 | 0.017 | 28 |
| 2-sec-Butyl-4, 6-dinitrophenol/Dinoseb | 88-85-7 | 0.066 | 2.5 |
| Carbon disulfide | 75-15-0 | 3.8 | 4.8 mg/l TCLP |
| Carbon tetrachloride | 56-23-5 | 0.057 | 6.0 |
| 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 |
| 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 |
| 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 |
| 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 |
| Heptachlor | 76-44-8 | 0.0012 | 0.066 |
| Heptachlor epoxide | 1024-57-3 | 0.016 | 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 |
| 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 Hexachlorodibenzo-furans) | 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 | 0.75mg/l TCLP |
| Methapyrilene | 91-80-5 | 0.081 | 1.5 |
| 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 |
| 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 |
| 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 |
| Pentachlorobenzene | 608-93-5 | 0.055 | 10 |
| PeCDDs (All Pentachlorodibenzo-p- dioxins) | NA | 0.000063 | 0.001 |
| PeCDFs (All Pentachlorodibenzo-furans) | 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 |
| Phenol | 108-95-2 | 0.039 | 6.2 |
| 1,3-Phenylenediamine | 108-45-2 | 0.010 | 0.66 |
| Phorate | 298-02-2 | 0.021 | 4.6 |
| Phthalic acid | 100-21-0 | 0.055 | 28 |
| Phthalic anhydride | 85-44-9 | 0.055 | 28 |
| Pronamide | 23950-58-5 | 0.093 | 1.5 |
| 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 Tetrachlorodi-benzo-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 |
| Toluene | 108-88-3 | 0.080 | 10 |
| Toxaphene | 8001-35-2 | 0.0095 | 2.6 |
| 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 |
| tris-(2,3-Dibromopropyl) phosphate | 126-72-7 | 0.11 | 0.10 |
| 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 |
| Selenium | 7782-49-2 | 0.82 | 5.7 mg/l TCLP |
| Silver | 7440-22-4 | 0.43 | 0.14 mg/l TCLP |
| Sulfide | 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 |
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 section 373-2.15 or 373-3.15 of this Title, 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 paragraph (a)(4) of this section. 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 section 370.1(e) of this Title, 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 in section 376.1(b)(1)(xii) of this Part.
6[Reserved]
7 This constituent is not an underlying hazardous constituent as defined at section 376.1(b) of this Part 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.
(k) Alternative LDR treatment standards for contaminated soil.
(1) 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 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 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 LDRs |
* For dates of LDR applicability, see 40 CFR part 268 Appendix VII, as incorporated by reference in section 370.1(e) of this Title. 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.
(2) Prior to land disposal, contaminated soil identified by paragraph (1) of this subdivision as needing to comply with LDRs must be treated according to the applicable treatment standards specified in paragraph (3) of this subdivision or according to the Universal Treatment Standards specified in subdivision (j) of this section 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 (3) of this subdivision and the Universal Treatment Standards may be modified through a treatment variance approved in accordance with subdivision (e) of this section.
(3) Treatment standards for contaminated soils. Prior to land disposal, contaminated soil identified by paragraph (1) of this subdivision 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 subdivision (j) of this section.
(i) All soils. Prior to land disposal, all constituents subject to treatment must be treated as follows:
(a) For nonmetals except carbon disulfide, cyclohexanone, and methanol, treatment must achieve 90 percent reduction in total constituent concentrations, except as provided by clause (3)(i)(c) of this paragraph.
(b) For metals and carbon disulfide, cycolohexanone, and methanol, treatment must achieve 90 percent reduction in constituent concentrations as measured in leachate from the treated media (tested according to the TCLP) or 90 percent reduction in total constituent concentrations (when a metal removal treatment technology is used), except as provided by clause (3)(i)(c) of this paragraph.
(c) When treatment of any constituent subject to treatment to a 90 percent reduction standard would result in a concentration less than 10 times the Universal Treatment Standard for that constituent, treatment to achieve constituent concentrations less than 10 times the Universal Treatment Standard is not required. Universal Treatment Standards are identified in subdivision (j) of this section, Table UTS.
(ii) Soils that exhibit the characteristic of ignitability, corrosivity or reactivity. In addition to the treatment required by subparagraph (i) of this paragraph, prior to land disposal, soils that exhibit the characteristic of ignitability, corrosivity, or reactivity must be treated to eliminate these characteristics.
(iii) Soils that contain nonanalyzable constituents. In addition to the treatment requirements of subparagraphs (i) and (ii) of this paragraph, prior to land disposal, the following treatment is required for soils that contain nonanalyzable constituents:
(a) for soil that contains only analyzable and nonanalyzable organic constituents, treatment of the analyzable organic constituents to the levels specified in subparagraphs (i) and (ii) of this paragraph; or
(b) for soil that contains only nonanalyzable constituents, treatment by the method(s) specified in subdivision (c) of this section for the waste contained in the soil.
(4) Constituents subject to treatment. When applying the soil treatment standards in paragraph (3) of this subdivision, constituents subject to treatment are any constituents listed in subdivision (j) of this section, Table UTS—Universal Treatment Standards that are reasonably expected to be present in any given volume of contaminated soil, except fluoride, selenium, sulfides, vanadium and zinc, and are present at concentrations greater than 10 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.
(5) Management of treatment residuals. Treatment residuals from treating contaminated soil identified by paragraph (1) of this subdivision as needing to comply with LDRs must be managed as follows:
(i) soil residuals are subject to the treatment standards of this subdivision;
(ii) non-soil residuals are subject to:
(a) for soils contaminated by listed hazardous waste, the hazardous waste management standards applicable to the listed hazardous waste; and
(b) for soils that exhibit a characteristic of hazardous waste, if the nonsoil residual also exhibits a characteristic of hazardous waste, the treatment standards applicable to the characteristic hazardous waste.
6 CRR-NY 376.4
Current through February 28, 2023
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