Chapter 3745-270 Hazardous Wastes Restricted from Land Disposal
3745-270-01
Purpose, scope, and applicability - land disposal restrictions.
(A) Chapter 3745-270 of the Administrative Code identifies hazardous wastes that are restricted from land disposal and defines those limited circumstances under which an otherwise prohibited waste may continue to be land disposed.
(B) Except as specifically provided otherwise in Chapter 3745-270 or 3745-51 of the Administrative Code, the requirements of Chapter 3745-270 of the Administrative Code apply to persons who generate or transport hazardous waste and owners and operators of hazardous waste treatment, storage, and disposal facilities.
(C) Restricted wastes may continue to be land disposed as follows:
(1) Where persons have been granted an extension to the effective date of a prohibition under rules 3745-270-20 to 3745-270-39 of the Administrative Code, or pursuant to rule 3745-270-05 of the Administrative Code, with respect to those wastes covered by the extension;
(2) Where persons have been granted an exemption from a prohibition pursuant to a petition under rule 3745-270-06 of the Administrative Code, with respect to those wastes and units covered by the exemption;
(3) Wastes that are hazardous only because they exhibit a hazardous characteristic, and which are otherwise prohibited from land disposal under Chapter 3745-270 of the Administrative Code, or 40 CFR Part 148, are not prohibited from land disposal if the wastes:
(a) Are disposed into a nonhazardous or hazardous injection well as described in 40 CFR 144.6(a); and
(b) Do not exhibit any prohibited characteristic of hazardous waste identified in rules 3745-51-20 to 3745-51-24 of the Administrative Code at the point of injection.
(4) Wastes that are hazardous only because they exhibit a hazardous characteristic, and which are otherwise prohibited by Chapter 3745-270 of the Administrative Code, are not prohibited if the wastes meet any of the following criteria, unless the wastes are subject to a specified method of treatment other than DEACT in rule 3745-270-40 of the Administrative Code, or are D003 reactive cyanide:
(a) The wastes are managed in a treatment system which subsequently discharges to waters of the United States pursuant to a permit issued under Section 402 of the Clean Water Act (CWA); or
(b) The wastes are treated for the purposes of the pretreatment requirements of Section 307 of the CWA; or
(c) The wastes are managed in a zero discharge system engaged in "CWA-equivalent treatment" as defined in paragraph (A) of rule 3745-270-37 of the Administrative Code; and
(d) The wastes no longer exhibit a prohibited characteristic at the point of land disposal (i.e., placement in a surface impoundment).
(D) The requirements of Chapter 3745-270 of the Administrative Code do not affect the availability of a waiver under Section 121(d)(4) of the Comprehensive Environmental Response, Compensation, and Liability Act of 1980, 42 U.S.C. 9601 et seq. (CERCLA).
(E) The following hazardous wastes are not subject to any provision of Chapter 3745-270 of the Administrative Code:
(1) Waste generated by small quantity generators of less than one hundred kilograms of non-acute hazardous waste per month or less than one kilogram of acute hazardous waste per month, as described in rule 3745-51-05 of the Administrative Code;
(2) Waste pesticides that a farmer disposes of pursuant to rule 3745-52-70 of the Administrative Code;
(3) Wastes identified or listed as hazardous after November 8, 1984 for which Ohio EPA has not promulgated land disposal prohibitions or treatment standards;
(4) De minimis losses of characteristic wastes to wastewaters are not considered to be prohibited wastes and are defined as losses from normal material handling operations (e.g. spills from the unloading or transfer of materials from bins or other containers; leaks from pipes, valves, or other devices used to transfer materials); minor leaks of process equipment, storage tanks, or containers; leaks from well-maintained pump packings and seals; sample purgings; and relief device discharges; discharges from safety showers and rinsing and cleaning of personal safety equipment; rinsate from empty containers or from containers that are rendered empty by that rinsing; and laboratory wastes not exceeding one per cent of the total flow of wastewater into the facility's headworks on an annual basis, or with a combined annualized average concentration not exceeding one part per million in the headworks of the facility's wastewater treatment or pretreatment facility.
(F) "Universal waste handlers" and "universal waste transporters" (as defined in rule 3745-50-10 of the Administrative Code) are exempt from rules 3745-270-07 and 3745-270-50 of the Administrative Code for the wastes listed in paragraphs (F)(1) to (F)(4) of this rule. These handlers and transporters are subject to regulation under Chapter 3745-273 of the Administrative Code when handling the following universal wastes:
(1) Batteries as described in rule 3745-273-02 of the Administrative Code;
(2) Pesticides as described in rule 3745-273-03 of the Administrative Code;
(3) Mercury-containing equipment as described in rule 3745-273-04 of the Administrative Code; and
(4) Lamps as described in rule 3745-273-05 of the Administrative Code.
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled "Incorporated by reference."]
Effective:
03/17/2012
R.C.
119.032 review dates: Exempt
Promulgated Under:
119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/30/1989, 02/11/1992, 09/02/1997, 12/07/2000, 12/07/2004,
02/16/2009, 09/05/2010
3745-270-02
Definitions pertaining to land disposal restrictions.
(A) When used in Chapter 3745-270 of the Administrative Code, the following terms have the meanings given in this rule:
(1) "Debris" means:
(a) Solid material exceeding a 60.0 millimeter particle size that is intended for disposal and that is:
(i) A manufactured object; or
(ii) Plant or animal matter; or
(iii) Natural geologic material.
(b) However, the following materials are not debris:
(i) Any material for which a specific treatment standard is provided in rules 3745-270-40 to 3745-270-49 of the Administrative Code, namely lead acid batteries, cadmium batteries, and radioactive lead solids;
(ii) Process residuals such as smelter slag and residues from the treatment of waste, wastewater, sludges, or air emission residues; and
(iii) Intact containers of hazardous waste that are not ruptured and that retain at least seventy-five per cent of their original volume.
(c) A mixture of debris that has not been treated to the standards provided by rule 3745-270-45 of the Administrative Code and other material is subject to regulation as debris if the mixture is comprised primarily of debris, by volume, based on visual inspection.
(2) "Hazardous constituent" or "hazardous constitutents" means those constituents in the appendix to rule 3745-51-11 of the Administrative Code.
(3) "Hazardous debris" means debris that contains a hazardous waste listed in rules 3745-51-30 to 3745-51-35 of the Administrative Code, or that exhibits a characteristic of hazardous waste identified in rules 3745-51-20 to 3745-51-24 of the Administrative Code. Any deliberate mixing of prohibited hazardous waste with debris that changes its treatment classification (i.e., from waste to hazardous debris) is not allowed under the dilution prohibition in rule 3745-270-03 of the Administrative Code.
(4) "Inorganic metal-bearing waste" is one for which Ohio EPA has established treatment standards for metal hazardous constituents, and which does not otherwise contain significant organic or cyanide content as described in paragraph (C)(1) of rule 3745-270-03 of the Administrative Code, and is specifically listed in the appendix to rule 3745-270-03 of the Administrative Code.
(5) "Land disposal" means placement in or on the land, except in a corrective action management unit or a staging pile, and includes, but is not limited to, placement in a landfill, surface impoundment, waste pile, injection well, land treatment facility, salt dome formation, salt bed formation, underground mine or cave, or placement in a concrete vault, or bunker intended for disposal purposes.
(6) "Nonwastewaters" are wastes that do not meet the criteria for "wastewaters" as defined in this rule.
(7) "Polychlorinated biphenyls" or "PCBs" are halogenated organic compounds defined in accordance with 40 CFR 761.3.
(8) "Soil" means unconsolidated earth material composing the superficial geologic strata (material overlying bedrock), consisting of clay, silt, sand, or gravel size particles as classified by the U.S. natural resources conservation service, or a mixture of such materials with liquids, sludges, or solids which is inseparable by simple mechanical removal processes, and is made up primarily of soil by volume based on visual inspection. Any deliberate mixing of prohibited hazardous waste with soil that changes its treatment classification (i.e., from waste to contaminated soil) is not allowed under the dilution prohibition in rule 3745-270-03 of the Administrative Code.
(9) "Underlying hazardous constituent" means any constituent listed in the table in rule 3745-270-48 of the Administrative Code, except fluoride, selenium, sulfides, vanadium, and zinc, which can reasonably be expected to be present at the point of generation of the hazardous waste at a concentration above the constituent-specific universal treatment standards.
(10) "Wastewaters" are wastes that contain less than one per cent by weight total organic carbon and less than one per cent by weight total suspended solids .
(B) All other terms have the meanings given in rule 3745-50-10, 3745-51-02, or 3745-51-03 of the Administrative Code.
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled "Incorporated by reference."]
Effective:
03/17/2012
R.C.
119.032 review dates: Exempt
Promulgated Under:
119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/30/1989, 02/11/1992, 12/07/2000, 12/07/2004
3745-270-03
Dilution prohibited as a substitute for treatment.
(A) Except as provided in paragraph (B) of this rule, no generator, transporter, handler, or owner or operator of a treatment, storage, or disposal facility must in any way dilute a restricted waste or the residual from treatment of a restricted waste as a substitute for adequate treatment to achieve compliance with rules 3745-270-40 to 3745-270-49 of the Administrative Code, to circumvent the effective date of a prohibition in rules 3745-270-20 to 3745-270-39 of the Administrative Code, to otherwise avoid a prohibition in rules 3745-270-20 to 3745-270-39 of the Administrative Code, or to circumvent a land disposal prohibition imposed by Section 3004 of RCRA .
(B) Dilution of wastes that are hazardous only because they exhibit a characteristic in treatment systems which include land-based units which treat wastes subsequently discharged to a water of the United States pursuant to a permit issued under Section 402 of the Clean Water Act (CWA), or which treat wastes in a CWA-equivalent treatment system, or which treat wastes for purposes of pretreatment requirements under Section 307 of the CWA is not impermissible dilution for purposes of this rule unless a method other than DEACT has been specified in rule 3745-270-40 of the Administrative Code as the treatment standard, or unless the waste is a D003 reactive cyanide wastewater or nonwastewater.
(C) Combustion of the EPA hazardous waste numbers listed in the appendix to this rule is prohibited, unless the waste, at the point of generation, or after any bona fide treatment such as cyanide destruction prior to combustion, can be demonstrated to comply with one or more of the following criteria (unless otherwise specifically prohibited from combustion):
(1) The waste contains hazardous organic constituents or cyanide at levels exceeding the constituent-specific treatment standard in rule 3745-270-48 of the Administrative Code;
(2) The waste consists of organic, debris-like materials (e.g., wood, paper, plastic, or cloth) contaminated with an inorganic metal-bearing hazardous waste;
(3) The waste, at point of generation, has reasonable heating value such as greater than or equal to five thousand British thermal units (Btu) per pound;
(4) The waste is co-generated with wastes for which combustion is a required method of treatment;
(5) The waste is subject to federal and/or state requirements necessitating reduction of organics (including biological agents); or
(6) The waste contains greater than one per cent total organic carbon.
(D) It is a form of impermissible dilution, and therefore prohibited, to add iron filings or other metallic forms of iron to lead-containing hazardous wastes in order to achieve any land disposal restriction treatment standard for lead. Lead-containing wastes include D008 wastes (wastes exhibiting a characteristic due to the presence of lead), all characteristic wastes containing lead as an underlying hazardous constituent, listed wastes containing lead as a regulated constituent, and hazardous media containing any of the aforementioned lead-containing wastes.
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled "Incorporated by reference."]
Effective:
03/17/2012
R.C.
119.032 review dates: Exempt
Promulgated Under:
119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/30/1989, 02/11/1992, 12/07/2000, 12/07/2004
3745-270-04
Treatment surface impoundment exemption.
(A) Wastes which are otherwise prohibited from land disposal under Chapter 3745-270 of the Administrative Code may be treated in a surface impoundment or series of impoundments provided that:
(1) Treatment of such wastes occurs in the impoundments;
(2) The following conditions are met:
(a) Sampling and testing. For wastes with treatment standards in rules 3745-270-40 to 3745-270-49 of the Administrative Code and/or prohibition levels in rules 3745-270-20 to 3745-270-39 of the Administrative Code or Section 3004(d) of RCRA, the residues from treatment are analyzed, as specified in rule 3745-270-07 of the Administrative Code, to determine if they meet the applicable treatment standards or where no treatment standards have been established for the waste, the applicable prohibition levels. The sampling method, specified in the waste analysis plan under rule 3745-54-13 or 3745-65-13 of the Administrative Code, must be designed such that representative samples of the sludge and the supernatant are tested separately rather than mixed to form homogeneous samples.
(b) Removal. The following treatment residues (including any liquid waste) must be removed at least annually: residues which do not meet the treatment standards promulgated under rules 3745-270-40 to 3745-270-49 of the Administrative Code; residues which do not meet the prohibition levels established under rules 3745-270-20 to 3745-270-39 of the Administrative Code or imposed by statute (where no treatment standards have been established); residues which are from the treatment of wastes prohibited from land disposal under rules 3745-270-20 to 3745-270-39 of the Administrative Code (where no treatment standards have been established and no prohibition levels apply); or residues from managing listed wastes which are not delisted under 40 CFR 260.22. If the volume of liquid flowing through the impoundment or series of impoundments annually is greater than the volume of the impoundment or impoundments, this flow-through constitutes removal of the supernatant for the purpose of this requirement.
(c) Subsequent management. Treatment residues may not be placed in any other surface impoundment for subsequent management.
(d) Recordkeeping. Sampling and testing and recordkeeping provisions of rules 3745-54-13 and 3745-65-13 of the Administrative Code apply.
(3) The impoundment meets the design requirements in paragraph (C) of rule 3745-56-21 or paragraph (A) of 3745-67-21 of the Administrative Code, regardless that the unit may not be new, expanded, or a replacement, and be in compliance with applicable ground water monitoring requirements of rules 3745-54-90 to 3745-54-101 or 3745-65-90 to 3745-65-94 of the Administrative Code unless:
(a) Exempted pursuant to paragraph (D) or (E) of rule 3745-56-21, or paragraph (C) or (D) of rule 3745-67-21 of the Administrative Code; or,
(b) Upon application by the owner or operator, the director, after notice and an opportunity to comment, has granted a waiver of the requirements on the basis that the surface impoundment:
(i) Has at least one liner, for which there is no evidence that such liner is leaking;
(ii) Is located more than one-quarter mile from an underground source of drinking water; and
(iii) Is in compliance with generally applicable ground water monitoring requirements for facilities with permits; or
(c) Upon application by the owner or operator, the director, after notice and an opportunity to comment, has granted a modification to the requirements on the basis of a demonstration that the surface impoundment is located, designed, and operated so as to assure that there will be no migration of any hazardous constituent into ground water or surface water at any future time.
(4) The owner or operator submits to the director a written certification that the requirements of paragraph (A)(3) of this rule have been met. The following certification is required:
"I certify under penalty of law that the requirements of paragraph (A)(3) of rule 3745-270-04 of the Administrative Code have been met for all surface impoundments being used to treat restricted wastes. 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."
(B) Evaporation of hazardous constituents as the principal means of treatment is not considered to be treatment for purposes of an exemption under this rule.
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled "Incorporated by reference."]
Effective:
03/17/2012
R.C.
119.032 review dates: Exempt
Promulgated Under:
119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/30/1989, 02/11/1992, 12/07/2000, 03/13/2002, 12/07/2004,
09/05/2010
3745-270-05
Procedures for case-by-case extensions to an effective date.
(A) Any person who generates, treats, stores, or disposes of a hazardous waste may seek an extension to any applicable restriction established under rules 3745-270-20 to 3745-270-39 of the Administrative Code by submitting an application to the administrator pursuant to 40 CFR 268.5.
(B) Ohio EPA will recognize the administrator's decision to grant or deny an application for an extension under 40 CFR 268.5.
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled "Incorporated by reference."]
Effective:
03/17/2012
R.C.
119.032 review dates:
11/30/2011 and
08/25/2016
Promulgated
Under: 119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/30/1989, 02/11/1992, 12/07/2000
(A) Any person seeking an exemption from a prohibition under rules 3745-270-20 to 3745-270-39 of the Administrative Code for the disposal of a restricted hazardous waste in a particular unit or units must submit a petition to the administrator pursuant to 40 CFR 268.6.
(B) Ohio EPA will recognize the administrator's decision to grant or deny a petition for an exemption under 40 CFR 268.6.
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled "Incorporated by reference."]
Effective:
03/17/2012
R.C.
119.032 review dates:
11/30/2011 and
08/25/2016
Promulgated
Under: 119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/30/1989, 02/11/1992, 12/07/2000, 03/13/2002
(A) Requirements for generators:
(1) A generator of a hazardous waste must determine if the waste has to be treated before it can be land disposed. This is done by determining if the hazardous waste meets the treatment standards in rule 3745-270-40, 3745-270-45, or 3745-270-49 of the Administrative Code. This determination can be made concurrently with the hazardous waste determination required in rule 3745-52-11 of the Administrative Code, in either of two ways: by testing the waste, or by using knowledge of the waste.
(a) If the generator tests the waste, testing would normally determine the total concentration of hazardous constituents, or the concentration of hazardous constituents in an extract of the waste obtained using test method 1311 in "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods," U.S. EPA publication SW-846, depending on whether the treatment standard for the waste is expressed as a total concentration or as concentration of hazardous constituent in the waste's extract. [Alternatively, the generator must send the waste to a permitted hazardous waste treatment facility, where the waste treatment facility must comply with the requirements of rule 3745-54-13 of the Administrative Code and paragraph (B) of this rule.]
(b) In addition, some hazardous waste must be treated by particular treatment methods before they can be land disposed, and some soils are contaminated with such hazardous wastes. These treatment standards are in rule 3745-270-40 of the Administrative Code, and are described in detail in the table in rule 3745-270-42 of the Administrative Code. These wastes, and soils contaminated with such wastes, do not need to be tested (however, if they are in a waste mixture, other wastes with concentration level treatment standards would have to be tested).
(c) If a generator determines that he is managing a waste, or soil contaminated with a waste, that displays a hazardous characteristic of ignitability, corrosivity, reactivity, or toxicity, he must comply with the special requirements of rule 3745-270-09 of the Administrative Code in addition to any applicable requirements in this rule.
(2) If the waste or contaminated soil does not meet the treatment standards, or if the generator chooses not to make the determination of whether his waste must be treated, with the initial shipment of waste to each treatment or storage facility, the generator must send a one-time written notice to each treatment or storage facility receiving the waste, and place a copy in the generator's files. The notice must include the information in column A of table 1 of this rule. (Alternatively, if the generator chooses not to make the determination of whether the waste must be treated, the notification must include the EPA hazardous waste numbers and manifest number of the first shipment and must state "This hazardous waste may or may not be subject to the LDR treatment standards. The treatment facility must make that determination.") No further notification is necessary until such time as the waste changes or the treatment or storage facility changes, in which case a new notification must be sent to the new treatment or storage facility and a copy must be placed in the generator's files.
(a) For contaminated soil, the following certification statement should be included, signed by an authorized representative:
"I certify under penalty of law that I personally have examined this contaminated soil and it [does/does not] contain listed hazardous waste and [does/does not] exhibit a characteristic of hazardous waste and requires treatment to meet the soil treatment standards as provided by paragraph (C) of rule 3745-270-49 of the Administrative Code."
(b) Reserved.
(3) If the waste or contaminated soil meets the treatment standard at the original point of generation:
(a) With the initial shipment of waste to each treatment, storage, or disposal facility, the generator must send a one-time written notice to each treatment, storage, or disposal facility receiving the waste, and place a copy in the generator's files. The notice must include the information in column B of table 1 of this rule and the following certification statement, signed by an authorized representative:
"I certify under penalty of law that I personally have examined and am familiar with the waste, through analysis and testing or through knowledge of the waste, to support this certification that the waste complies with the treatment standards specified in rules 3745-270-40 to 3745-270-49 of the Administrative Code. I believe that the information I submitted is true, accurate, and complete. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment."
(b) For contaminated soil, with the initial shipment of wastes to each treatment, storage, or disposal facility, the generator must send a one-time written notice to each facility receiving the waste, and place a copy in the generator's files. The notice must include the information in column B of table 1 of this rule.
(c) If the waste changes, the generator must send a new notice and certification to the receiving facility, and place a copy in their files. Generators of hazardous debris excluded from the definition of "hazardous waste" under paragraph (F) of rule 3745-51-03 of the Administrative Code are not subject to these requirements.
(4) For reporting, tracking, and recordkeeping when exceptions allow certain wastes or contaminated soil that do not meet the treatment standards to be land disposed. There are certain exemptions from the requirements that hazardous wastes or contaminated soil meet treatment standards before they can be land disposed. These include, but are not limited to case-by-case extensions under rule 3745-270-05 of the Administrative Code, disposal in a no-migration unit under rule 3745-270-06 of the Administrative Code, or a national capacity variance or case-by-case capacity variance under rules 3745-270-20 to 3745-270-39 of the Administrative Code. If a generator's waste is so exempt, then with the initial shipment of waste, the generator must send a one-time written notice to each land disposal facility receiving the waste. The notice must include the information in column C of table 1 of this rule. If the waste changes, the generator must send a new notice to the receiving facility, and place a copy in the generator's files.
| Table 1: Generator Paperwork Requirements | ||||
| Column A | Column B | Column C | Column D | |
| Required Information | 3745-270-07 (A)(2) | 3745-270-07 (A)(3) | 3745-270-07 (A)(4) | 3745-270-07 (A)(9) |
| 1. EPA hazardous waste numbers and manifest number of first shipment. | X | X | X | X |
| 2. Statement: This waste is not prohibited from land disposal. | X | |||
| 3. The waste is subject to the land disposal restrictions (LDRs) of Chapter 3745-270 of the Administrative Code. The constituents of concern for F001 to F005, and F039, and underlying hazardous constituents in characteristic wastes, unless the waste will be treated and monitored for all constituents. If all constituents will be treated and monitored, there is no need to put them all on the LDR notice. | X | X | ||
| 4. The notice must include the applicable wastewater/nonwastewate category (see the definitions of "wastewaters" and "nonwastewaters" in rule 3745-270-02 of the Administrative Code) and subdivisions made within an EPA hazardous waste number based on waste-specific criteria (such as D003 reactive cyanide). | X r | X | ||
| 5. Waste analysis data (when available). | X | X | X | |
| 6. Date the waste is subject to the prohibition. | X | |||
| 7. For hazardous debris, when treating with the alternate treatment technologies provided by rule 3745-270-45 of the Administrative Code: the contaminants subject to treatment, as described in paragraph (B) of rule 3745-270-45 of the Administrative Code; and an indication that these contaminants are being treated to comply with rule 3745-270-45 of the Administrative Code. | X | X | ||
| 8. For contaminated soil subject to LDRs as provided in paragraph (A) of rule 3745-270-49 of the Administrative Code, the constituents subject to treatment as described in paragraph (D) of rule 3745-270-49 of the Administrative Code, and the following statement: This contaminated soil [does/does not] contain listed hazardous waste and [does/does not] exhibit a characteristic of hazardous waste and [is subject to/complies with] the soil treatment standards as provided by paragraph (C) of rule 3745-270-49 of the Administrative Code or the universal treatment standards. | X | X | ||
| 9. A certification is needed (see applicable rule for exact wording). | X | X | ||
(5) If a generator is managing and treating prohibited waste or contaminated soil in tanks, containers, or containment buildings regulated under rule 3745-52-34 of the Administrative Code to meet applicable LDR treatment standards in rule 3745-270-40 of the Administrative Code, the generator must develop and follow a written waste analysis plan which describes the procedures he will carry out to comply with the treatment standards. (Generators treating hazardous debris under the alternate treatment standards of the table in rule 3745-270-45 of the Administrative Code, however, are not subject to this waste analysis requirement.) The plan must be kept on site in the generator's records, and the following requirements must be met:
(a) The waste analysis plan must be based on a detailed chemical and physical analysis of a representative sample of the prohibited waste(s) being treated, and contain all information necessary to treat the waste(s) in accordance with the requirements of Chapter 3745-270 of the Administrative Code, including the selected testing frequency.
(b) Such plan must be kept in the generator's on-site files and made available to inspectors.
(c) Wastes shipped off-site pursuant to paragraph (A)(5) of this rule must comply with the notification requirements of paragraph (A)(3) of this rule.
(6)
(a) If a generator determines that the waste or contaminated soil is restricted based solely on his knowledge of the waste, all supporting data used to make this determination must be retained on-site in the generator's files.
(b) If a generator determines that the waste is restricted based on testing this waste or an extract developed using the test method 1311 in "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods," U.S. EPA publication SW-846, and all waste analysis data must be retained on-site in the generator's files.
(7) If a generator determines that he is managing a prohibited waste that is excluded from the definition of "hazardous waste" or "waste," or is exempt from regulation as a hazardous waste under rules 3745-51-02 to 3745-51-06 of the Administrative Code subsequent to the point of generation [including deactivated characteristic hazardous wastes managed in wastewater treatment systems subject to the Clean Water Act (CWA) as specified in paragraph (A)(2) of rule 3745-51-04 of the Administrative Code, or are CWA-equivalent, or are managed in an underground injection well regulated by the Safe Drinking Water Act], he must place in the generator's files a one-time notice describing such generation, subsequent exclusion from the definition of "hazardous waste" or "waste" or exemption from regulation as a hazardous waste, and the disposition of the waste.
(8) Generators must retain on-site a copy of all notices, certifications, waste analysis data, and other documentation produced pursuant to this rule for at least three years from the date that the waste that is the subject of such documentation was last sent to on-site or off-site treatment, storage, or disposal. The three year record retention period is automatically extended during the course of any unresolved enforcement action regarding the regulated activity or as requested by the director. The requirements of this paragraph apply to the wastes even when the hazardous characteristic is removed prior to disposal, when the waste is excluded from the definition of "hazardous waste" or "waste" under rules 3745-51-02 to 3745-51-06 of the Administrative Code, or when the waste is exempted from regulation as a hazardous waste, subsequent to the point of generation.
(9) If a generator is managing a lab pack containing hazardous wastes and wishes to use the alternative treatment standard for lab packs in paragraph (C) of rule 3745-270-42 of the Administrative Code:
(a) With the initial shipment of waste to a treatment facility, the generator must submit a notice that provides the information in column D of table 1 of this rule, and the following certification. The certification, which must be signed by an authorized representative and must be placed in the generator's files, must say the following:
"I certify under penalty of law that I personally have examined and am familiar with the waste, and that the lab pack contains only wastes that have not been excluded under appendix I to rule 3745-270-42 of the Administrative Code, and that this lab pack will be sent to a combustion facility in compliance with the alternative treatment standards for lab packs in paragraph (C) of rule 3745-270-42 of the Administrative Code. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment."
(b) No further notification is necessary until such time that the wastes in the lab pack change or the receiving facility changes, in which case a new notice and certification must be sent to the new receiving facility and a copy placed in the generator's files.
(c) If the lab pack contains characteristic hazardous wastes (D001 to D043),"underlying hazardous constituents" (as defined in rule 3745-270-02 of the Administrative Code ) need not be determined.
(d) The generator must comply with the requirements in paragraphs (A)(6) and (A)(7) of this rule.
(10) Small quantity generators with tolling agreements pursuant to paragraph (F) of rule 3745-52-20 of the Administrative Code must comply with the applicable notification and certification requirements of paragraph (A) of this rule for the initial shipment of the waste subject to the agreement. Such generators must retain on-site a copy of the notification and certification, together with the tolling agreement, for at least three years after termination or expiration of the agreement. The three-year record retention period is automatically extended during the course of any unresolved enforcement action regarding the regulated activity or as requested by the director.
(B) Treatment facilities must test their wastes according to the frequency specified in their waste analysis plans as required by rule 3745-54-13 or 3745-65-13 of the Administrative Code. Such testing must be performed as provided in paragraphs (B)(1), (B)(2), and (B)(3) of this rule.
(1) For wastes or contaminated soil with treatment standards expressed as concentrations in the waste extract (TCLP), the owner or operator of the treatment facility must test an extract of the treatment residues, using test method 1311 in "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods," U.S. EPA publication SW-846, to assure that the treatment residues extract meet the applicable treatment standards in Chapter 3745-270 of the Administrative Code.
(2) For wastes or contaminated soil with treatment standards expressed as concentrations in the waste, the owner or operator of the treatment facility must test the treatment residues (not an extract of such residues) to assure that they meet the applicable treatment standards in Chapter 3745-270 of the Administrative Code.
(3) A one-time notice must be sent with the initial shipment of waste or contaminated soil to the land disposal facility. A copy of the notice must be placed in the treatment facility's file.
(a) No further notification is necessary until such time that the waste changes or the receiving facility changes, in which case a new notice must be sent to the new receiving facility and a copy placed in the treatment facility's files.
(b) The one-time notice must include the requirements in table 2 of this rule:
| Table 2: Treatment Facility Paperwork Requirements | |
| Required information | 3745-270-07(B) |
| 1. EPA hazardous waste numbers and manifest number of first shipment | X |
| 2. The waste is subject to the LDRs of Chapter 3745-270 of the Administrative Code. The constituents of concern for F001 to F005 and F039, and underlying hazardous constituents in characteristic wastes, unless the waste will be treated and monitored for all constituents. If all constituents will be treated and monitored, there is no need to put them all on the LDR notice. | X |
| 3. The notice must include the applicable wastewater/nonwastewater category [see the definitions of "wastewaters" and "nonwastewaters" in of rule 3745-270-02 of the Administrative Code and subdivisions made within an EPA hazardous waste number based on waste-specific criteria (such as D003 reactive cyanide)]. | |
| 4. Waste analysis data (when available) | X |
| 5. For contaminated soil subject to LDRs as provided in paragraph (A) of rule 3745-270-49 of the Administrative Code, the constituents subject to treatment as described in paragraph (D) of rule 3745-270-49 of the Administrative Code, and the following statement: "This contaminated soil [does/does not] contain listed hazardous waste and [does/does not] exhibit a characteristic of hazardous waste and [is subject to/complies with] the soil treatment standards as provided by paragraph (C) of rule 3745-270-49 of the Administrative Code." | X |
| 6. A certification is needed (see applicable rule for exact wording) | X |
(4) The treatment facility must submit a one-time certification signed by an authorized representative with the initial shipment of waste or treatment residue of a restricted waste to the land disposal facility. The certification must state:
"I certify under penalty of law that I have personally examined and am familiar with the treatment technology and operation of the treatment process used to support this certification. Based on my inquiry of those individuals immediately responsible for obtaining this information, I believe that the treatment process has been operated and maintained properly so as to comply with the treatment standards specified in rule 3745-270-40 of the Administrative Code without impermissible dilution of the prohibited wastes. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment."
A certification is also necessary for contaminated soil, and it must state:
"I certify under penalty of law that I personally have examined and am familiar with the treatment technology and operation of the treatment process used to support this certification and believe that it has been maintained and operated properly so as to comply with treatment standards specified in rule 3745-270-49 of the Administrative Code without impermissible dilution of the prohibited wastes. I am aware there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment."
(a) A copy of the certification must be placed in the treatment facility's on-site files. If the waste or treatment residue changes or if the receiving facility changes, a new certification must be sent to the receiving facility, and a copy placed in the file.
(b) Debris excluded from the definition of "hazardous waste" under paragraph (F) of rule 3745-51-03 of the Administrative Code (i.e., debris treated by an extraction or destruction technology provided in the table in rule 3745-270-45 of the Administrative Code, and debris that the director has determined does not contain hazardous waste), however, is subject to the notification and certification requirements of paragraphs (D) to (D)(3) of this rule rather than the certification requirements of paragraphs (B)(4) to (B)(4)(e) of this rule.
(c) For wastes with organic constituents having treatment standards expressed as concentration levels, if compliance with the treatment standards is based in whole or in part on the analytical detection limit alternative specified in paragraph (D) of rule 3745-270-40 of the Administrative Code, the certification, signed by an authorized representative, must state the following:
"I certify under penalty of law that I have personally examined and am familiar with the treatment technology and operation of the treatment process used to support this certification. Based on my inquiry of those individuals immediately responsible for obtaining this information, I believe that the nonwastewater organic constituents have been treated by combustion units as specified in the table in rule 3745-270-42 of the Administrative Code. I have been unable to detect the nonwastewater organic constituents, despite having used best good-faith efforts to analyze for such constituents. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment."
(d) For characteristic wastes that are subject to the treatment standards in rule 3745-270-40 of the Administrative Code (other than those expressed as a method of treatment), or rule 3745-270-49 of the Administrative Code, and that contain "underlying hazardous constituents" as defined in rule 3745-270-02 of the Administrative Code; if these wastes are treated on-site to remove the hazardous characteristic; and are then sent off-site for treatment of underlying hazardous constituents, the certification must state the following:
"I certify under penalty of law that the waste has been treated in accordance with the requirements of rule 3745-270-40 or 3745-270-49 of the Administrative Code to remove the hazardous characteristic. This decharacterized waste contains underlying hazardous constituents that require further treatment to meet treatment standards. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment."
(e) For characteristic wastes that contain "underlying hazardous constituents" as defined in rule 3745-270-02 of the Administrative Code that are treated on-site to remove the hazardous characteristic and to treat underlying hazardous constituents to levels in the table in rule 3745-270-48 of the Administrative Code, the certification must state the following:
"I certify under penalty of law that the waste has been treated in accordance with the requirements of rule 3745-270-40 of the Administrative Code to remove the hazardous characteristic, and that "underlying hazardous constituents" as defined in rule 3745-270-02 of the Administrative Code have been treated on-site to meet the standards in the table in rule 3745-270-48 of the Administrative Code. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment."
(5) If the waste or treatment residue will be further managed at a different treatment, storage, or disposal facility, the treatment, storage, or disposal facility sending the waste or treatment residue off-site must comply with the notice and certification requirements applicable to generators under this rule.
(6) Where the wastes are recyclable materials used in a manner constituting disposal subject to the provisions of paragraph (B) of rule 3745-266-20 of the Administrative Code regarding treatment standards and prohibition levels, the owner or operator of a treatment facility (i.e., the recycler), for the initial shipment of waste, must prepare a one-time certification described in paragraph (B)(4) of this rule, and a one-time notice which includes the information in paragraph (B)(3) of this rule (except the manifest number). The certification and notification must be placed in the facility's on-site files. if the waste or the receiving facility changes, a new certification and notification must be prepared and placed in the on-site files. In addition, the recycling facility also must keep records of the name and location of each entity receiving the hazardous waste-derived product.
(C) Except where the owner or operator is disposing of any waste that is a recyclable material used in a manner constituting disposal pursuant to paragraph (B) of rule 3745-266-20 of the Administrative Code, the owner or operator of any land disposal facility disposing any waste subject to restrictions under Chapter 3745-270 of the Administrative Code must:
(1) Have copies of the notice and certifications specified in paragraph (A) or (B) of this rule.
(2) Test the waste, or an extract of the waste or treatment residue developed using test method 1311 (the toxicity characteristic leaching procedure, described in "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods," U.S. EPA publication SW-846) to assure that the wastes or treatment residues are in compliance with the applicable treatment standards set forth in rules 3745-270-40 to 3745-270-49 of the Administrative Code. Such testing must be performed according to the frequency specified in the facility's waste analysis plan as required by rule 3745-54-13 or 3745-65-13 of the Administrative Code.
(D) Generators or treaters who first claim that hazardous debris is excluded from the definition of "hazardous waste" under paragraph (F) of rule 3745-51-03 of the Administrative Code (i.e., debris treated by an extraction or destruction technology provided in the table in rule 3745-270-45 of the Administrative Code, and debris that the director has determined does not contain hazardous waste) are subject to the following notification and certification requirements:
(1) A one-time notification including the following information must be submitted to the director:
(a) The name and address of the licensed solid waste landfill receiving the treated debris;
(b) A description of the hazardous debris as initially generated, including the applicable EPA hazardous waste number(s); and
(c) For debris excluded under paragraph (F)(1) of rule 3745-51-03 of the Administrative Code, the technology from the table in rule 3745-270-45 of the Administrative Code used to treat the debris.
(2) The notification must be updated if the debris is shipped to a different facility, and, for debris excluded under paragraph (F)(1) of rule 3745-51-03 of the Administrative Code, if a different type of debris is treated or if a different technology is used to treat the debris.
(3) For debris excluded under paragraph (F)(1) of rule 3745-51-03 of the Administrative Code, the owner or operator of the treatment facility must document and certify compliance with the treatment standards from the table in rule 3745-270-45 of the Administrative Code as follows:
(a) Records must be kept of all inspections, evaluations, and analyses of treated debris that are made to determine compliance with the treatment standards;
(b) Records must be kept of any data or information the treater obtains during treatment of the debris that identifies key operating parameters of the treatment unit; and
(c) For each shipment of treated debris, a certification of compliance with the treatment standards must be signed by an authorized representative and placed in the treatment facility's files. The certification must state the following:
"I certify under penalty of law that the debris has been treated in accordance with the requirements of rule 3745-270-45 of the Administrative Code. I am aware that there are significant penalties for making a false certification, including the possibility of fine and imprisonment."
(E) Generators and treaters who first receive from Ohio EPA a determination that a given contaminated soil subject to LDRs as provided in paragraph (A) of rule 3745-270-49 of the Administrative Code no longer contains a listed hazardous waste and generators and treaters who first determine that a contaminated soil subject to LDRs as provided in paragraph (A) of rule 3745-270-49 of the Administrative Code no longer exhibits a characteristic of hazardous waste must:
(1) Prepare a one-time only documentation of these determinations including all supporting information; and
(2) Maintain that information in the facility files and other records for a minimum of three years.
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled "Incorporated by reference."]
Effective:
03/17/2012
R.C.
119.032 review dates: Exempt
Promulgated Under:
119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/30/1989, 02/11/1992, 09/02/1997, 10/20/1998, 12/07/2000,
12/07/2004, 09/05/2010
3745-270-09
Special rules regarding wastes that exhibit a characteristic.
(A) The initial generator of a waste must determine each EPA hazardous waste number applicable to the waste in order to determine the applicable treatment standards under rules 3745-270-40 to 3745-270-49 of the Administrative Code.This determination may be made concurrently with the hazardous waste determination required for rule 3745-52-11 of the Administrative Code. For purposes of Chapter 3745-270 of the Administrative Code, the waste will carry the EPA hazardous waste number for any applicable listing under rules 3745-51-30 to 3745-51-35 of the Administrative Code. In addition, where the waste exhibits a characteristic, the waste will carry one or more of the characteristic EPA hazardous waste numbers under rules 3745-51-20 to 3745-51-24 of the Administrative Code, except when the treatment standard for the listed waste operates in lieu of the treatment standard for the characteristic waste, as specified in paragraph (B) of this rule. If the generator determines that his waste displays a hazardous characteristic(and is not D001 nonwastewater treated by CMBST, RORGS, or POLYM in the table in rule 3745-270-42 of the Administrative Code), the generator must determine underlying hazardous constituents (as defined in rule 3745-270-02 of the Administrative Code) in the characteristic waste.
(B) Where a prohibited waste is both listed under rules 3745-51-30 to 3745-51-35 of the Administrative Code and exhibits a characteristic under rules 3745-51-20 to 3745-51-24 of the Administrative Code, the treatment standard for the EPA hazardous waste number listed in rules 3745-51-30 to 3745-51-35 of the Administrative Code will operate in lieu of the standard for the EPA hazardous waste number under rules 3745-51-20 to 3745-51-24 of the Administrative Code, provided that the treatment standard for the listed waste includes a treatment standard for the constituent that causes the waste to exhibit the characteristic. Otherwise, the waste must meet the treatment standards for all applicable listed and characteristic EPA hazardous waste numbers.
(C) In addition to any applicable standards determined from the initial point of generation, no prohibited waste which exhibits a characteristic under rules 3745-51-20 to 3745-51-24 of the Administrative Code may be land disposed unless the waste complies with the treatment standards under rules 3745-270-40 to 3745-270-49 of the Administrative Code.
(D) Wastes that exhibit a characteristic are also subject to requirements of rule 3745-270-07 of the Administrative Code, except that once the waste is no longer hazardous, a one-time notification and certification must be placed in the generator's or treater's on-site files . The notification and certification must be updated if the process or operation generating the waste changes and/or if the licensed solid waste landfill facility receiving the waste changes.
(1) The notification must include the following information:
(a) The name and address of the licensed solid waste facility receiving the waste shipment; and
(b) A description of the waste as initially generated, including the applicable EPA hazardous waste number(s), treatability group(s), and underlying hazardous constituents (as defined in rule 3745-270-02 of the Administrative Code), unless the waste will be treated and monitored for all underlying hazardous constituents. If all underlying hazardous constituents will be treated and monitored, there is no requirement to list any of the underlying hazardous constituents on the notice.
(2) The certification must be signed by an authorized representative and must state the language in paragraph (B)(4) of rule 3745-270-07 of the Administrative Code.
(a) If treatment removes the characteristic but does not meet standards applicable to underlying hazardous constituents, then the certification in paragraph (B)(4)(d) of rule 3745-270-07 of the Administrative Code applies.
(b) Reserved.
Effective:
09/05/2010
R.C.
119.032 review dates:
04/14/2010 and
08/25/2014
Promulgated
Under: 119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 02/11/1992, 09/02/1997, 10/20/1998, 12/07/2000, 12/07/2004
3745-270-20
Waste specific prohibitions- dyes and/or pigments production wastes.
(A) The waste specified in Chapter 3745-51 of the Administrative Code as EPA hazardous waste number K181, and soil and debris contaminated with this waste, radioactive wastes mixed with this waste, and soil and debris contaminated with radioactive wastes mixed with this waste are prohibited from land disposal.
(B) The requirements of paragraph (A) of this rule do not apply if:
(1) The wastes meet the applicable treatment standards specified in rules 3745-270-40 to 3745-270-49 of the Administrative Code;
(2) Persons have been granted an exemption from a prohibition pursuant to a petition under rule 3745-270-06 of the Administrative Code, with respect to those wastes and units covered by the petition;
(3) The wastes meet the applicable treatment standards established pursuant to a petition granted under rule 3745-270-44 of the Administrative Code;
(4) Hazardous debris has met the treatment standards in rule 3745-270-40 of the Administrative Code or the alternative treatment standards in rule 3745-270-45 of the Administrative Code; or
(5) Persons have been granted an extension to the effective date of a prohibition pursuant to rule 3745-270-05 of the Administrative Code, with respect to these wastes covered by the extension.
(C) To determine whether a hazardous waste identified in this rule exceeds the applicable treatment standards specified in rule 3745-270-40 of the Administrative Code, the initial generator must test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract of the waste, or the generator may use knowledge of the waste. If the waste contains regulated constituents in excess of the applicable levels in rules 3745-270-40 to 3745-270-49 of the Administrative Code, the waste is prohibited from land disposal, and all requirements of Chapter 3745-270 of the Administrative Code are applicable, except as otherwise specified.
Effective: 02/16/2009
R.C.
119.032 review dates: Exempt
Promulgated Under:
119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
3745-270-30
Waste specific prohibitions- wood preserving wastes.
(A) The wastes specified in rules 3745-51-30 to 3745-51-35 of the Administrative Code as EPA hazardous waste numbers F032, F034, and F035 are prohibited from land disposal.
(B) The following wastes are prohibited from land disposal:
(1) Soil and debris contaminated with F032, F034, or F035; and
(2) F032, F034, or F035 mixed with radioactive mixed wastes.
(C) Reserved.
(D) Paragraphs (A) and (B) of this rule do not apply if:
(1) The wastes meet the applicable treatment standards in rules 3745-270-40 to 3745-270-49 of the Administrative Code;
(2) Persons have been granted an exemption from a prohibition pursuant to rule 3745-270-06 of the Administrative Code with respect to those wastes and units covered by the petition;
(3) The wastes meet the applicable alternate treatment standards established pursuant to a petition granted under rule 3745-270-44 of the Administrative Code; or
(4) Persons have been granted an extension to the effective date of a prohibition pursuant to rule 3745-270-05 of the Administrative Code with respect to those wastes covered by the extension.
(E) To determine whether a hazardous waste identified in this rule exceeds the applicable treatment standards specified in rule 3745-270-40 of the Administrative Code, the initial generator shall test a sample of the waste extract or the entire waste(depending on whether the treatment standards are expressed as concentrations in the waste extract or as concentrations in the waste), or the generator may use knowledge of the waste. If the waste contains constituents in excess of the applicable universal treatment standard levels in rule 3745-270-48 of the Administrative Code, the waste is prohibited from land disposal, and all requirements of Chapter 3745-270 of the Administrative Code are applicable, except as otherwise specified.
Eff 12-7-00
Rule promulgated under: RC Chapter 119.
Rule authorized
by: RC 3734.12
Rule
amplifies: RC
3734.12
119.032 review dates: Exempt
3745-270-31
Waste specific prohibitions- dioxin-containing wastes.
(A) The dioxin-containing wastes specified in rule 3745-51-31 of the Administrative Code as hazardous waste numbers F020, F021, F022, F023, F026, F027, and F028 are prohibited from land disposal unless the following condition applies:
(1) The F020 to F023 and F026 to F028 dioxin-containing waste is contaminated soil and debris resulting from a response action taken under Section 104 or Section 106 of the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) or a corrective action taken under subtitle C of the Resource Conservation and Recovery Act (RCRA).
(2) Reserved.
(B) Effective November 8, 1990, the F020 to F023 and F026 to F028 dioxin-containing wastes listed in paragraph (A)(1) of this rule are prohibited from land disposal.
(C) Between December 30, 1989 and November 8, 1990, wastes included in paragraph (A)(1) of this rule may be disposed of in a landfill or surface impoundment only if such unit is in compliance with the requirements specified in of 40 CFR 268.5(h)(2) and all other applicable requirements of Chapters 3745-54 to 3745-57, 3745-65 to 3745-69, 3745-205 and 3745-256 of the Administrative Code.
(D) The requirements of paragraphs (A) and (B) of this rule do not apply if:
(1) The wastes meet the standards of rules 3745-270-40 to 3745-270-49 of the Administrative Code; or
(2) Persons have been granted an exemption from a prohibition pursuant to a petition under rule 3745-270-06 of the Administrative Code, with respect to those wastes and units covered by the petition; or
(3) Persons have been granted an extension to the effective date of a prohibition pursuant to rule 3745-270-05 of the Administrative Code with respect to those wastes covered by the extension.
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled "Incorporated by reference."]
Effective:
03/17/2012
R.C.
119.032 review dates: Exempt
Promulgated Under:
119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/30/1989, 12/07/2000, 12/07/2004
(A) The following wastes are prohibited from land disposal: Any volumes of soil exhibiting the toxicity characteristic solely because of the presence of metals (EPA hazardous waste numbers D004 to D011) and containing polychlorinated biphenyls (PCBs).
(B) The requirements of paragraph (A) of this rule do not apply if:
(1)
(a) The wastes contain halogenated organic compounds (HOCs) in total concentration less than one thousand milligrams per kilogram; and
(b) The wastes meet the treatment standards specified in rules 3745-270-40 to 3745-270-49 of the Administrative Code for EPA hazardous waste numbers D004 to D011, as applicable; or
(2)
(a) The wastes contain HOCs in total concentration less than one thousand milligrams per kilogram; and
(b) The wastes meet the alternative treatment standards specified in rule 3745-270-49 of the Administrative Code for contaminated soil; or
(3) Persons have been granted an exemption from a prohibition pursuant to a petition under rule 3745-270-06 of the Administrative Code with respect to those wastes and units covered by the petition; or
(4) The wastes meet applicable alternative treatment standards established pursuant to a petition granted under rule 3745-270-44 of the Administrative Code.
Effective:
09/05/2010
R.C.
119.032 review dates: Exempt
Promulgated Under:
119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
3745-270-33
Waste specific prohibitions- chlorinated aliphatic wastes.
(A) The wastes specified in Chapter 3745-51 of the Administrative Code as EPA hazardous wastes numbers K174 and K175, soil and debris contaminated with these wastes, radioactive wastes mixed with these wastes, and soil and debris contaminated with radioactive wastes mixed with these wastes are prohibited from land disposal.
(B) The requirements of paragraph (A) of this rule do not apply if:
(1) The wastes meet the applicable treatment standards specified in rules 3745-270-40 to 3745-270-49 of the Administrative Code;
(2) Persons have been granted an exemption from a prohibition pursuant to a petition under rule 3745-270-06 of the Administrative Code, with respect to those wastes and units covered by the petition;
(3) The wastes meet the applicable treatment standards established pursuant to a petition granted under rule 3745-270-44 of the Administrative Code;
(4) Hazardous debris has met the treatment standards in rule 3745-270-40 of the Administrative Code or the alternative treatment standards in rule 3745-270-45 of the Administrative Code; or
(5) Persons have been granted an extension to the effective date of a prohibition pursuant to rule 3745-270-05 of the Administrative Code, with respect to these wastes covered by the extension.
(C) To determine whether a hazardous waste identified in this rule exceeds the applicable treatment standards specified in rule 3745-270-40 of the Administrative Code, the initial generator must test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or the waste, or the generator may use knowledge of the waste. If the waste contains regulated constituents in excess of the applicable levels of rules 3745-270-40 to 3745-270-49 of the Administrative Code, the waste is prohibited from land disposal, and all requirements of Chapter 3745-270 of the Administrative Code are applicable, except as otherwise specified.
(D) Disposal of K175 wastes that have complied with all applicable treatment standards in rule 3745-270-40 of the Administrative Code must also be macroencapsulated in accordance with the table in rule 3745-270-40 of the Administrative Code unless the waste is placed in:
(1) A permitted hazardous waste landfill containing only K175 wastes that meet all applicable treatment standards in rule 3745-270-40 of the Administrative Code; or
(2) A dedicated permitted hazardous waste landfill cell in which all other wastes being co-disposed are at pH 6.0.
Eff 12-7-04
Rule promulgated under: RC
119.03
Rule authorized
by: RC 3734.12
Rule
amplifies: RC
3734.12
R.C.
119.032 review dates: Exempt
3745-270-34
Waste specific prohibitions- toxicity characteristic metal wastes.
(A) The following wastes are prohibited from land disposal: The wastes specified in Chapter 3745-51 of the Administrative Code as EPA hazardous waste numbers D004 to D011 that are newly identified (i.e. wastes, soil, or debris identified as hazardous by the toxic characteristic leaching procedure but not the extraction procedure), and waste, soil, or debris from mineral processing operations that is identified as hazardous by the specifications in Chapter 3745-51 of the Administrative Code.
(B) The following waste is prohibited from land disposal: Slag from secondary lead smelting which exhibits the toxicity characteristic due to the presence of one or more metals.
(C) The following wastes are prohibited from land disposal: Newly identified characteristic wastes from elemental phosphorus processing; radioactive wastes mixed with EPA hazardous wastes D004 to D011 that are newly identified (i.e. wastes, soil, or debris identified as hazardous by the toxic characteristic leaching procedure but not the extraction procedure); or mixed with newly identified characteristic mineral processing wastes, soil, or debris.
(D) Reserved.
(E) The requirements of paragraphs (A) and (C) of this rule do not apply if:
(1) The wastes meet the applicable treatment standards specified in rules 3745-270-40 to 3745-270-49 of the Administrative Code;
(2) Persons have been granted an exemption from a prohibition pursuant to a petition under rule 3745-270-06 of the Administrative Code, with respect to those wastes and units covered by the petition;
(3) The wastes meet the applicable alternate treatment standards established pursuant to a petition granted under rule 3745-270-44 of the Administrative Code; or
(4) Persons have been granted an extension to the effective date of a prohibition pursuant to rule 3745-270-05 of the Administrative Code, with respect to these wastes covered by the extension.
(F) To determine whether a hazardous waste identified in this rule exceeds the applicable treatment standards specified in rule 3745-270-40 of the Administrative Code, the initial generator shall test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or in the waste, or the generator may use knowledge of the waste. If the waste contains constituents(including underlying hazardous constituents in characteristic wastes) in excess of the applicable universal treatment standard levels in rule 3745-270-48 of the Administrative Code, the waste is prohibited from land disposal, and all requirements of Chapter 3745-270 of the Administrative Code are applicable, except as otherwise specified.
Eff 12-7-00
Rule promulgated under: RC Chapter 119.
Rule authorized
by: RC 3734.12
Rule
amplifies: RC
3734.12
119.032 review date: Exempt
3745-270-35
Waste-specific prohibitions-petroleum refining wastes.
(A) The wastes specified in Chapter 3745-51 of the Administrative Code as EPA hazardous wastes numbers K169, K170, K171, and K172, soils and debris contaminated with these wastes, radioactive wastes mixed with these hazardous wastes, and soils and debris contaminated with these radioactive mixed wastes, are prohibited from land disposal.
(B) The requirements of paragraph (A) of this rule do not apply if:
(1) The wastes meet the applicable treatment standards specified in rules 3745-270-40 to 3745-270-49 of the Administrative Code;
(2) Persons have been granted an exemption from a prohibition pursuant to a petition under rule 3745-270-06 of the Administrative Code, with respect to those wastes and units covered by the petition;
(3) The wastes meet the applicable treatment standards established pursuant to a petition granted under rule 3745-270-44 of the Administrative Code;
(4) Hazardous debris that has met treatment standards in rule 3745-270-40 of the Administrative Code or in the alternative treatment standards in rule 3745-270-45 of the Administrative Code; or
(5) Persons have been granted an extension to the effective date of a prohibition pursuant to rule 3745-270-05 of the Administrative Code, with respect to these wastes covered by the extension.
(C) To determine whether a hazardous waste identified in this rule exceeds the applicable treatment standards specified in rule 3745-270-40 of the Administrative Code, the initial generator shall test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or the waste, or the generator may use knowledge of the waste. If the waste contains constituents in excess of the applicable universal treatment standard levels of rule 3745-270-48 of the Administrative Code, the waste is prohibited from land disposal, and all requirements of Chapter 3745-270 of the Administrative Code are applicable, except as otherwise specified.
Eff 12-7-00
Rule promulgated under: RC Chapter 119.
Rule authorized
by: RC 3734.12
Rule
amplifies: RC
3734.12
119.032 review date: Exempt
3745-270-36
Waste specific prohibitions- inorganic chemical wastes.
(A) The wastes specified in Chapter 3745-51 of the Administrative Code as EPA hazardous waste numbers K176, K177, and K178, and soil and debris contaminated with these wastes, radioactive wastes mixed with these wastes, and soil and debris contaminated with radioactive wastes mixed with these wastes, are prohibited from land disposal.
(B) The requirements of paragraph (A) of this rule do not apply if:
(1) The wastes meet the applicable treatment standards specified in rules 3745-270-40 to 3745-270-49 of the Administrative Code;
(2) Persons have been granted an exemption from a prohibition pursuant to a petition under rule 3745-270-06 of the Administrative Code, with respect to those wastes and units covered by the petition;
(3) The wastes meet the applicable treatment standards established pursuant to a petition granted under rule 3745-270-44 of the Administrative Code;
(4) Hazardous debris has met the treatment standards in rule 3745-270-40 of the Administrative Code or the alternative treatment standards in rule 3745-270-45 of the Administrative Code; or
(5) Persons have been granted an extension to the effective date of a prohibition pursuant to rule 3745-270-05 of the Administrative Code, with respect to these wastes covered by the extension.
(C) To determine whether a hazardous waste identified in this rule exceeds the applicable treatment standards specified in rule 3745-270-40 of the Administrative Code, the initial generator must test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or the waste, or the generator may use knowledge of the waste. If the waste contains regulated constituents in excess of the applicable levels specified in rules 3745-270-40 to 3745-270-49 of the Administrative Code, the waste is prohibited from land disposal, and all requirements of Chapter 3745-270 of the Administrative Code are applicable, except as otherwise specified.
Eff 12-7-04
Rule promulgated under: RC
119.03
Rule authorized
by: RC 3734.12
Rule
amplifies: RC
3734.12
R.C.
119.032 review dates: Exempt
(A) The wastes specified in rule 3745-51-21 of the Administrative Code as D001(and is not in the high TOC ignitable liquids subcategory), and specified in in rule 3745-51-22 of the Administrative Code as D002, that are managed in systems other than those whose discharge is regulated under the clean water act(CWA), or that inject in Class I deep wells regulated under the safe drinking water act, or that are zero dischargers that engage in CWA-equivalent treatment before ultimate land disposal, are prohibited from land disposal. CWA-equivalent treatment means biological treatment for organics, alkaline chlorination or ferrous sulfate precipitation for cyanide, precipitation/sedimentation for metals, reduction of hexavalent chromium, or other treatment technology that can be demonstrated to perform equally or greater than these technologies.
(B) The wastes specified in rule 3745-51-21 of the Administrative Code as D001(and is not in the high TOC ignitable liquids subcategory), and specified in rule 3745-51-22 of the Administrative Code as D002, that are managed in systems defined in 40 CFR 144.6(e) and 40 CFR 146.6(e) as Class V injection wells, that do not engage in CWA-equivalent treatment before injection, are prohibited from land disposal.
Eff 12-7-00
Rule promulgated under: RC Chapter 119.
Rule authorized
by: RC 3734.12
Rule
amplifies: RC
3734.12
119.032 review date: Exempt
(A) (1) The wastes specified in rule 3745-51-32 of the Administrative Code as EPA hazardous waste numbers K141, K142, K143, K144, K145, K147, K148, K149, K150, and K151 are prohibited from land disposal.
(2) Debris contaminated with EPA hazardous waste numbers F037, F038, K107 to K112, K117, K118, K123 to K126, K131, K132, K136, U328, U353, U359, and soil and debris contaminated with D012 to D043, K141 to K145, and K147 to K151 are prohibited from land disposal.
(3) The following wastes that are specified in Table 1 of rule 3745-51-24 of the Administrative Code as EPA hazardous waste numbers: D012, D013, D014, D015, D016, D017, D018, D019, D020, D021, D022, D023, D024, D025, D026, D027, D028, D029, D030, D031, D032, D033, D034, D035, D036, D037, D038, D039, D040, D041, D042, D043 that are not radioactive, or that are managed in systems other than those whose discharge is regulated under the clean water act(CWA), or that are zero dischargers that do not engage in CWA-equivalent treatment before ultimate land disposal, or that are injected in Class I deep wells regulated under the safe drinking water act (SDWA), are prohibited from land disposal. CWA-equivalent treatment means biological treatment for organics, alkaline chlorination or ferrous sulfate precipitation for cyanide, precipitation/sedimentation for metals, reduction of hexavalent chromium, or other treatment technology that can be demonstrated to perform equally or better than these technologies.
(B) (1) Radioactive wastes that are mixed with D018 to D043 wastes that are managed in systems other than those whose discharge is regulated under the CWA, or that inject in Class I deep wells regulated under the SDWA, or that are zero dischargers that engage in CWA-equivalent treatment before ultimate land disposal, are prohibited from land disposal. CWA-equivalent treatment means biological treatment for organics, alkaline chlorination or ferrous sulfate precipitation for cyanide, precipitation/sedimentation for metals, reduction of hexavalent chromium, or other treatment technology that can be demonstrated to perform equally or greater than these technologies.
(2) Radioactive wastes mixed with K141 to K145 wastes, and K147 to K151 wastes are also prohibited from land disposal.
(3) Soil and debris contaminated with the radioactive mixed wastes indicated in paragraphs (B)(1) and (B)(2) of this rule are prohibited from land disposal.
(C) Reserved.
(D) The requirements of paragraphs (A), (B), and (C) of this rule do not apply if:
(1) The wastes meet the applicable treatment standards specified in rules 3745-270-40 to 3745-270-49 of the Administrative Code;
(2) Persons have been granted an exemption from a prohibition pursuant to a petition under rule 3745-270-06 of the Administrative Code, with respect to those wastes and units covered by the petition;
(3) The wastes meet the applicable alternate treatment standards established pursuant to a petition granted under rule 3745-270-44 of the Administrative Code;
(4) Persons have been granted an extension to the effective date of a prohibition pursuant to rule 3745-270-05 of the Administrative Code, with respect to these wastes covered by the extension.
(E) To determine whether a hazardous waste identified in this rule exceeds the applicable treatment standards specified in rule 3745-270-40 of the Administrative Code, the initial generator shall test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or the waste, or the generator may use knowledge of the waste. If the waste contains constituents in excess of the applicable levels in rules 3745-270-40 to 3745-270-49 of the Administrative Code, the waste is prohibited from land disposal, and all requirements of Chapter 3745-270 of the Administrative Code are applicable, except as otherwise specified.
Eff 12-7-00
Rule promulgated under: RC Chapter 119.
Rule authorized
by: RC 3734.12
Rule
amplifies: RC
3734.12
119.032 review date: Exempt
(A) The wastes specified in rule 3745-51-32 of the Administrative Code as EPA hazardous waste numbers K156 to K159, and K161, and in rule 3745-51-33 of the Administrative Code as EPA hazardous waste numbers P127, P128, P185, P188 to P192, P194, P196 to P199, P201 to P205, U271, U278 to U280, U364, U367, U372, U373, U387, U389, U394, U395, U404, and U409 to U411, are prohibited from land disposal. In addition, soil and debris contaminated with these wastes are prohibited from land disposal.
(B) The wastes identified in rule 3745-51-23 of the Administrative Code as D003 that are managed in systems other than those whose discharge is regulated under the clean water act(CWA), or that inject in Class I deep wells regulated under the safe drinking water act (SDWA), or that are zero dischargers that engage in CWA-equivalent treatment before ultimate land disposal, are prohibited from land disposal. This prohibition does not apply to unexploded ordnance and other explosive devices which have been the subject of an emergency response. [Such D003 wastes are prohibited unless they meet the treatment standard of DEACT before land disposal (see rule 3745-270-40 of the Administrative Code)].
(C) The wastes specified in rule 3745-51-32 of the Administrative Code as EPA hazardous waste number K088 are prohibited from land disposal. In addition, soil and debris contaminated with these wastes are prohibited from land disposal.
(D) Radioactive wastes mixed with K088, K156 to K159, K161, P127, P128, P185, P188 to P192, P194, P196 to P199, P201 to P205, U271, U278 to U280, U364, U367, U372, U373, U387, U389, U394, U395, U404, and U409 to U411 are also prohibited from land disposal. In addition, soil and debris contaminated with these radioactive mixed wastes are prohibited from land disposal.
(E) Reserved.
(F) The requirements of paragraphs (A), (B), (C), and (D) of this rule do not apply if:
(1) The wastes meet the applicable treatment standards specified in rules 3745-270-40 to 3745-270-49 of the Administrative Code;
(2) Persons have been granted an exemption from a prohibition pursuant to a petition under rule 3745-270-06 of the Administrative Code with respect to those wastes and units covered by the petition;
(3) The wastes meet the applicable alternate treatment standards established pursuant to a petition granted under rule 3745-270-44 of the Administrative Code;
(4) Persons have been granted an extension to the effective date of a prohibition pursuant to rule 3745-270-05 of the Administrative Code with respect to these wastes covered by the extension.
(G) To determine whether a hazardous waste identified in this rule exceeds the applicable treatment standards specified in rule 3745-270-40 of the Administrative Code, the initial generator shall test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or the waste, or the generator may use knowledge of the waste. If the waste contains constituents in excess of the applicable levels in rules 3745-270-40 to 3745-270-49 of the Administrative Code, the waste is prohibited from land disposal, and all requirements of Chapter 3745-270 of the Administrative Code are applicable, except as otherwise specified.
Eff 12-7-00
Rule promulgated under: RC Chapter 119.
Rule authorized
by: RC 3734.12
Rule
amplifies: RC
3734.12
119.032 review date: Exempt
3745-270-40
Applicability -treatment standards.
(A) A prohibited waste identified in the table in this rule "Treatment Standards for Hazardous Wastes" may be land disposed only if it meets the requirements found in the table in this rule. For each waste, the table in this rule identifies one of three types of treatment standard requirements:
(1) All hazardous constituents in the waste or in the treatment residue must be at or below the values found in the table in this rule for that waste ("total waste standards"); or
(2) 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 in this rule ("waste extract standards"); or
(3) The waste must be treated using the technology specified in the table in this rule ("technology standard"), which are described in detail in the table in rule 3745-270-42 of the Administrative Code.
(B)
(1) For wastewaters, compliance with concentration level standards is based on maximums for any one day, except for D004 to D011 wastes for which the previously promulgated treatment standards based on grab samples remain in effect.
(2) For all nonwastewaters, compliance with concentration level standards is based on grab sampling.
(3) 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," U.S. EPA publication SW-846, 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.
(4) 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 director under the procedures set forth in paragraph (B) of rule 3745-270-42 of the Administrative Code.
(C) 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.
(D) Notwithstanding the prohibitions specified in paragraph (A) of this rule, treatment and disposal facilities may demonstrate [and certify pursuant to paragraph (B)(5) of rule 3745-270-07 of the Administrative Code] compliance with the treatment standards for organic constituents specified by a footnote in the table in this rule, provided the following conditions are satisfied:
(1) The treatment standards for the organic constituents were established based on incineration in units operated in accordance with the technical requirements of rules 3745-57-40 to 3745-57-51 of the Administrative Code, or based on combustion in fuel substitution units operating in accordance with applicable technical requirements in the hazardous waste rules;
(2) The treatment or disposal facility has used the methods referenced in paragraph (D)(1) of this rule to treat the organic constituents; and
(3) 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 by an order of magnitude the treatment standards specified in this rule.
(E) For characteristic wastes (D001 to D043) that are subject to treatment standards in the table in this rule, 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 rule 3745-270-02 of the Administrative Code) must meet universal treatment standards found in the table in rule 3745-270-48 of the Administrative Code prior to "land disposal" (as defined in rule 3745-270-02 of the Administrative Code).
(F) The treatment standards for F001 to 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. If the waste contains any of these three constituents along with any of the other twenty-five constituents found in F001 to F005, then compliance with treatment standards for carbon disulfide, cyclohexanone, and/or methanol is not required.
(G) Reserved.
(H) Prohibited D004 to 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 re-treated to meet treatment standards in this ruleprior to land disposal.
(I) Reserved.
(J) The treatment standards for the wastes specified in rule 3745-51-33 of the Administrative Code 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 in this rule, or by treating the waste by the following technologies: combustion, as described by the technology code CMBST in the table in rule 3745-270-42 of the Administrative Code, for nonwastewaters; and, biodegradation as described by the technology code BIODG, carbon adsorption as described by the technology code CARBN, chemical oxidation as described by the technology code CHOXD, or combustion as described as technology code CMBST in the table in rule 3745-270-42 of the Administrative Code, for wastewaters.
Table: Treatment Standards for Hazardous Wastes
The treatment standards that previously appeared in tables in rules 3745-59-41, 3745-59-42, and 3745-59-43 of the Administrative Code have been consolidated into this table.
| EPA hazardous waste number | Waste description and treatment/regulatory subcategory 1 | Regulated hazardous constituent | Wastewaters | Nonwastewaters | |
| Common name | CAS 2 number | Concentration 3 in mg/l; or technology code 4 | Concentration 5 in mg/kg unless noted as "mg/l TCLP;" or technology code 4 | ||
| D001 9 | Ignitable characteristic wastes, except for the paragraph (A)(1) of rule 3745-51-21 of the Administrative Code high TOC subcategory. | NA | NA | DEACT and meet standards in rule 3745-270-48 of the Administrative Code 8; or RORGS; or CMBST | DEACT and meet standards in rule 3745-270-48 of the Administrative Code 8; or RORGS; or CMBST |
| High TOC ignitable characteristic liquids subcategory based on paragraph (A)(1) of rule 3745-51-21 of the Administrative Code- greater than or equal to ten per cent total organic carbon. (Comment: This subcategory consists of nonwastewaters only.) | NA | NA | NA | RORGS; CMBST; or POLYM | |
| D002 9 | Corrosive characteristic wastes. | NA | NA | DEACT and meet standards in rule 3745-270-48 of the Administrative Code 8 | DEACT and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D002, D004, D005, D006, D007, D008, D009, D010, D011 | Radioactive high level wastes generated during the reprocessing of fuel rods. (Comment: This subcategory consists of nonwastewaters only.) | Corrosivity (pH) | NA | NA | HLVIT |
| Arsenic | 7440-38-2 | NA | HLVIT | ||
| Barium | 7440-39-3 | NA | HLVIT | ||
| Cadmium | 7440-43-9 | NA | HLVIT | ||
| Chromium (total) | 7440-47-3 | NA | HLVIT | ||
| Lead | 7439-92-1 | NA | HLVIT | ||
| Mercury | 7439-97-6 | NA | HLVIT | ||
| Selenium | 7782-49-2 | NA | HLVIT | ||
| Silver | 7440-22-4 | NA | HLVIT | ||
| D003 9 | Reactive sulfides subcategory based on paragraph (A)(5) of rule 3745-51-23 of the Administrative Code. | NA | NA | DEACT | DEACT |
| Explosives subcategory based on paragraphs (A)(6), (A)(7), and (A)(8) of rule 3745-51-23 of the Administrative Code. | NA | NA | DEACT and meet standards in rule 3745-270-48 of the Administrative Code 8 | DEACT and meet standards in rule 3745-270-48 of the Administrative Code 8 | |
| Unexploded ordnance and other explosive devices which have been the subject of an emergency response. | NA | NA | DEACT | DEACT | |
| Other reactives subcategory based on paragraph (A)(1) of rule 3745-51-23 of the Administrative Code. | NA | NA | DEACT and meet standards in rule 3745-270-48 of the Administrative Code 8 | DEACT and meet standards in rule 3745-270-48 of the Administrative Code 8 | |
| Water reactive subcategory based on paragraphs (A)(2), (A)(3), and (A)(4) of rule 3745-51-23 of the Administrative Code. (Comment: This subcategory consists of nonwastewaters only.) | NA | NA | NA | DEACT and meet standards in rule 3745-270-48 of the Administrative Code 8 | |
| Reactive cyanides subcategory based paragraph (A)(5) of rule 3745-51-23 of the Administrative Code. | Cyanides (total) 7 | 57-12-5 | Reserved | 590.0 | |
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| D004 9 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for arsenic based on the toxicity characteristic leaching procedure (TCLP) in SW-846. | Arsenic | 7440-38-2 | 1.4 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 5.0 mg/l TCLP and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D005 9 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for barium based on the extraction procedure (EP) in SW-846. | Barium | 7440-39-3 | 1.2 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 21 mg/l TCLP and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D006 9 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for cadmium based on the TCLP in SW-846. | Cadmium | 7440-43-9 | 0.69 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 0.11 mg/l TCLP and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| Cadmium containing batteries subcategory. (Comment: This subcategory consists of nonwastewaters only.) | Cadmium | 7440-43-9 | NA | RTHRM | |
| Radioactively contaminated cadmium-containing batteries. (Comment: This subcategory consists of nonwastewaters only.) | Cadmium | 7440-43-9 | NA | Macroencapsulation in accordance with rule 3745-270-45 of the Administrative Code | |
| D007 9 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for chromium based on the TCLP) in SW-846. | Chromium (Total) | 7440-47-3 | 2.77 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 0.6 mg/l TCLP and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D008 9 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for lead based on the TCLP in SW-846. | Lead | 7439-92-1 | 0.69 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 0.75 mg/l TCLP and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| Lead acid batteries subcategory. [Comment: This standard only applies to lead acid batteries that are identified as RCRA hazardous wastes and that are not excluded elsewhere from regulation under Chapter 3745-270 of the Administrative Code or exempted under other rules (see rule 3745-266-80 of the Administrative Code). This subcategory consists of nonwastewaters only.] | Lead | 7439-92-1 | NA | RLEAD | |
| Radioactive lead solids subcategory. (Comment: 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 | |
| D009 9 | Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the TCLP in SW-846; and contain greater than or equal to 260.0 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 TCLP in SW-846; and contain greater than or equal to 260.0 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 TCLP in SW-846; and contain less than 260.0 mg/kg total mercury and that are residues from RMERC only. (Low mercury subcategory) | Mercury | 7439-97-6 | NA | 0.2 mg/l TCLP and meet standards in rule 3745-270-48 of the Administrative Code 8 | |
| All other nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the TCLP in SW-846; and contain less than 260.0 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 standards in rule 3745-270-48 of the Administrative Code 8 | |
| All D009 wastewaters | Mercury | 7439-97-6 | 0.15 and meet standards in rule 3745-270-48 of the Administrative Code 8 | NA | |
| Elemental mercury contaminated with radioactive materials. (Comment: This subcategory consists of nonwastewaters only.) | Mercury | 7439-97-6 | NA | AMLGM | |
| Hydraulic oil contaminated with mercury radioactive materials subcategory. (Comment: This subcategory consists of nonwastewaters only.) | Mercury | 7439-97-6 | NA | IMERC | |
| Radioactively contaminated mercury-containing batteries. (Comment: This subcategory consists of nonwastewaters only.) | Mercury | 7439-97-6 | NA | Macroencapsulation in accordance with rule 3745-270-45 of the Administrative Code | |
| D010 9 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for selenium based on the TCLP in SW-846. | Selenium | 7782-49-2 | 0.82 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 5.7 mg/l TCLP and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D011 9 | Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for silver based on the TCLP in SW-846. | Silver | 7440-22-4 | 0.43 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 0.14 mg/l TCLP and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| Radioactively contaminated silver-containing batteries. (Comment: This subcategory consists of nonwastewaters only.) | Silver | 7440-22-4 | NA | Macroencapsulation in accordance with rule 3745-270-45 of the Administrative Code | |
| D012 9 | Wastes that are TC for Endrin based on the TCLP in SW-846 method 1311. | Endrin | 72-20-8 | BIODG; or CMBST | 0.13 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| Endrin aldehyde | 7421-93-4 | BIODG; or CMBST | 0.13 and meet standards in rule 3745-270-48 of the Administrative Code 8 | ||
| D013 9 | Wastes that are TC for Lindane based on the TCLP in SW-846 method 1311. | alpha-BHC | 319-84-6 | CARBN; or CMBST | 0.066 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| beta-BHC | 319-85-7 | CARBN; or CMBST | 0.066 and meet standards in rule 3745-270-48 of the Administrative Code 8 | ||
| delta-BHC | 319-86-8 | CARBN; or CMBST | 0.066 and meet standards in rule 3745-270-48 of the Administrative Code 8 | ||
| gamma-BHC (Lindane) | 58-89-9 | CARBN; or CMBST | 0.066 and meet standards in rule 3745-270-48 of the Administrative Code 8 | ||
| D014 9 | Wastes that are TC for Methoxychlor based on the TCLP in SW-846 method 1311. | Methoxychlor | 72-43-5 | WETOX or CMBST | 0.18 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D015 9 | Wastes that are TC for Toxaphene based on the TCLP in SW-846 method 1311. | Toxaphene | 8001-35-2 | BIODG or CMBST | 2.6 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D016 9 | Wastes that are TC for 2,4-D (2,4-Dichlorophenoxyacetic acid) based on the TCLP in SW-846 method 1311. | 2,4-D (2,4-Dichlorophenoxyacetic acid) | 94-75-7 | CHOXD, BIOGD, or CMBST | 10.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D017 9 | Wastes that are TC for 2,4,5-TP (Silvex) based on the TCLP in SW-846 method 1311. | 2,4,5-TP (Silvex) | 93-72-1 | CHOXD or CMBST | 7.9 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D018 9 | Wastes that are TC for Benzene based on the TCLP in SW-846 method 1311. | Benzene | 71-43-2 | 0.14 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 10.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D019 9 | Wastes that are TC for Carbon tetrachloride based on the TCLP in SW-846 method 1311. | Carbon tetrachloride | 56-23-5 | 0.057 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 6.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D020 9 | Wastes that are TC for Chlordane based on the TCLP in SW-846 method 1311. | Chlordane (alpha and gamma isomers) | 57-74-9 | 0.0033 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 0.26 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D021 9 | Wastes that are TC for Chlorobenzene based on the TCLP in SW-846 method 1311. | Chlorobenzene | 108-90-7 | 0.057 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 6.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D022 9 | Wastes that are TC for Chloroform based on the TCLP in SW-846 method 1311. | Chloroform | 67-66-3 | 0.046 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 6.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D023 9 | Wastes that are TC for o-Cresol based on the TCLP in SW-846 method 1311. | o-Cresol | 95-48-7 | 0.11 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 5.6 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D024 9 | Wastes that are TC for m-Cresol based on the TCLP in SW-846 method 1311. | m-Cresol (difficult to distinguish from p-Cresol) | 108-39-4 | 0.77 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 5.6 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D025 9 | Wastes that are TC for p-Cresol based on the TCLP in SW-846 method 1311. | p-Cresol (difficult to distinguish from m-Cresol) | 106-44-5 | 0.77 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 5.6 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D026 9 | Wastes that are TC for Cresols (total) based on the TCLP in SW-846 method 1311. | Cresol- mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations) | 1319-77-3 | 0.88 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 11.2 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D027 9 | Wastes that are TC for p-Dichlorobenzene based on the TCLP in SW-846 method 1311. | p-Dichlorobenzene (1,4-Dichlorobenzene) | 106-46-7 | 0.09 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 6.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D028 9 | Wastes that are TC for 1,2-Dichloroethane based on the TCLP in SW-846 method 1311. | 1,2-Dichloroethane | 107-06-2 | 0.21 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 6.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D029 9 | Wastes that are TC for 1,1-Dichlorethylene based on the TCLP in SW-846 method 1311. | 1,1-Dichlorethylene | 75-35-4 | 0.025 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 6.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D030 9 | Wastes that are TC for 2,4-Dinitrotoluene based on the TCLP in SW-846 method 1311. | 2,4-Dinitrotoluene | 121-14-2 | 0.32 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 140.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D031 9 | Wastes that are TC for Heptachlor based on the TCLP in SW-846 method 1311. | Heptachlor | 76-44-8 | 0.0012 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 0.066 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| Heptachlor epoxide | 1024-57-3 | 0.016 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 0.066 and meet standards in rule 3745-270-48 of the Administrative Code 8 | ||
| D032 9 | Wastes that are TC for Hexachlorobenzene based on the TCLP in SW-846 method 1311. | Hexachlorobenzene | 118-74-1 | 0.055 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 10.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D033 9 | Wastes that are TC for Hexachlorobutadiene based on the TCLP in SW-846 method 1311. | Hexachlorobutadiene | 87-68-3 | 0.055 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 5.6 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D034 9 | Wastes that are TC for Hexachloroethane based on the TCLP in SW-846 method 1311. | Hexachloroethane | 67-72-1 | 0.055 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 30.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D035 9 | Wastes that are TC for Methyl ethyl ketone based on the TCLP in SW-846 method 1311. | Methyl ethyl ketone | 78-93-3 | 0.28 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 36.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D036 9 | Wastes that are TC for Nitrobenzene based on the TCLP in SW-846 method 1311. | Nitrobenzene | 98-95-3 | 0.068 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 14.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D037 9 | Wastes that are TC for Pentachlorophenol based on the TCLP in SW-846 method 1311. | Pentachlorophenol | 87-86-5 | 0.089 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 7.4 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D038 9 | Wastes that are TC for Pyridine based on the TCLP in SW-846 method 1311. | Pyridine | 110-86-1 | 0.014 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 16.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D039 9 | Wastes that are TC for Tetrachloroethylene based on the TCLP in SW-846 method 1311. | Tetrachloroethylene | 127-18-4 | 0.056 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 6.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D040 9 | Wastes that are TC for Trichloroethylene based on the TCLP in SW-846 method 1311. | Trichloroethylene | 79-01-6 | 0.054 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 6.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D041 9 | Wastes that are TC for 2,4,5-Trichlorophenol based on the TCLP in SW-846 method 1311. | 2,4,5-Trichlorophenol | 95-95-4 | 0.18 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 7.4 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D042 9 | Wastes that are TC for 2,4,6-Trichlorophenol based on the TCLP in SW-846 method 1311. | 2,4,6-Trichlorophenol | 88-06-2 | 0.035 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 7.4 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| D043 9 | Wastes that are TC for Vinyl chloride based on the TCLP in SW-846 method 1311. | Vinyl chloride | 75-01-4 | 0.27 and meet standards in rule 3745-270-48 of the Administrative Code 8 | 6.0 and meet standards in rule 3745-270-48 of the Administrative Code 8 |
| F001, F002, F004, and 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, ethyly benzene, ethyl ether, isobutyl alcohol, methanol, methylene chloride, methyl ethyl ketone, methyl isobutyl ketone, nitrobenzene, 2-nitropane, pyridine, tetrachloroethylene, toluene, 1,1,1-trichloroethane, 1,1,2-trichloroethane, 1,1,2-trichloro-1,2,2-trifluoroethane, trichloroethylene, trichloromono-fluoromethane, and/or xylenes (except as specifically noted in other subcategories). See further details of these listings in rule 3745-51-31 of the Administrative Code. | Acetone | 67-64-1 | 0.28 | 160.0 |
| Benzene | 71-43-2 | 0.14 | 10.0 | ||
| n-Butyl alcohol | 71-36-3 | 5.6 | 2.6 | ||
| Carbon disulfide | 75-15-0 | 3.8 | NA | ||
| Carbon tetrachloride | 56-23-5 | 0.057 | 6.0 | ||
| Chlorobenzene | 108-90-7 | 0.057 | 6.0 | ||
| o-Cresol | 95-48-7 | 0.11 | 5.6 | ||
| m-Cresol (difficult to distinguish from 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 | ||
| Cyclohexanone | 108-94-1 | 0.36 | NA | ||
| o-Dichlorobenzene | 95-50-1 | 0.088 | 6.0 | ||
| Ethyl acetate | 141-78-6 | 0.34 | 33.0 | ||
| Ethyly benzene | 100-41-4 | 0.057 | 10.0 | ||
| Ethyl ether | 60-29-7 | 0.12 | 160.0 | ||
| Isobutyl alcohol | 78-83-1 | 5.6 | 170.0 | ||
| Methanol | 67-56-1 | 5.6 | NA | ||
| Methylene chloride | 75-9-2 | 0.089 | 30.0 | ||
| Methyl ethyl ketone | 78-93-3 | 0.28 | 36.0 | ||
| Methyl isobutyl ketone | 108-10-1 | 0.14 | 33.0 | ||
| Nitrobenzene | 98-95-3 | 0.068 | 14.0 | ||
| Pyridine | 110-86-1 | 0.014 | 16.0 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| Toluene | 108-88-3 | 0.08 | 10.0 | ||
| 1,1,1-Trichloroethane | 71-55-6 | 0.054 | 6.0 | ||
| 1,1,2-Trichloroethane | 79-00-5 | 0.054 | 6.0 | ||
| 1,1,2-Trichloro-1,2,2-trifluoroethane | 76-13-1 | 0.057 | 30.0 | ||
| Trichloroethylene | 79-01-6 | 0.054 | 6.0 | ||
| Trichloromono-fluoromethane | 75-69-4 | 0.02 | 30.0 | ||
| Xylenes- mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30.0 | ||
| F003 and/or F005 solvent wastes that contain any combination of one or more of the following three solvents as the only listed F001 to F005 solvents: carbon disulfide, cyclohexanone, and/or methanol. | Carbon disulfide | 75-15-0 | 3.8 | 4.8 mg/l TCLP | |
| Cyclohexanone | 108-94-1 | 0.36 | 0.75 mg/l TCLP | ||
| Methanol | 67-56-1 | 5.6 | 0.75 mg/l TCLP | ||
| F005 solvent waste containing 2-Nitropropane as the only listed F001 to F005 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 to F005 solvent. | 2-Ethoxyethanol | 110-80-5 | BIOGD; 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 | 7440-43-9 | 0.69 | 0.11 mg/l TCLP |
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 mg/l TCLP | ||
| Silver | 7440-22-4 | NA | 0.14 mg/l TCLP | ||
| F007 | Spent cyanide plating bath solutions from electroplating operations | Cadmium | 7440-43-9 | NA | 0.11 mg/l TCLP |
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 mg/l TCLP | ||
| Silver | 7440-22-4 | NA | 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 | 7440-43-9 | NA | 0.11 mg/l TCLP |
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 mg/l TCLP | ||
| Silver | 7440-22-4 | NA | 0.14 mg/l TCLP | ||
| F009 | Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process | Cadmium | 7440-43-9 | NA | 0.11 mg/l TCLP |
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 mg/l TCLP | ||
| Silver | 7440-22-4 | NA | 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 | 590.0 |
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | NA | ||
| F011 | Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations | Cadmium | 7440-43-9 | NA | 0.11 mg/l TCLP |
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 mg/l TCLP | ||
| Silver | 7440-22-4 | NA | 0.14 mg/l TCLP | ||
| F012 | Quenching wastewater treatment sludges from metal heat treating operations where cyanides are used in the process | Cadmium | 7440-43-9 | NA | 0.11 mg/l TCLP |
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 mg/l TCLP | ||
| Silver | 7440-22-4 | NA | 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) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP |
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| 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 deivatives (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 hexa-chlorobenzenes under alkaline conditions (i.e., F026) | 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 | ||
| Pentachlorophenol | 87-86-5 | 0.089 | 7.4 | ||
| TCDDs (all Tetrachlorodibenzo-p-dioxins) | NA | 0.000063 | 0.001 | ||
| TCDFs (all Tetrachlorodibenzofurans) | NA | 0.000063 | 0.001 | ||
| 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 | 0.03 | 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, or wastes listed in rule 3745-51-31 or 3745-51-32 of the Administrative Code.) | all F024 wastes | NA | CMBST 11 | CMBST 11 |
| 2-Chloro-1,3-butadiene | 126-99-8 | 0.057 | 0.28 | ||
| 3-Chloropropylene | 107-05-1 | 0.036 | 30.0 | ||
| 1,1-Dichloroethane | 75-34-3 | 0.059 | 6.0 | ||
| 1,2-Dichloroethane | 107-06-2 | 0.21 | 6.0 | ||
| 1,2-Dichloropropane | 78-87-5 | 0.85 | 18.0 | ||
| cis-1,3-Dichloropropylene | 10061-01-5 | 0.036 | 18.0 | ||
| trans-1,3-Dichloropropylene | 10061-02-6 | 0.036 | 18.0 | ||
| bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28.0 | ||
| Hexachloroethane | 67-72-1 | 0.055 | 30.0 | ||
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 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 | 56-23-5 | 0.057 | 6.0 |
| 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 | ||
| Methylene chloride | 75-9-2 | 0.089 | 30.0 | ||
| 1,1,2-Trichloroethane | 79-00-5 | 0.054 | 6.0 | ||
| Trichloroethylene | 79-01-6 | 0.054 | 6.0 | ||
| Vinyl chloride | 75-01-4 | 0.27 | 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 | 56-23-5 | 0.057 | 6.0 | |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Hexachlorobenzene | 118-74-1 | 0.055 | 10.0 | ||
| Hexachlorobutadiene | 87-68-3 | 0.055 | 5.6 | ||
| Hexachloroethane | 67-72-1 | 0.055 | 30.0 | ||
| Methylene chloride | 75-9-2 | 0.089 | 30.0 | ||
| 1,1,2-Trichloroethane | 79-00-5 | 0.054 | 6.0 | ||
| Trichloroethylene | 79-01-6 | 0.054 | 6.0 | ||
| Vinyl chloride | 75-01-4 | 0.27 | 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) | 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 | ||
| Pentachlorophenol | 87-86-5 | 0.089 | 7.4 | ||
| TCDDs (all Tetrachlorodibenzo-p-dioxins) | NA | 0.000063 | 0.001 | ||
| TCDFs (all Tetrachlorodibenzofurans) | NA | 0.000063 | 0.001 | ||
| 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 | 0.03 | 7.4 | ||
| F028 | Residues resulting from the incineration or thermal treatment of soil contaminated with EPA hazardous waste numbers F020, F021, F023, F026, and F027. | 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 | ||
| Pentachlorophenol | 87-86-5 | 0.089 | 7.4 | ||
| TCDDs (all Tetrachlorodibenzo-p-dioxins) | NA | 0.000063 | 0.001 | ||
| TCDFs (all Tetrachlorodibenzofurans) | NA | 0.000063 | 0.001 | ||
| 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 | 0.03 | 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 previously used chlorophenolic formulations [except potentially cross-contaminated wastes that have had the F032 EPA hazardous waste number deleted in accordance with rule 3745-51-35 of the Administrative Code 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 pentachlorophenol. | Acenaphthene | 83-32-9 | 0.059 | 3.4 |
| Anthracene | 120-12-7 | 0.059 | 3.4 | ||
| Benz(a)anthracene | 56-55-3 | 0.059 | 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 | ||
| 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 | ||
| 2-4-Dimethyl phenol | 105-67-9 | 0.036 | 14.0 | ||
| Fluorene | 86-73-7 | 0.059 | 3.4 | ||
| Hexachlorodibenzo-p-dioxins | NA | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| Hexachlorodibenzofurans | NA | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| Indeno-(1,2,3-c,d)-pyrene | 193-39-5 | 0.0055 | 3.4 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Pentachlorodibenzo-p-dioxins | NA | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| Pentachlorodibenzofurans | NA | 0.000035 or CMBST 11 | 0.001 or CMBST 11 | ||
| Pentachlorophenol | 87-86-5 | 0.089 | 7.4 | ||
| Phenanthrene | 85-01-8 | 0.059 | 5.6 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Pyrene | 129-00-0 | 0.067 | 8.2 | ||
| Tetrachlorodibenzo-p-dioxins | NA | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| Tetrachlorodibenzofurans | NA | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| 2,3,4,6-Tetrachlorophenol | 58-90-2 | 0.03 | 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 | 0.6 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 | 83-32-9 | 0.059 | 3.4 |
| Anthracene | 120-12-7 | 0.059 | 3.4 | ||
| Benz(a)anthracene | 56-55-3 | 0.059 | 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 | ||
| 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 | ||
| Fluorene | 86-73-7 | 0.059 | 3.4 | ||
| Indeno(1,2,3-c,d)-pyrene | 193-39-5 | 0.0055 | 3.4 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenanthrene | 85-01-8 | 0.059 | 5.6 | ||
| Pyrene | 129-00-0 | 0.067 | 8.2 | ||
| Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP | ||
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 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 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 | 7440-38-2 | 1.4 | 5.0 mg/l TCLP |
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 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 paragraph (B)(2) of rule 3745-51-31 of the Administrative Code (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 | 83-32-9 | 0.059 | NA |
| Anthracene | 120-12-7 | 0.059 | 3.4 | ||
| Benzene | 71-43-2 | 0.14 | 10.0 | ||
| Benz(a)anthracene | 56-55-3 | 0.059 | 3.4 | ||
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28.0 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Di-n-butyl phthalate | 84-74-2 | 0.057 | 28.0 | ||
| Ethylbenzene | 100-41-4 | 0.057 | 10.0 | ||
| 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 | 10.0 | ||
| Xylenes- mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30.0 | ||
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Nickel | 7440-02-0 | NA | 11.0 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 paragraph (B)(2) of rule 3745-51-31 of the Administrative Code (including sludges and floats generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and F037, K048, and K051 wastes are not included in this listing. | Benzene | 71-43-2 | 0.14 | 10.0 |
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28.0 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Di-n-butyl phthalate | 84-74-2 | 0.057 | 28.0 | ||
| Ethylbenzene | 100-41-4 | 0.057 | 10.0 | ||
| 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 | 10.0 | ||
| Xylenes- mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30.0 | ||
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| 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 rules 3745-270-40 to 3745-270-49 of the Administrative Code. (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 | 208-96-8 | 0.059 | 3.4 |
| Acenaphthene | 83-32-9 | 0.059 | 3.4 | ||
| Acetone | 67-64-1 | 0.28 | 160.0 | ||
| Acetonitrile | 75-05-8 | 5.6 | NA | ||
| Acetophenone | 96-86-2 | 0.01 | 9.7 | ||
| 2-Acetylaminofluorine | 53-96-3 | 0.059 | 140.0 | ||
| Acrolein | 107-02-8 | 0.29 | NA | ||
| Acrylonitrile | 107-13-1 | 0.24 | 84.0 | ||
| Aldrin | 309-00-2 | 0.021 | 0.066 | ||
| 4-Aminobiphenyl | 92-67-1 | 0.13 | NA | ||
| Aniline | 62-53-3 | 0.81 | 14.0 | ||
| 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 | 10.0 | ||
| Benz(a)anthracene | 56-55-3 | 0.059 | 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 | ||
| 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 | 15.0 | ||
| Methyl bromide (Bromomethane) | 74-83-9 | 0.11 | 15.0 | ||
| 4-Bromophenyl phenyl ether | 101-55-3 | 0.055 | 15.0 | ||
| n-Butyl alcohol | 71-36-3 | 5.6 | 2.6 | ||
| Butyl benzyl phthalate | 85-68-7 | 0.017 | 28.0 | ||
| 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 | 16.0 | ||
| Chlorobenzene | 108-90-7 | 0.057 | 6.0 | ||
| Chlorobenzilate | 510-15-6 | 0.1 | NA | ||
| 2-Chloro-1,3-butadiene | 126-99-8 | 0.057 | NA | ||
| Chlorodibromomethane | 124-48-1 | 0.057 | 15.0 | ||
| 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 | 14.0 | ||
| Chloromethane (Methyl chloride) | 74-87-3 | 0.19 | 30.0 | ||
| 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 | 30.0 | ||
| 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-chloropropane | 96-12-8 | 0.11 | 15.0 | ||
| Ethylene dibromide (1,2-Dibromoethane) | 106-93-4 | 0.028 | 15.0 | ||
| Dibromomethane | 74-95-3 | 0.11 | 15.0 | ||
| 2,4-D (2,4-Dichlorophenoxyacetic acid) | 94-75-7 | 0.72 | 10.0 | ||
| 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 | 0.09 | 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 | 30.0 | ||
| 2,4-Dichlorophenol | 120-83-2 | 0.044 | 14.0 | ||
| 2,6-Dichlorophenol | 87-65-0 | 0.044 | 14.0 | ||
| 1,2-Dichloropropane | 78-87-5 | 0.85 | 18.0 | ||
| cis-1,3-Dichloropropylene | 10061-01-5 | 0.036 | 18.0 | ||
| trans-1,3-Dichloropropylene | 10061-02-6 | 0.036 | 18.0 | ||
| Dieldrin | 60-57-1 | 0.017 | 0.13 | ||
| Diethyl phthalate | 84-66-2 | 0.2 | 28.0 | ||
| 2,4-Dimethylaniline (2,4-xylidine) | 95-68-1 | 0.010 | 0.66 | ||
| 2,4-Dimethyl phenol | 105-67-9 | 0.036 | 14.0 | ||
| Dimethyl phthalate | 131-11-3 | 0.047 | 28.0 | ||
| Di-n-butyl phthalate | 84-74-2 | 0.057 | 28.0 | ||
| 1,4-Dinitrobenzene | 100-25-4 | 0.32 | 2.3 | ||
| 4,6-Dinitro-o-cresol | 534-52-1 | 0.28 | 160.0 | ||
| 2,4-Dinitrophenol | 51-28-5 | 0.12 | 160.0 | ||
| 2,4-Dinitrotoluene | 121-14-2 | 0.32 | 140.0 | ||
| 2,6-Dinitrotoluene | 606-20-2 | 0.55 | 28.0 | ||
| Di-n-octyl phthalate | 117-84-0 | 0.017 | 28.0 | ||
| Di-n-propylnitrosamine | 621-64-7 | 0.4 | 14.0 | ||
| 1,4-Dioxane | 123-91-1 | 12.0 | 170.0 | ||
| Diphenylamine (difficult to distinguish from diphenylnitrosamine) | 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 | 33.0 | ||
| Ethyl cyanide (Propanenitrile) | 107-12-0 | 0.24 | 360.0 | ||
| Ethyl benzene | 100-41-4 | 0.057 | 10.0 | ||
| Ethyl ether | 60-29-7 | 0.12 | 160.0 | ||
| bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28.0 | ||
| Ethyl methacrylate | 97-63-2 | 0.14 | 160.0 | ||
| Ethylene oxide | 75-21-8 | 0.12 | NA | ||
| Famfur | 52-85-7 | 0.017 | 15.0 | ||
| 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-HpCCD) | 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 | 10.0 | ||
| Hexachlorobutadiene | 87-68-3 | 0.055 | 5.6 | ||
| Hexachloro cyclopentadiene | 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 | 30.0 | ||
| Hexachloropropylene | 1888-71-7 | 0.035 | 30.0 | ||
| Indeno (1,2,3-c,d) pyrene | 193-39-5 | 0.0055 | 3.4 | ||
| Iodomethane | 74-88-4 | 0.19 | 65.0 | ||
| Isobutyl alcohol | 78-83-1 | 5.6 | 170.0 | ||
| 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 | 84.0 | ||
| 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 | 15.0 | ||
| 4,4-Methylene bis(2-chloroaniline) | 101-14-4 | 0.5 | 30.0 | ||
| Methylene chloride | 75-09-2 | 0.089 | 30.0 | ||
| Methyl ethyl ketone | 78-93-3 | 0.28 | 36.0 | ||
| Methyl isobutyl ketone | 108-10-1 | 0.14 | 33.0 | ||
| Methyl methacrylate | 80-62-6 | 0.14 | 160.0 | ||
| 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 | 28.0 | ||
| Nitrobenzene | 98-95-3 | 0.068 | 14.0 | ||
| 5-Nitro-0-toluidine | 99-55-8 | 0.32 | 28.0 | ||
| p-Nitrophenol | 100-02-7 | 0.12 | 29.0 | ||
| N-Nitrosodiethylamine | 55-18-5 | 0.4 | 28.0 | ||
| N-Nitrosodimethylamine | 62-75-9 | 0.4 | NA | ||
| N-Nitroso-di-n-butylamine | 924-16-3 | 0.4 | 17.0 | ||
| N-Nitrosomethyl ethylamine | 10595-95-6 | 0.4 | 2.3 | ||
| N-Nitrosomorpholine | 59-89-2 | 0.4 | 2.3 | ||
| N-Nitrosopiperidine | 100-75-4 | 0.013 | 35.0 | ||
| N-Nitrosopyrrolidine | 930-55-2 | 0.013 | 35.0 | ||
| 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (OCDD) | 3268-87-9 | 0.000063 | 0.0025 | ||
| 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) | 1336-36-3 | 0.1 | 10.0 | ||
| Pentachlorobenzene | 608-93-5 | 0.055 | 10.0 | ||
| PeCDDs (all Pentachlorodibenzo-p-dioxins) | NA | 0.000063 | 0.001 | ||
| PeCDDs (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 | 16.0 | ||
| 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 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 | 16.0 | ||
| Safrole | 94-59-7 | 0.081 | 22.0 | ||
| 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 | 14.0 | ||
| TCDDs (all Tetrachlorodibenzo-p-dioxins) | NA | 0.000063 | 0.001 | ||
| TCDDs (all Tetrachlorodibenzofurans) | NA | 0.000063 | 0.001 | ||
| 1,1,1,2-Tetrachloroethane | 630-20-6 | 0.057 | 6.0 | ||
| 1,1,2,2-Tetrachloroethane | 79-34-6 | 0.057 | 6.0 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| 2,3,4,6-Tetrachlorophenol | 58-90-2 | 0.03 | 7.4 | ||
| Toluene | 108-88-3 | 0.08 | 10.0 | ||
| Toxaphene | 8001-35-2 | 0.0095 | 2.6 | ||
| Bromoform (Tribromomethane) | 75-25-2 | 0.63 | 15.0 | ||
| 1,2,4-Trichlorobenzene | 120-82-1 | 0.055 | 19.0 | ||
| 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 | ||
| Trichloromono fluoromethane | 75-69-4 | 0.02 | 30.0 | ||
| 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-Trichlopropane | 96-18-4 | 0.85 | 30.0 | ||
| 1,1,2-Trichloro-1,2,2-trifluoroethane | 76-13-1 | 0.057 | 30.0 | ||
| 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 | 30.0 | ||
| 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 | 21.0 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 | 0.6 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | NA | ||
| Fluoride | 16964-48-8 | 35.0 | 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 | 11.0 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 | 14.0 | 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 creosotes and/or pentachlorophenol | 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 | 0.08 | 10.0 | ||
| Xylenes- mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30.0 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| K002 | Wastewater treatment sludge from the production of chrome yellow and orange pigments | Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP |
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| K003 | Wastewater treatment sludge from the production of molybdate orange pigments | Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP |
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| K004 | Wastewater treatment sludge from the production of zinc yellow pigments | Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP |
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| K005 | Wastewater treatment sludge from the production of chrome green pigments | Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP |
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| K006 | Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous) | Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP |
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated) | Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | |
| Lead | 7439-92-1 | 0.69 | NA | ||
| K007 | Wastewater treatment sludge from the production of iron blue pigments | Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP |
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| K008 | Oven residues from the production of chrome oxide green pigments | Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP |
| Lead | 7439-92-1 | 0.69 | 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 | 75-05-8 | 5.6 | 38.0 |
| Acrylonitrile | 107-13-1 | 0.24 | 84.0 | ||
| Acrylamide | 79-06-1 | 19.0 | 23.0 | ||
| Benzene | 71-43-2 | 0.14 | 10.0 | ||
| Cyanide (total) | 57-12-5 | 1.2 | 590.0 | ||
| K013 | Bottom stream from the acetonitrile column in the production of acrylonitrile | Acetonitrile | 75-05-8 | 5.6 | 38.0 |
| Acrylonitrile | 107-13-1 | 0.24 | 84.0 | ||
| Acrylamide | 79-06-1 | 19.0 | 23.0 | ||
| Benzene | 71-43-2 | 0.14 | 10.0 | ||
| Cyanide (total) | 57-12-5 | 1.2 | 590.0 | ||
| K014 | Bottoms from the acetonitrile purification column in the production of acrylonitrile | Acetonitrile | 75-05-8 | 5.6 | 38.0 |
| Acrylonitrile | 107-13-1 | 0.24 | 84.0 | ||
| Acrylamide | 79-06-1 | 19.0 | 23.0 | ||
| Benzene | 71-43-2 | 0.14 | 10.0 | ||
| Cyanide (total) | 57-12-5 | 1.2 | 590.0 | ||
| 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 | 0.08 | 10.0 | ||
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 mg/l TCLP | ||
| K016 | Heavy ends or distillation residues from the production of carbon tetrachloride | Hexachlorobenzene | 118-74-1 | 0.055 | 10.0 |
| Hexachlorobutadiene | 87-68-3 | 0.055 | 5.6 | ||
| Hexachloro cyclopentadiene | 77-47-4 | 0.057 | 2.4 | ||
| Hexachloroethane | 67-72-1 | 0.055 | 30.0 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| 1,1-Dichloroethane | 75-34-3 | 0.059 | 6.0 | ||
| 1,2-Dichloroethane | 107-06-2 | 0.21 | 6.0 | ||
| K017 | Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin | bis(2-Choloroethyl)ether | 111-44-4 | 0.033 | 6.0 |
| 1,2-Dichloropropane | 78-87-5 | 0.85 | 18.0 | ||
| 1,2,3-Trichloropropane | 96-18-4 | 0.85 | 30.0 | ||
| K018 | Heavy ends from the fractionation column in ethyl chloride production | Chloroethane | 75-00-3 | 0.27 | 6.0 |
| Chloromethane | 74-87-3 | 0.19 | 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 | 10.0 | ||
| Hexachlorobutadiene | 87-68-3 | 0.055 | 5.6 | ||
| Hexachloroethane | 67-72-1 | 0.055 | 30.0 | ||
| 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 thylene dichloride production | bis(2-Chloroethyl)ether | 111-44-4 | 0.033 | 6.0 |
| Chlorobenzene | 108-90-7 | 0.057 | 6.0 | ||
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| p-Dichlorobenzene | 106-46-7 | 0.09 | NA | ||
| 1,2-Dichloroethane | 107-06-2 | 0.21 | 6.0 | ||
| Fluorene | 86-73-7 | 0.059 | NA | ||
| Hexachloroethane | 67-72-1 | 0.055 | 30.0 | ||
| 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-Trichloroethane | 120-82-1 | 0.055 | 19.0 | ||
| 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 | 56-23-5 | 0.057 | 6.0 |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Antimony | 7440-36-0 | 1.9 | 1.15 mg/l TCLP | ||
| K022 | Distillation bottom tars from the production of phenol/acetone from cumene | Toluene | 108-88-3 | 0.08 | 10.0 |
| Acetophenone | 96-86-2 | 0.01 | 9.7 | ||
| Diphenylamine (difficult to distinguish from diphenylnitrosamine) | 122-39-4 | 0.92 | 13.0 | ||
| Diphenylnitrosamine (difficult to distinguish from diphenylamine) | 86-30-6 | 0.92 | 13.0 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 mg/l TCLP | ||
| K023 | Distillation light ends from the production of phthalic anhidride from naphthalene | Phthalic anhydride (measured as phthalic acid or terephthalic acid) | 100-21-0 | 0.055 | 28.0 |
| Phthalic anhydride (measured as phthalic acid or terephthalic acid) | 85-44-9 | 0.055 | 28.0 | ||
| K024 | Distillation bottoms from the production of phthalic anhidride from naphthalene | Phthalic anhydride (measured as phthalic acid or terephthalic acid) | 100-21-0 | 0.055 | 28.0 |
| Phthalic anhydride (measured as phthalic acid or terephthalic acid) | 85-44-9 | 0.055 | 28.0 | ||
| 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 | 75-34-3 | 0.059 | 6.0 |
| trans-1,2-Dichloroethylene | 156-60-5 | 0.054 | 30.0 | ||
| Hexachlorobutadiene | 87-68-3 | 0.055 | 5.6 | ||
| Hexachloroethane | 67-72-1 | 0.055 | 30.0 | ||
| 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 | 0.6 mg/l TCLP | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 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 | 0.09 | NA | ||
| Hexachlorobutadiene | 87-68-3 | 0.055 | 5.6 | ||
| Hexachloroethane | 67-72-1 | 0.055 | 30.0 | ||
| Hexachloropropylene | 1888-71-7 | NA | 30.0 | ||
| Pentachlorobenzene | 608-93-5 | NA | 10.0 | ||
| Pentachloroethane | 76-01-7 | NA | 6.0 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14.0 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| 1,2,4-Trichlorobenzene | 120-82-1 | 0.055 | 19.0 | ||
| 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 | Hexachloro cyclopentadiene | 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 | Hexachloro cyclopentadiene | 77-47-4 | 0.057 | 2.4 |
| K034 | Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane | Hexachloro cyclopentadiene | 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 | 0.08 | 10.0 | ||
| 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 diethylphosphorodithioic 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 | 0.09 | 6.0 | ||
| Pentachlorobenzene | 608-93-5 | 0.055 | 10.0 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14.0 | ||
| 1,2,4-Trichlorobenzene | 120-82-1 | 0.055 | 19.0 | ||
| K043 | 2,6-Dichlorophenol waste from the production of 2,4-D | 2,4-Dichlorophenol | 120-83-2 | 0.044 | 14.0 |
| 2,6-Dichlorophenol | 187-65-0 | 0.044 | 14.0 | ||
| 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 | 0.03 | 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 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 | ||
| 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 | 10.0 |
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28.0 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Di-n-butyl phthalate | 84-74-2 | 0.057 | 28.0 | ||
| Ethylbenzene | 100-41-4 | 0.057 | 10.0 | ||
| 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 | 0.08 | 10.0 | ||
| Xylenes- mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30.0 | ||
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Nickel | 7440-02-0 | NA | 11.0 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 | 10.0 | ||
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28.0 | ||
| 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 | 10.0 | ||
| 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 | 0.08 | 10.0 | ||
| Xylenes- mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30.0 | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Nickel | 7440-02-0 | NA | 11.0 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 | 590.0 | ||
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Nickel | 7440-02-0 | NA | 11.0 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 | 10.0 | ||
| Benzo(a)pyrene | 50-32-8 | 0.061 | 3.4 | ||
| bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28.0 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Di-n-butyl phthalate | 105-67-9 | 0.057 | 28.0 | ||
| Ethylbenzene | 100-41-4 | 0.057 | 10.0 | ||
| 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 | 10.0 | ||
| Xylenes- mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30.0 | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Nickel | 7440-02-0 | NA | 11.0 mg/l TCLP | ||
| K052 | Tank bottoms (leaded) from the petroleum refining industry | Benzene | 71-43-2 | 0.14 | 10.0 |
| 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 | 10.0 | ||
| 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 | 10.0 | ||
| Xylenes- mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30.0 | ||
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Lead | 7439-92-1 | 0.69 | NA | ||
| Nickel | 7440-02-0 | NA | 11.0 mg/l TCLP | ||
| K060 | Ammonia still lime sludge from coking operations | Benzene | 71-43-2 | 0.14 | 10.0 |
| 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 | 590.0 | ||
| 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 | 21.0 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 | 0.6 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 | 11.0 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 | 0.2 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 331X and 332X) | Chromium (total) | 7440-47-3 | 2.77 | 0.6 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 Emission control dust/sludge from secondary lead smelting- non-calcium sulfate (high lead) subcategory | Cadmium | 7440-43-9 | 0.69 | 0.11 mg/l TCLP |
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| NA | NA | NA | RLEAD | ||
| K071 | K071 (brine purification muds from the mercury cell process in chlorine production, where separate prepurified brine is not used) nonwastewaters that are residues from RMERC | Mercury | 7439-97-6 | NA | 0.2 mg/l TCLP |
| K071 (brine purification muds from the mercury cell process in chlorine production, where separate 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 diaphram 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 | 30.0 | ||
| 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 | 14.0 |
| Benzene | 71-43-2 | 0.14 | 10.0 | ||
| Cyclohexanone | 108-94-1 | 0.36 | NA | ||
| Diphenylamine (difficult to distinguish from diphenylnitrosamine) | 122-39-4 | 0.92 | 13.0 | ||
| Diphenylnitrosamine (difficult to distinguish from diphenylamine) | 86-30-6 | 0.92 | 13.0 | ||
| Nitrobenzene | 98-95-3 | 0.068 | 14.0 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 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 | 10.0 |
| 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 | 0.09 | 6.0 | ||
| Hexachlorobenzene | 118-74-1 | 0.055 | 10.0 | ||
| Total PCBs (sum of all PCB isomers, or all aroclors) | 1336-36-3 | 0.1 | 10.0 | ||
| Pentachlorobenzene | 608-93-5 | 0.055 | 10.0 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14.0 | ||
| 1,2,4-Trichlorobenzene | 120-82-1 | 0.055 | 19.0 | ||
| K086 | Solvent waste 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 | 160.0 |
| Acetophenone | 96-86-2 | 0.01 | 9.7 | ||
| bis(2-Ethylhexyl)phthalate | 117-81-7 | 0.28 | 28.0 | ||
| n-Butyl alcohol | 71-36-3 | 5.6 | 2.6 | ||
| Butylbenzyl phthalate | 85-68-7 | 0.017 | 28.0 | ||
| Cyclohexanone | 108-94-1 | 0.36 | NA | ||
| o-Dichlorobenzene | 95-50-1 | 0.088 | 6.0 | ||
| Diethyl phthalate | 84-66-2 | 0.2 | 28.0 | ||
| Dimethyl phthalate | 131-11-3 | 0.047 | 28.0 | ||
| Di-n-butyl phthalate | 84-74-2 | 0.057 | 28.0 | ||
| Di-n-octyl phthalate | 117-84-0 | 0.017 | 28.0 | ||
| Ethyl acetate | 141-78-6 | 0.34 | 33.0 | ||
| Ethylbenzene | 100-41-4 | 0.057 | 10.0 | ||
| Methanol | 67-56-1 | 5.6 | NA | ||
| Methyl ethyl ketone | 78-93-3 | 0.28 | 36.0 | ||
| Methyl isobutyl ketone | 108-10-1 | 0.14 | 33.0 | ||
| Methylene chloride | 75-09-2 | 0.089 | 30.0 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Nitrobenzene | 98-95-3 | 0.068 | 14.0 | ||
| Toluene | 108-88-33 | 0.08 | 10.0 | ||
| 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 | 30.0 | ||
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| K087 | Decanter tank tar from coking operations | Acenaphthylene | 208-96-8 | 0.059 | 3.4 |
| Benzene | 71-43-2 | 0.14 | 10.0 | ||
| 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 | 0.08 | 10.0 | ||
| Xylenes- mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30.0 | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP | ||
| K088 | Spent potliners from primary aluminum reduction | Acenaphthene | 83-32-9 | 0.059 | 3.4 |
| Anthracene | 120-12-7 | 0.059 | 3.4 | ||
| Benz(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 | 26.1 | ||
| Barium | 7440-39-3 | 1.2 | 21.0 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 | 0.6 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 | 11.0 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 | 590.0 | ||
| Cyanide (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| Fluoride | 16984-48-8 | 35.0 | NA | ||
| K093 | Distillation light ends from the production of phthalic anhidride from ortho-xylene | Phthalic anhydride (measured as phthalic acid or terephthalic acid) | 100-21-0 | 0.055 | 28.0 |
| Phthalic anhydride (measured as phthalic acid or terephthalic acid) | 85-44-9 | 0.055 | 28.0 | ||
| K094 | Distillation bottoms from the production of phthalic anhidride from ortho-xylene | Phthalic anhydride (measured as phthalic acid or terephthalic acid) | 100-21-0 | 0.055 | 28.0 |
| Phthalic anhydride (measured as phthalic acid or terephthalic acid) | 85-44-9 | 0.055 | 28.0 | ||
| K095 | Distillation bottoms from the production of 1,1,1-trichloroethane | Hexachloroethane | 67-72-1 | 0.055 | 30.0 |
| 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 | ||
| 1,1,2-Trichloroethane | 79-00-5 | 0.054 | 6.0 | ||
| Trichloroethylene | 79-01-6 | 0.054 | 6.0 | ||
| K096 | Heavy ends from the heavy end 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 | 19.0 | ||
| 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 | ||
| Hexachloro cyclopentadiene | 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 process wastewater from the production of 2,4-D | 2,4-Dichloro phenoxyacetic acid | 94-75-7 | 0.72 | 10.0 |
| 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 | 0.000063 | 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 | 0.11 mg/l TCLP |
| Chromium (total) | 7440-47-3 | 2.77 | 0.6 mg/l TCLP | ||
| Lead | 7439-92-1 | 0.69 | 0.75 mg/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 | 14.0 |
| 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 | Residues from the use of activated carbon for decolonization in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds | o-Nitrophenol | 88-75-5 | 0.028 | 13.0 |
| 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 | 14.0 |
| Benzene | 71-43-2 | 0.14 | 10.0 | ||
| 2,4-Dinitrophenol | 51-28-5 | 0.12 | 160.0 | ||
| Nitrobenzene | 98-95-3 | 0.068 | 14.0 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| K014 | Combined wastewater streams generated from nitrobenzene/aniline production | Aniline | 62-53-3 | 0.81 | 14.0 |
| Benzene | 71-43-2 | 0.14 | 10.0 | ||
| 2,4-Dinitrophenol | 51-28-5 | 0.12 | 160.0 | ||
| Nitrobenzene | 98-95-3 | 0.068 | 14.0 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| K105 | Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes | Benzene | 71-43-2 | 0.14 | 10.0 |
| 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 | 0.9 | 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 260.0 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 260.0 mg/kg total mercury that are residues from RMERC | Mercury | 7439-97-6 | NA | 0.02 mg/l TCLP | |
| Other K106 nonwastewaters that contain less than 260.0 mg/kg total mercury that 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 BIOGD 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 BIOGD 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 BIOGD 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 BIOGD fb CARBN | CMBST |
| K111 | Product washwaters from the production of dinitrotoluene via nitration of toluene | 2,4-Dinitrotoluene | 121-14-2 | 0.32 | 140.0 |
| 2,6-Dinitrotoluene | 606-20-2 | 0.55 | 28.0 | ||
| 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 BIOGD fb CARBN | CMBST |
| K113 | Condensed liquid light ends from the purification of toluenediamine via hydrogenation of dinitrotoluene | NA | NA | CARBN; or CMBST | CMBST |
| K114 | Vicinals from the purification 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 | 11.0 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 | 15.0 |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Ethylene dibromide (1,2-Dibromoethane) | 106-93-4 | 0.028 | 15.0 | ||
| 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 | 15.0 |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Ethylene dibromide (1,2-Dibromoethane) | 106-93-4 | 0.028 | 15.0 | ||
| K123 | Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylene bisdithiocarbamic acid and its salts | NA | NA | CMBST; or CHOXD fb (BIOGD or CARBN) | CMBST |
| K124 | Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts | NA | NA | CMBST; or CHOXD fb (BIOGD or CARBN) | CMBST |
| K125 | Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts | NA | NA | CMBST; or CHOXD fb (BIOGD or CARBN) | CMBST |
| K126 | Baghouse dust and floor sweepings in milling and packaging operations in the production or formulation of ethylenebisdithiocarbamic acid and its salts | NA | NA | CMBST; or CHOXD fb (BIOGD 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 | 15.0 |
| K132 | Spent absorbent and wastewater separator solids from the production of methyl bromide | Methyl bromide (Bromomethane) | 74-83-9 | 0.11 | 15.0 |
| K136 | Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene | Methyl bromide (Bromomethane) | 74-83-9 | 0.11 | 15.0 |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Ethylene dibromide (1,2-Dibromoethane) | 106-93-4 | 0.028 | 15.0 | ||
| 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 byproducts produced from coal. This listing does not include K087 (decanter tank tar sludge from coking operations). | Benzene | 71-43-2 | 0.14 | 10.0 |
| 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 tar or from the recovery of coke byproducts produced from coal | Benzene | 71-43-2 | 0.14 | 10.0 |
| 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 byproducts produced from coal | Benzene | 71-43-2 | 0.14 | 10.0 |
| 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 | ||
| 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 | 10.0 |
| 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 byproducts produced from coal | Benzene | 71-43-2 | 0.14 | 10.0 |
| 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 | 10.0 |
| 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 cola 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 | 30.0 | ||
| p-Dichlorobenzene | 106-46-7 | 0.09 | 6.0 | ||
| Hexachlorobenzene | 118-74-1 | 0.055 | 10.0 | ||
| Pentachlorobenzene | 608-93-5 | 0.055 | 10.0 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14.0 | ||
| Toluene | 108-88-3 | 0.08 | 10.0 | ||
| 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 | 30.0 | ||
| p-Dichlorobenzene | 106-46-7 | 0.09 | 6.0 | ||
| Hexachlorobenzene | 118-74-1 | 0.055 | 10.0 | ||
| Pentachlorobenzene | 608-93-5 | 0.055 | 10.0 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14.0 | ||
| 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 | 19.0 | ||
| 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 | 10.0 |
| Carbon tetrachloride | 56-23-5 | 0.057 | 6.0 | ||
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Hexachlorobenzene | 118-74-1 | 0.055 | 10.0 | ||
| Pentachlorobenzene | 608-93-5 | 0.055 | 10.0 | ||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.055 | 14.0 | ||
| Tetrachloroethylene | 127-18-4 | 0.056 | 6.0 | ||
| Toluene | 108-88-3 | 0.08 | 10.0 | ||
| K156 | Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.) | Acetonitrile | 75-05-8 | 5.6 | 1.8 |
| Acetophenone | 98-86-2 | 0.01 | 9.7 | ||
| Aniline | 62-53-3 | 0.81 | 14.0 | ||
| Benomyl | 17804-35-2 | 0.056 | 1.4 | ||
| Benzene | 71-43-2 | 0.14 | 10.0 | ||
| Carbaryl | 63-25-2 | 0.006 | 0.14 | ||
| Carbenzadim | 10605-21-7 | 0.056 | 1.4 | ||
| Carbofuran | 1563-66-2 | 0.006 | 0.14 | ||
| Carbosulfan | 55285-14-8 | 0.028 | 1.4 | ||
| 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 | ||
| Methomyl | 16752-77-5 | 0.028 | 0.14 | ||
| Methylene chloride | 75-09-2 | 0.089 | 30.0 | ||
| Methyl ethyl ketone | 78-93-3 | 0.28 | 36.0 | ||
| Naphthalene | 91-20-3 | 0.059 | 5.6 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| Pyridine | 110-86-1 | 0.014 | 16.0 | ||
| Toluene | 108-88-3 | 0.08 | 10.0 | ||
| Triethylamine | 121-44-8 | 0.081 | 1.5 | ||
| K157 | Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.) | Carbon tetrachloride | 56-23-5 | 0.057 | 6.0 |
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Chloromethane | 74-87-3 | 0.19 | 30.0 | ||
| Methomyl | 16752-77-5 | 0.028 | 0.14 | ||
| Methylene chloride | 75-09-2 | 0.089 | 30.0 | ||
| Methyl ethyl ketone | 78-93-3 | 0.28 | 36.0 | ||
| Pyridine | 110-86-1 | 0.014 | 16.0 | ||
| Triethylamine | 121-44-8 | 0.081 | 1.5 | ||
| K158 | Bag house dusts and filter/separation solids from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.) | Benomyl | 17804-35-2 | 0.056 | 1.4 |
| Benzene | 71-43-2 | 0.14 | 10.0 | ||
| Carbenzadim | 10605-21-7 | 0.056 | 1.4 | ||
| Carbofuran | 1563-66-2 | 0.006 | 0.14 | ||
| Carbosulfan | 55285-14-8 | 0.028 | 1.4 | ||
| Chloroform | 67-66-3 | 0.046 | 6.0 | ||
| Methylene chloride | 75-09-2 | 0.089 | 30.0 | ||
| Phenol | 108-95-2 | 0.039 | 6.2 | ||
| K159 | Organics from the treatment of thiocarbamate wastes 10 | Benzene | 71-43-2 | 0.14 | 10.0 |
| Butylate | 2008-41-5 | 0.042 | 1.4 | ||
| EPTC (Eptam) | 759-94-4 | 0.042 | 1.4 | ||
| Molinate | 2212-67-1 | 0.042 | 1.4 | ||
| Pebulate | 1114-71-2 | 0.042 | 1.4 | ||
| Vernolate | 1929-77-7 | 0.042 | 1.4 | ||
| 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 | 1.1511 |
| Arsenic | 7440-38-2 | 1.4 | 5.011 | ||
| Carbon disulfide | 75-15-0 | 3.8 | 4.811 | ||
| Dithiocarbamates (total) | 137-30-4 | 0.028 | 28.0 | ||
| Lead | 7439-92-1 | 0.69 | 0.7511 | ||
| Nickel | 7440-02-0 | 3.98 | 11.011 | ||
| Selenium | 7782-49-2 | 0.82 | 5.711 | ||
| 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 | 10.0 | ||
| 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 | 10.0 | ||
| Fluorene | 86-73-7 | 0.059 | 3.4 | ||
| Naphthalene | 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 | 0.08 | 10.0 | ||
| Xylene(s) (total) | 1330-20-7 | 0.32 | 30.0 | ||
| 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 | 10.0 | ||
| 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 | 10.0 | ||
| Fluorene | 86-73-7 | 0.059 | 3.4 | ||
| Indeno(1,2,3,-cd)pyrene | 193-39-5 | 0.0055 | 3.4 | ||
| Naphthalene | 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 | 0.08 | 10.0 | ||
| Xylene(s) (total) | 1330-20-7 | 0.32 | 30.0 | ||
| K171 | Spent 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 | 56-55-3 | 0.059 | 3.4 |
| Benzene | 71-43-2 | 0.14 | 10.0 | ||
| Chrysene | 218-01-9 | 0.059 | 3.4 | ||
| Ethyl benzene | 100-41-4 | 0.057 | 10.0 | ||
| Naphthalene | 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 | 0.08 | 10.0 | ||
| Xylene(s) (total) | 1330-20-7 | 0.32 | 30.0 | ||
| Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 mg/l TCLP | ||
| Vanadium | 7440-62-2 | 4.3 | 1.6 mg/l TCLP | ||
| Reactive sulfides | NA | DEACT | DEACT | ||
| K172 | Spent hydrorefining 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 | 71-43-2 | 0.14 | 10.0 |
| Ethyl benzene | 100-41-4 | 0.057 | 10.0 | ||
| Toluene (Methyl benzene) | 108-88-3 | 0.08 | 10.0 | ||
| Xylene(s) (total) | 1330-20-7 | 0.32 | 30.0 | ||
| Antimony | 7740-36-0 | 1.9 | 1.15 mg/l TCLP | ||
| Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 mg/l TCLP | ||
| Vanadium | 7440-62-2 | 4.3 | 1.6 mg/l TCLP | ||
| Reactive sulfides | NA | DEACT | 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-HpCCD) | 35822-46-9 | 0.000035 or CMBST 11 | 0.0025 or CMBST 11 |
| 1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF) | 67562-39-4 | 0.000035 or CMBST 11 | 0.0025 or CMBST 11 | ||
| 1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF) | 55673-89-7 | 0.000035 or CMBST 11 | 0.0025 or CMBST 11 | ||
| HxCDDs (all Hexachlorodibenzo-p-dioxins) | 34465-46-8 | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| HxCDFs (all Hexachlorodibenzofurans) | 55684-94-1 | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (OCDD) | 3268-87-9 | 0.000063 or CMBST 11 | 0.0025 or CMBST 11 | ||
| 1,2,3,4,6,7,8,9-Octachlorodibenzofuran (OCDF) | 39001-02-0 | 0.000063 or CMBST 11 | 0.005 or CMBST 11 | ||
| PeCDDs (all Pentachlorodibenzo-p-dioxins) | 36088-22-9 | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| PeCDFs (all Pentachlorodibenzofurans) | 30402-15-4 | 0.000035 or CMBST 11 | 0.001 or CMBST 11 | ||
| TCDDs (all Tetrachlorodibenzo-p-dioxins) | 41903-57-5 | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| TCDFs (all Tetrachlorodibenzofurans) | 55722-27-5 | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| 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. All K175 wastewaters | Mercury 12 | 7438-97-6 | NA | 0.025 mg/l TCLP |
| pH 12 | -- | NA | pH less than or equal to 6.0 | ||
| Mercury | 7438-97-6 | 0.15 | NA | ||
| K176 | Baghouse filters from the production of antimony oxide., including filters from the production of intermediates (e.g., antimony metal or crude antimony oxide). | Antimony | 7440-36-0 | 1.9 | 1.15 mg/l TCLP |
| Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP | ||
| Cadmium | 7440-43-9 | 0.69 | 0.11 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 | ||
| 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 | 7440-36-0 | 1.9 | 1.15 mg/l TCLP |
| Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP | ||
| Lead | 7439-92-1 | 0.069 | 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 CMBST 11 | 0.0025 or CMBST 11 |
| 1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF) | 67562-39-4 | 0.000035 or CMBST 11 | 0.0025 or CMBST 11 | ||
| 1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF) | 55673-89-7 | 0.000035 or CMBST 11 | 0.0025 or CMBST 11 | ||
| HxCDDs (all Hexachlorodibenzo-p-dioxins) | 34465-46-8 | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| HxCDFs (all Hexachlorodibenzofurans) | 55684-94-1 | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (OCDD) | 3268-87-9 | 0.000063 or CMBST 11 | 0.005 or CMBST 11 | ||
| 1,2,3,4,6,7,8,9-Octachlorodibenzofuran (OCDF) | 39001-02-0 | 0.000063 or CMBST 11 | 0.005 or CMBST 11 | ||
| PeCDDs (all Pentachlorodibenzo-p-dioxins | 36088-22-9 | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| PeCDFs (all Pentachlorodibenzofurans) | 30402-15-4 | 0.000035 or CMBST 11 | 0.001 or CMBST 11 | ||
| TCDDs (all Tetrachlorodibenzo-p-dioxins) | 41903-57-5 | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| TCDDs (all Tetrachlorodibenzofurans) | 55722-27-5 | 0.000063 or CMBST 11 | 0.001 or CMBST 11 | ||
| Thallium | 7440-28-0 | 1.4 | 0.20 mg/l TCLP | ||
| K181 | Nonwastewaters from the production of dyes and-or pigments (including nonwastewaters comingled 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 (C) of rule 3745-51-32 of the Administrative Code that are equal to or greater than the corresponding levels in paragraph (C) of rule 3745-51-32 of the Administrative Code as determined on a calendar year basis. | Aniline | 62-53-3 | 0.81 | 14.0 |
| o-Anisidine (2-Methoxyaniline) | 90-04-0 | 0.010 | 0.66 | ||
| 4-Chloroaniline | 106-47-8 | 0.46 | 16.0 | ||
| 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, and salts, when present at concentrations greater than 0.3 per cent | 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; BIOGD; 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 | 21.0 mg/l TCLP |
| Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 | ||
| Cyanide (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| P014 | Thiophenol (Benzene thiol) | Thiophenol (Benzene thiol) | 108-98-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P015 | Beryllium dust | 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 | 590.0 |
| Cyanide (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| P022 | Carbon disulfide | Carbon disulfide | 75-15-0 | 3.8 | CMBST |
| Carbon disulfide; alternate 6 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 | 16.0 |
| 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 | 590.0 |
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| P030 | Cyanides (soluble salts and complexes) | Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 |
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| 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-Cyclohexyl-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) | Diisopropylfluoro phosphate (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-Dimethylphen ethylamine | 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 | 160.0 |
| 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 | 160.0 |
| 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 | 35.0 | 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 | 590.0 |
| Cyanide (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| P064 | Isocyanic acid, ethyl ester | Isocyanic acid, ethyl ester | 624-83-0 | (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 260.0 mg/kg total mercury | Mercury | 7439-97-6 | NA | RMERC | |
| Mercury fulminate nonwastewaters that are residues from RMERC and contain less than 260.0 mg/kg total mercury | Mercury | 7439-97-6 | NA | 0.2 mg/l TCLP | |
| Mercury fulminate nonwastewaters that are incinerator residues and contain less than 260.0 mg/kg total mercury | Mercury | 7439-97-6 | NA | 0.25 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; BIOGD; 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 | 11.0 mg/l TCLP |
| P074 | Nickel cyanide | Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 |
| Cyanide (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| Nickel | 7440-02-0 | 3.98 | 11.0 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 | 28.0 |
| P078 | Nitrogen dioxide | Nitrogen dioxide | 10102-44-0 | ADGAS | ADGAS |
| P081 | Nitroglycerin | Nitroglycerin | 55-63-0 | CHOXD; CHRED; CARBN; BIOGD; or CMBST | CHOXD; CHRED; or CMBST |
| P082 | N-Nitrosodimethylamine | N-Nitrosodimethylamine | 62-75-9 | 0.4 | 2.3 |
| P084 | N-Nitrosomethylvinylamine | N-Nitrosomethylvinylamine | 4549-40-0 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P085 | Octamethylpyrophosphoramide | Octamethyl pyrophosphoramide | 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 260.0 mg/kg total mercury | Mercury | 7439-97-6 | NA | RMERC | |
| Phenyl mercuric acetate nonwastewaters that are residues from RMERC and contain less than 260.0 mg/kg total mercury | Mercury | 7439-97-6 | NA | 0.2 mg/l TCLP | |
| Phenyl mercuric acetate nonwastewaters that are incinerator residues and contain less than 260.0 mg/kg total mercury | Mercury | 7439-97-6 | NA | 0.25 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 | 15.0 |
| P098 | Potassium cyanide | Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 |
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| P099 | Potassium silver cyanide | Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 |
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| Silver | 7440-22-4 | 0.43 | 0.14 mg/l TCLP | ||
| P101 | Ethyl cyanide (Propanenitrile) | Ethyl cyanide (Propanenitrile) | 107-12-0 | 0.24 | 360.0 |
| 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 | 590.0 |
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| Silver | 7440-22-4 | 0.43 | 0.14 mg/l TCLP | ||
| P105 | Sodium azide | Sodium azide | 26628-22-8 | CHOXD; CHRED; CARBN; BIOGD; or CMBST | CHOXD; CHRED; or CMBST |
| P106 | Sodium cyanide | Cyanides (total) 7 | 57-12-5 | 1.2 | 590.0 |
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| P108 | Strychnine and salts | Strychnine and salts | 57-24-9 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| P109 | Tetraethyldithiopyrophosphate | Tetraethyldithio pyrophosphate | 3689-24-5 | CARBN; or CMBST | CMBST |
| P110 | Tetraethyl lead | Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP |
| P111 | Tetraethylpyrophosphate | Tetraethyl pyrophosphate | 107-49-3 | CARBN; or CMBST | CMBST |
| P112 | Tetranitromethane | Tetranitromethane | 509-14-8 | CHOXD; CHRED; CARBN; BIOGD; 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 | 590.0 |
| Cyanides (amenable) 7 | 57-12-5 | 0.86 | 30.0 | ||
| P122 | Zinc phosphide Zn3P2, when present at concentrations greater than 10.0 per cent | Zinc phosphide | 1314-84-7 | CHOXD; CHRED; or CMBST | CHOXD; CHRED; or CMBST |
| P123 | Toxaphene | Toxaphene | 8001-35-2 | 0.0095 | 2.6 |
| P127 | Carbofuran | Carbofuran | 1563-66-2 | 0.006 | 0.14 |
| P128 | Mexacarbate | Mexacarbate | 315-18-4 | 0.056 | 1.4 |
| P185 | Tirpate 10 | Tirpate | 26419-73-8 | 0.056 | 0.28 |
| P188 | Physostigmine salicylate | Physostigmine salicylate | 57-64-7 | 0.056 | 1.4 |
| P189 | Carbosulfan | Carbosulfan | 55285-14-8 | 0.028 | 1.4 |
| P190 | Metolcarb | Metolcarb | 1129-41-5 | 0.056 | 1.4 |
| P191 | Dimetilan 10 | Dimetilan | 644-64-4 | 0.056 | 1.4 |
| P192 | Isolan 10 | Isolan | 119-38-0 | 0.056 | 1.4 |
| P194 | Oxamyl | Oxamyl | 23135-22-0 | 0.056 | 0.28 |
| P196 | Manganese dimethyldithiocarbamate | Dithiocarbamates (total) | NA | 0.028 | 28.0 |
| P197 | Formparanate 10 | Formparanate | 17702-57-7 | 0.056 | 1.4 |
| P198 | Formetanate hydrochloride | Formetanate hydrochloride | 23422-53-9 | 0.056 | 1.4 |
| P199 | Methiocarb | Methiocarb | 2032-65-7 | 0.056 | 1.4 |
| P201 | Promecarb | Promecarb | 2631-37-0 | 0.056 | 1.4 |
| P202 | m-Cumenyl methylcarbamate | m-Cumenyl methylcarbamate | 64-00-6 | 0.056 | 1.4 |
| P203 | Aldicarb sulfone | Aldicarb sulfone | 1646-88-4 | 0.056 | 0.28 |
| P204 | Physostigmine | Physostigmine | 57-47-6 | 0.056 | 1.4 |
| P205 | Ziram | Dithiocarbamates (total) | NA | 0.028 | 28.0 |
| U001 | Acetaldehyde | Acetaldehyde | 75-07-0 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U002 | Acetone | Acetone | 67-64-1 | 0.28 | 160.0 |
| U003 | Acetonitrile | Acetonitrile | 75-05-8 | 5.6 | CMBST |
| Acetonitrile; alternate 6 standard for nonwastewaters only | 75-05-8 | NA | 38.0 | ||
| U004 | Acetophenone | Acetophenone | 98-86-2 | 0.01 | 9.7 |
| U005 | 2-Acetylaminofluorene | 2-Acetylaminofluorene | 53-96-3 | 0.059 | 140.0 |
| 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 | 84.0 |
| 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 | 14.0 |
| 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 | 10.0 |
| 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; BIOGD; 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 | Chloraphazine | Chloraphazine | 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 | 28.0 |
| U029 | Methyl bromide (Bromomethane) | Methyl bromide (Bromomethane) | 74-83-9 | 0.11 | 15.0 |
| U030 | 4-Bromophenyl phenyl ether | 4-Bromophenyl phenyl ether | 101-55-3 | 0.055 | 15.0 |
| U031 | n-Butyl alcohol | n-Butyl alcohol | 71-36-3 | 5.6 | 2.6 |
| U032 | Calcium chromate | Chromium (total) | 7440-47-3 | 2.77 | 0.6 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 | 0.1 | CMBST |
| U039 | p-Chloro-m-cresol | p-Chloro-m-cresol | 59-50-7 | 0.018 | 14.0 |
| 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 | 30.0 |
| 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-Cloro-o-toluidine hydrochloride | 4-Cloro-o-toluidine hydrochloride | 3165-93-3 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U050 | Chrysene | Chrysene | 2218-01-9 | 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 | 0.08 | 10.0 | ||
| Xylenes- mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30.0 | ||
| 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; alternate 6 standard 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-chloropropane | 96-12-8 | 0.11 | 15.0 |
| U067 | Ethylene dibromide (1,2-Dibromoethane) | Ethylene dibromide (1,2-Dibromoethane) | 106-93-4 | 0.028 | 15.0 |
| U068 | Dibromomethane | Dibromomethane | 74-95-3 | 0.11 | 15.0 |
| U069 | Di-n-butyl phthalate | Di-n-butyl phthalate | 84-74-2 | 0.057 | 28.0 |
| 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 | 0.09 | 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 | 30.0 |
| U080 | Methylene chloride | Methylene chloride | 75-09-2 | 0.089 | 30.0 |
| U081 | 2,4-Dichlorophenol | 2,4-Dichlorophenol | 120-83-2 | 0.044 | 14.0 |
| U082 | 2,6-Dichlorophenol | 2,6-Dichlorophenol | 87-65-0 | 0.044 | 14.0 |
| U083 | 1,2-Dichloropropane | 1,2-Dichloropropane | 78-87-5 | 0.85 | 18.0 |
| U084 | 1,3-Dichloropropylene | cis-1,3-Dichloropropylene | 10061-01-5 | 0.036 | 18.0 |
| trans-1,3-Dichloropropylene | 10061-02-6 | 0.036 | 18.0 | ||
| 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; BIOGD; 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 | 0.2 | 28.0 |
| 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-Dimethylamino azobenzene | 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; BIOGD; 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; BIOGD; or CMBST | CHOXD; CHRED; or CMBST |
| U099 | 1,2-Dimethylhydrazine | 1,2-Dimethylhydrazine | 540-73-8 | CHOXD; CHRED; CARBN; BIOGD; or CMBST | CHOXD; CHRED; or CMBST |
| U101 | 2,4-Dimethylphenol | 2,4-Dimethylphenol | 105-67-9 | 0.036 | 14.0 |
| U102 | Dimethyl phthalate | Dimethyl phthalate | 131-11-3 | 0.047 | 28.0 |
| U103 | Dimethyl sulfate | Dimethyl sulfate | 77-78-1 | CHOXD; CHRED; CARBN; BIOGD; or CMBST | CHOXD; CHRED; or CMBST |
| U105 | 2,4-Dinotrotoluene | 2,4-Dinotrotoluene | 121-14-2 | 0.32 | 140.0 |
| U106 | 2,6-Dinotrotoluene | 2,6-Dinotrotoluene | 606-20-2 | 0.55 | 28.0 |
| U107 | Di-n-octyl- phthalate | Di-n-octyl- phthalate | 117-84-0 | 0.017 | 28.0 |
| U108 | 1,4-Dioxane | 1,4-Dioxane | 123-91-1 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| 1,4-Dioxane; alternate 6 standard for nonwastewaters only | 123-91-1 | 12.0 | 170.0 | ||
| U109 | 1,2-Diphenylhydrazine | 1,2-Diphenylhydrazine | 122-66-7 | CHOXD; CHRED; CARBN; BIOGD; or CMBST | CHOXD; CHRED; or CMBST |
| 1,2-Diphenylhydrazine; alternate 6 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 | 0.4 | 14.0 |
| U112 | Ethyl acetate | Ethyl acetate | 141-78-6 | 0.34 | 33.0 |
| U113 | Ethyl acrylate | Ethyl acrylate | 140-88-5 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U114 | Ethylenebisdithiocarbamic acid salts and esters | Ethylenebis dithiocarbamic 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; alternate 6 standard 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 | 160.0 |
| U118 | Ethyl methacrylate | Ethyl methacrylate | 97-63-2 | 0.14 | 160.0 |
| 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 | Trichloromono fluoromethane | 75-69-4 | 0.02 | 30.0 |
| 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 | 10.0 |
| 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 | Hexachloro cyclopentadiene | 77-47-4 | 0.057 | 2.4 |
| U131 | Hexachloroethane | Hexachloroethane | 67-72-1 | 0.055 | 30.0 |
| U132 | Hexachlorophene | Hexachlorophene | 70-30-4 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U133 | Hydrazine | Hydrazine | 302-01-2 | CHOXD; CHRED; CARBN; BIOGD; or CMBST | CHOXD; CHRED; or CMBST |
| U134 | Hydrogen fluoride | Fluoride (measured in wastewaters only) | 7664-39-3 | 35.0 | 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-cd)pyrene | Indeno(1,2,3-cd)pyrene | 193-39-5 | 0.0055 | 3.4 |
| U138 | Iodomethane | Iodomethane | 74-88-4 | 0.19 | 65.0 |
| U140 | Isobutyl alcohol | Isobutyl alcohol | 78-83-1 | 5.6 | 170.0 |
| 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 | Malonitrile | Malonitrile | 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 260.0 mg/kg total mercury | Mercury | 7439-97-6 | NA | RMERC |
| U151 (mercury) nonwastewaters that contain less than 260.0 mg/kg total mercury and that are residues from RMERC only | Mercury | 7439-97-6 | NA | 0.2 mg/l TCLP | |
| U151 (mercury) nonwastewaters that contain less than 260.0 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 | 84.0 |
| 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; alternate 6 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 | 15.0 |
| U158 | 4,4'-Methylene bis(2-chloroaniline) | 4,4'-Methylene bis(2-chloroaniline) | 101-14-4 | 0.5 | 30.0 |
| U159 | Methyl ethyl ketone | Methyl ethyl ketone | 78-93-3 | 0.28 | 36.0 |
| U160 | Methyl ethyl ketone peroxide | Methyl ethyl ketone peroxide | 1338-23-4 | CHOXD; CHRED; CARBN; BIOGD; or CMBST | CHOXD; CHRED; or CMBST |
| U161 | Methyl isobutyl ketone | Methyl isobutyl ketone | 108-10-1 | 0.14 | 33.0 |
| U162 | Methyl methacrylate | Methyl methacrylate | 80-62-6 | 0.14 | 160.0 |
| 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-Naphthylamine | 1-Naphthylamine | 134-32-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U168 | 2-Naphthylamine | 2-Naphthylamine | 91-59-8 | 0.52 | CMBST |
| U169 | Nitrobenzene | Nitrobenzene | 98-95-3 | 0.068 | 14.0 |
| U170 | p-Nitrophenol | p-Nitrophenol | 100-02-7 | 0.12 | 29.0 |
| 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 | 0.4 | 17.0 |
| U173 | N-Nitrosodiethanolamine | N-Nitrosodiethanolamine | 1116-54-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U174 | N-Nitrosodiehtylamine | N-Nitrosodiehtylamine | 55-18-5 | 0.4 | 28.0 |
| 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 | 35.0 |
| U180 | N-Nitrosopyrrolidine | N-Nitrosopyrrolidine | 930-55-2 | 0.013 | 35.0 |
| U181 | 5-Nitro-o-toluidine | 5-Nitro-o-toluidine | 99-55-8 | 0.32 | 28.0 |
| U182 | Paraldehyde | Paraldehyde | 123-63-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U183 | Pentachlorobenzene | Pentachlorobenzene | 608-93-5 | 0.055 | 10.0 |
| U184 | Pentachloroethane | Pentachloroethane | 76-01-7 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| Pentachloroethane; alternate 6 standards 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 | 16.0 |
| 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 | 28.0 |
| Phthalic anhydride (measured as phthalic acid or terephthalic acid) | 85-44-9 | 0.055 | 28.0 | ||
| 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 | 16.0 |
| 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 |
| U202 | Saccharin and salts | Saccharin | 81-07-2 | (WETOX or CHOXD) fb CARBN; or CMBST | CMBST |
| U203 | Safrole | Safrole | 94-59-7 | 0.081 | 22.0 |
| 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 | 14.0 |
| 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 | 79-34-6 | 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 | 0.08 | 10.0 |
| 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 | 15.0 |
| 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 | 0.1 |
| 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 | 30.0 |
| U240 | 2,4-D (2,4-Dichlorophenoxyacetic acid) | 2,4-D (2,4-Dichlorophenoxyacetic acid) | 94-75-7 | 0.72 | 10.0 |
| 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 | 30.0 |
| 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, and salts, when present at concentrations of 0.3 per cent or less | Warfarin | 81-81-2 | x | CMBST |
| U249 | Zinc phosphide, Zn3P2, when present at concentrations of 10.0 per cent or less | Zinc phosphide | 1314-84-7 | CHOXD; CHRED; or CMBST | CHOXD; CHRED; or CMBST |
| U271 | Benomyl | Benomyl | 17804-35-2 | 0.056 | 1.4 |
| U278 | Bendiocarb | Bendiocarb | 22781-23-3 | 0.056 | 1.4 |
| U279 | Carbaryl | Carbaryl | 63-25-2 | 0.006 | 0.14 |
| U280 | Barban | Barban | 101-27-9 | 0.056 | 1.4 |
| U328 | o-Toluidine | o-Toluidine | 95-53-4 | CMBST; or CHOXD fb (BIOGD or CARBN); or BIOGD fb CARBN | CMBST |
| U353 | p-Toluidine | p-Toluidine | 106-49-0 | CMBST; or CHOXD fb (BIOGD or CARBN); or BIOGD fb CARBN | CMBST |
| U359 | 2-Ethoxyethanol | 2-Ethoxyethanol | 110-80-5 | CMBST; or CHOXD fb (BIOGD or CARBN); or BIOGD fb CARBN | CMBST |
| U364 | Bendiocarb phenol 10 | Bendiocarb phenol | 22961-82-6 | 0.056 | 1.4 |
| U367 | Carbofuran phenol | Carbofuran phenol | 1563-38-8 | 0.056 | 1.4 |
| U372 | Carbenzadim | Carbenzadim | 10605-21-7 | 0.056 | 1.4 |
| U373 | Propham | Propham | 122-42-9 | 0.056 | 1.4 |
| U387 | Prosulfocarb | Prosulfocarb | 52888-80-9 | 0.042 | 1.4 |
| U389 | Triallate | Triallate | 2303-17-5 | 0.042 | 1.4 |
| U394 | A2213 10 | A2213 | 30558-43-1 | 0.042 | 1.4 |
| U395 | Diethylene glycol, dicarbamate 10 | Diethylene glycol, dicarbamate | 5952-26-1 | 0.056 | 1.4 |
| U404 | Triethylamine | Triethylamine | 121-44-8 | 0.081 | 1.5 |
| U409 | Thiophanate-methyl | Thiophanate-methyl | 23564-05-8 | 0.056 | 1.4 |
| U410 | Thiodicarb | Thiodicarb | 59669-26-0 | 0.019 | 1.4 |
| U411 | Propoxur | Propoxur | 114-26-1 | 0.056 | 1.4 |
| Footnotes: | |||||
| NA NA means not applicable. | |||||
| 1 The waste descriptions provided in this table do not replace waste descriptions in Chapter 3745-51 of the Administrative Code. Descriptions of treatment/regulatory subcategories are provided, as needed, to distinguish between applicability of different standards. | |||||
| 2 CAS means chemical abstract services. When the EPA hazardous waste number and/or regulated constituents are described as a combination of a chemical with it's 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. | |||||
| 4 All treatment standards expressed as a technology code or combination of technology codes are explained in detail in the table in rule 3745-270-42 of the Administrative Code. | |||||
| 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 rules 3745-57-40 to 3745-57-51 or 3745-68-40 to 3745-68-52 of the Administrative Code, 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 (D) of this rule. 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 method 9012B found in "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,", U.S. EPA publication SW-846 with a sample size of ten grams and a distillation time of one hour and fifteen minutes. | |||||
| 8 These wastes, when rendered nonhazardous and then subsequently managed in Clean Water Act (CWA), or CWA-equivalent systems, are not subject to treatment standards. [See paragraphs (C)(3) and (C)(4) of rule 3745-270-01 of the Administrative Code.] | |||||
| 9 These wastes, when rendered nonhazardous and then subsequently injected in a "Class I SDWA" well are not subject to treatment standards. [See 40 CFR 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 described by the technology code CMBST in the table in rule 3745-270-42 of the Administrative Code, for nonwastewaters; and, biodegradation as described by the technology code BIOGD, carbon adsorption as described by the technology code CARBN, chemical oxidation as described by the technology code CHOXD, or combustion as described by the technology code CMBST in the table in rule 3745-270-42 of the Administrative Code, for wastewaters. | |||||
| 11 For these wastes, the definition of CMBST is limited to: (1) combustion units operating under Chapter 3745-266 of the Administrative Code, (2) combustion units permitted under rules 3745-57-40 to 3745-57-51 of the Administrative Code, or (3) combustion units operating under rules 3745-68-40 to 3745-68-52 of the Administrative Code, which have obtained a determination of equivalent treatment under paragraph (B) of rule 3745-270-42 of the Administrative Code. | |||||
| 12 Disposal of K175 wastes that have complied with all applicable treatment standards in this rule must also be macroencapsulated in accordance with the table in rule 3745-270-45 of the Administrative Code unless the waste is placed in: (1) A permitted hazardous waste landfill containing only K175 wastes that meet all applicable treatment standards in this rule; or (2) A dedicated permitted hazardous waste landfill cell in which all other wastes being co-disposed are at pH less than or equal to 6.0. | |||||
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled "Incorporated by reference."
Effective:
03/17/2012
R.C.
119.032 review dates: Exempt
Promulgated Under:
119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/30/1989, 02/11/1992, 09/02/1997, 12/07/2000, 02/08/2005,
02/16/2009, 09/05/2010
3745-270-42
Treatment standards expressed as specified technologies.
(A) The following wastes in the table in rule 3745-270-40 of the Administrative Code"Treatment Standards for Hazardous Wastes," 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 in this rule.






(B) Any person may submit an application to the director demonstrating that an alternative treatment method can achieve a measure of performance equivalent to that achieved by methods specified in paragraphs (A), (C), and (D) of this rule for wastes or specified in the table in rule 3745-270-45 of the Administrative Code for hazardous debris. The applicant must submit information demonstrating that his 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 administrator may approve the use of the alternative treatment method if he finds that the alternative treatment method provides a measure of performance equivalent to that achieved by methods specified in paragraphs (A), (C), and (D) of this rule for wastes or in the table in rule 3745-270-45 of the Administrative Code for hazardous debris. Any approval must be stated in writing and may contain such provisions and conditions as the director deems appropriate. The person to whom such approval is issued must comply with all limitations contained in such a determination.
(C) As an alternative to the otherwise applicable treatment standards in rules 3745-270-40 to 3745-270-49 of the Administrative Code, lab packs are eligible for land disposal provided the following requirements are met:
(1) The lab packs comply with the applicable provisions of rules 3745-57-16 and 3745-68-16 of the Administrative Code;
(2) The lab pack does not contain any ofthe wastes listed in appendix I to this rule;
(3) The lab packs are incinerated in accordance with the requirements of rules 3745-57-40 to 3745-57-51 or 3745-68-40 to 3745-68-52 of the Administrative Code; and
(4) 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 rules 3745-270-40 to 3745-270-49 of the Administrative Code.
(D) Radioactive hazardous mixed wastes are subject to the treatment standards in rule 3745-270-40 of the Administrative Code. 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 hazardous waste number) applies. Hazardous debris containing radioactive waste is subject to the treatment standards specified in rule 3745-270-45 of the Administrative Code.
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled"Incorporated by reference."]
Effective:
09/05/2010
R.C.
119.032 review dates:
04/14/2010 and
08/25/2014
Promulgated
Under: 119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/30/1989, 06/29/1990, 02/11/1992, 09/02/1997, 12/07/2000,
03/13/2002, 12/07/2004
3745-270-44
Variance from a treatment standard.
(A) Where the treatment standard is expressed as a concentration in a waste or waste extract and a waste cannot be treated to the specified level, or where the treatment technology is not appropriate to the waste, the generator or treatment facility may petition the administrator pursuant to 40 CFR 268.44 for a variance.
(B) Ohio EPA will recognize the administrator's decision to grant or deny a variance under 40 CFR 268.44.
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled "Incorporated by reference."]
Effective:
03/17/2012
R.C.
119.032 review dates:
11/30/2011 and
08/25/2016
Promulgated
Under: 119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/30/1989, 02/11/1992, 12/07/2000
3745-270-45
Treatment standards for hazardous debris.
(A) Treatment standards. Hazardous debris must be treated prior to land disposal as follows unless Ohio EPA determines under paragraph (F)(2) of rule 3745-51-03 of the Administrative Code that the debris is no longer contaminated with hazardous waste or the debris is treated to the waste-specific treatment standard provided in rules 3745-270-40 to 3745-270-49 of the Administrative Code for the waste contaminating the debris:
(1) General. Hazardous debris must be treated for each "contaminant subject to treatment" defined by paragraph (B) of this rule using the technology or technologies identified in the table in this rule.
(2) Characteristic debris. Hazardous debris that exhibits the characteristic of ignitability, corrosivity, or reactivity identified under rules 3745-51-21, 3745-51-22, and 3745- 51-23 of the Administrative Code, respectively, must be deactivated by treatment using one of the technologies identified in the table in this rule.
(3) Mixtures of debris types. The treatment standards in the table in this rule 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.
(4) Mixtures of contaminant types. Debris that is contaminated with two or more contaminants subject to treatment identified under paragraph (B) of this rule must be treated for each contaminant using one or more treatment technologies identified in the table in this rule. If an immobilization technology is used in a treatment train, it must be the last treatment technology used.
(5) Waste polychlorinated biphenyls (PCBs). Hazardous debris that is also a waste PCB under 40 CFR Part 761 is subject to the requirements of either 40 CFR Part 761 or the requirements of this rule, whichever are more stringent.
(B) 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:
(1) Toxicity characteristic debris. The contaminants subject to treatment for debris that exhibits the toxicity characteristic under rule 3745-51-24 of the Administrative Code are those extraction procedure constituents for which the debris exhibits the toxicity characteristic.
(2) 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 rule 3745-270-40 of the Administrative Code.
(3) Cyanide reactive debris. Hazardous debris that is reactive because of cyanide must be treated for cyanide.
(C) Conditioned exclusion of treated debris. Hazardous debris that has been treated using one of the extraction or destruction technologies specified in the table in this rule, and that does not exhibit a characteristic of hazardous waste identified in rules 3745-51-20 to 3745- 51-24 of the Administrative Code after treatment, is not a hazardous waste and need not be managed in a permitted hazardous waste facility. Hazardous debris contaminated with a listed waste that is treated by an immobilization technology specified in the table in this rule is a hazardous waste and must be managed in a permitted hazardous waste facility.
(D) Treatment residuals.
(1) General requirements. Except as provided by paragraphs (D)(2) and (D)(4) of this rule:
(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 rules 3745-270-40 to 3745- 270-49 of the Administrative Code for the waste contaminating the debris.
(2) 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 (B) of this rule must be deactivated prior to land disposal and is not subject to the waste-specific treatment standards of rules 3745-270-40 to 3745-270-49 of the Administrative Code.
(3) Cyanide-reactive debris. Residue from the treatment of debris that is reactive because of cyanide must meet the standards for D003 in "Treatment Standards for Hazardous Wastes" in rule 3745-270-40 of the Administrative Code.
(4) Ignitable nonwastewater residue. Ignitable nonwastewater residue containing equal to or greater than ten per cent total organic carbon is subject to the technology specified in the treatment standard for D001: ignitable liquids.
(5) Residue from spalling. Layers of debris removed by spalling are hazardous debris that remain subject to the treatment standards of this rule.










[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled"Incorporated by reference."]
Effective:
09/05/2010
R.C.
119.032 review dates: Exempt
Promulgated Under:
119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/07/2000, 12/07/2004
3745-270-48
Universal treatment standards.
(A) The table in this rule identifies the hazardous constituents, along with the nonwastewater and wastewater treatment standard levels, that are used to regulate most prohibited hazardos wastes with numerical limits. For determining compliance with treatment standards for underlying hazardous constituents as defined in rule 3745-270-02 of the Administrative Code, 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 table in this rule.











(B) Reserved.
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled"Incorporated by reference."]
Effective:
09/05/2010
R.C.
119.032 review dates:
04/14/2010 and
08/25/2014
Promulgated
Under: 119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/07/2000, 12/07/2004, 02/16/2009
3745-270-49
Alternative land disposal restriction treatment standards for contaminated soil.
(A) Applicability. You must comply with land disposal restrictions (LDRs) contained in Chapter 3745-270 of the Administrative Code 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:

(B) Prior to land disposal, contaminated soil identified by paragraph (A) of this rule as needing to comply with LDRs must be treated according to the applicable treatment standards specified in paragraph (C) of this rule or according to the universal treatment standards specified in rule 3745-270-48 of the Administrative Code 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 (C) of this rule and the universal treatment standards may be modified through a treatment variance approved in accordance with rule 3745-270-44 of the Administrative Code.
(C) Treatment standards for contaminated soils. Prior to land disposal, contaminated soil identified by paragraph (A) of this rule as needing to comply with LDRs must be treated according to all the standards specified in paragraphs (C) to (C)(3)(b) of this rule or according to the universal treatment standards specified in rule 3745-270-48 of the Administrative Code.
(1) All soils. Prior to land disposal, all constituents subject to treatment must be treated as follows:
(a) For non-metals except carbon disulfide, cyclohexanone, and methanol, treatment must achieve ninety per cent reduction in total constituent concentrations, except as provided by paragraph (C)(1)(c) of this rule.
(b) For metals and carbon disulfide, cyclohexanone, and methanol, treatment must achieve ninety per cent reduction in constituent concentrations as measured in leachate from the treated media (tested according to the toxicity characteristic leaching procedure) or ninety per cent reduction in total constituent concentrations (when a metal removal treatment technology is used), except as provided by paragraph (C)(1)(c) of this rule.
(c) When treatment of any constituent subject to treatment to a ninety per cent reduction standard would result in a concentration less than ten times the universal treatment standard for that constituent, treatment to achieve constituent concentrations less than ten times the universal treatment standard is not required. Universal treatment standards are identified in the table in rule 3745-270-48 of the Administrative Code.
(2) Soils that exhibit the characteristic of ignitability, corrosivity or reactivity. In addition to the treatment required by paragraph (C)(1) of this rule, prior to land disposal, soils that exhibit the characteristic of ignitability, corrosivity, or reactivity must be treated to eliminate these characteristics.
(3) Soils that contain nonanalyzable constituents. In addition to the treatment requirements of paragraphs (C)(1) and (C)(2) of this rule, 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 paragraphs (C)(1) and (C)(2) of this rule; or,
(b) For soil that contains only nonanalyzable constituents, treatment by the method(s) specified in rule 3745-270-42 of the Administrative Code for the waste contained in the soil.
(D) Constituents subject to treatment. When applying the soil treatment standards in paragraph (C) of this rule, constituents subject to treatment are any constituents listed in the table in rule 3745-270-48 of the Administrative Code that are reasonably expected to be present in any given volume of contaminated soil, except fluoride, selenium, sulfides, vanadium, and zinc, and that are present at concentrations greater than ten times the universal treatment standard. Polychlorinated biphenyls (PCBs) are not constituent subject to treatment in any given volume of soil which exhibits the toxicity characteristic solely because of the presence of metals.
(E) Management of treatment residuals. Treatment residuals from treating contaminated soil identified by paragraph (A) of this rule as needing to comply with LDRs must be managed as follows:
(1) Soil residuals are subject to the treatment standards of this rule;
(2) Non-soil residuals are subject to:
(a) For soils contaminated by listed hazardous waste, the hazardous waste rules applicable to the listed hazardous waste; and
(b) For soils that exhibit a characteristic of hazardous waste, if the non-soil residual also exhibits a characteristic of hazardous waste, the treatment standards applicable to the characteristic hazardous waste.
Effective:
09/05/2010
R.C.
119.032 review dates: Exempt
Promulgated Under:
119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/07/2000
3745-270-50
Prohibitions on storage of restricted wastes.
(A) Except as provided in this rule, the storage of hazardous wastes restricted from land disposal under rules 3745-270-20 to 3745-270-39 of the Administrative Code or Section 3004(d) of RCRA is prohibited, unless the following conditions are met:
(1) A generator stores such wastes in tanks, containers, or containment buildings on-site solely for the purpose of the accumulation of such quantities of hazardous waste as necessary to facilitate proper recovery, treatment, or disposal and the generator complies with the requirements in rule 3745-52-34 and Chapters 3745-54 to 3745-57, 3745-65 to 3745-69, 3745-205, and 3745-256 of the Administrative Code.
[ Comment: A generator who is in existence on the effective date of a rule in Chapter 3745-270 of the Administrative Code and who must store hazardous wastes for longer than ninety days due to the rules of Chapter 3745-270 of the Administrative Code becomes an owner or operator of a storage facility and must obtain an Ohio hazardous waste installation and operation permit. Such a facility may qualify for a permit by rule upon compliance with rule 3745-50-46 and paragraph (C) of rule 3745-50-40 of the Administrative Code.]
(2) An owner or operator of a hazardous waste treatment, storage, or disposal facility stores such wastes in tanks, containers, or containment buildings solely for the purpose of the accumulation of such quantities of hazardous waste as necessary to facilitate proper recovery, treatment, or disposal and:
(a) Each container is clearly marked to identify its contents and the date each period of accumulation begins;
(b) Each tank is clearly marked with a description of its contents, the quantity of each hazardous waste received, and the date each period of accumulation begins, or such information for each tank is recorded and maintained in the operating record at that facility. Regardless of whether the tank itself is marked, an owner or operator must comply with the operating record requirements specified in rule 3745-54-73 or 3745-65-73 of the Administrative Code.
(3) A transporter stores manifested shipments of such wastes at a transfer facility for ten days or less.
(B) An owner or operator of a treatment, storage, or disposal facility may store such wastes for up to one year unless Ohio EPA can demonstrate that such storage was not solely for the purpose of accumulation of such quantities of hazardous waste as are necessary to facilitate proper recovery, treatment, or disposal.
(C) An owner or operator of a treatment, storage, or disposal facility may store such wastes beyond one year; however, the owner or operator bears the burden of proving that such storage was solely for the purpose of accumulation of such quantities of hazardous waste as are necessary to facilitate proper recovery, treatment, or disposal.
(D) If a generator's waste is exempt from a prohibition on the type of land disposal utilized for the waste (for example, because of an approved case-by-case extension under rule 3745-270-05 of the Administrative Code, an approved petition under rule 3745-270-06 of the Administrative Code, or a national capacity variance under rules 3745-270-30 to 3745-270-39 of the Administrative Code), the prohibition in paragraph (A) of this rule does not apply during the period of such exemption.
(E) The prohibition in paragraph (A) of this rule does not apply to hazardous wastes that meet the treatment standards specified in rule 3745-270-42 of the Administrative Code or the treatment standards specified in a variance granted under rule 3745-270-44 of the Administrative Code, or, where treatment standards have not been specified, is in compliance with the applicable prohibitions specified in Section 3004 of RCRA.
(F) Liquid hazardous wastes containing polychlorinated biphenyls (PCBs) at concentrations greater than or equal to fifty parts per million must be stored at a facility that meets the requirements of 40 CFR 761.65(b) and must be removed from storage and treated or disposed as required by Chapter 3745-270 of the Administrative Code within one year of the date when such wastes are first placed into storage.
(G) The prohibition and requirements in this rule do not apply to hazardous remediation wastes stored in a staging pile approved pursuant to rule 3745-57-74 of the Administrative Code.
[Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see rule 3745-50-11 of the Administrative Code titled "Incorporated by reference."]
Effective:
03/17/2012
R.C.
119.032 review dates: Exempt
Promulgated Under:
119.03
Statutory
Authority:
3734.12
Rule
Amplifies:
3734.12
Prior
Effective Dates: 12/30/1989, 02/11/1992, 12/07/2000, 12/07/2004