LAND DISPOSAL RESTRICTIONS

• Citation: 40 CFR Part 268
• Sections: 38

§ 268.1 Purpose, scope, and applicability.

(a) This part 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 this part or part 261 of this chapter, the requirements of this part 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 subpart C of this part or pursuant to § 268.5, 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 § 268.6, with respect to those wastes and units covered by the petition;

(3) Wastes that are hazardous only because they exhibit a hazardous characteristic, and which are otherwise prohibited under this part, or part 148 of this chapter, are not prohibited if the wastes:

(i) Are disposed into a nonhazardous or hazardous injection well as defined under 40 CFR 146.6(a); and

(ii) Do not exhibit any prohibited characteristic of hazardous waste identified in 40 CFR part 261, subpart C at the point of injection.

(4) Wastes that are hazardous only because they exhibit a hazardous characteristic, and which are otherwise prohibited under this part, 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 § 268.40, or are D003 reactive cyanide:

(i) The wastes are managed in a treatment system which subsequently discharges to waters of the U.S. pursuant to a permit issued under section 402 of the Clean Water Act; or

(ii) The wastes are treated for purposes of the pretreatment requirements of section 307 of the Clean Water Act; or

(iii) The wastes are managed in a zero discharge system engaged in Clean Water Act-equivalent treatment as defined in § 268.37(a); and

(iv) 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 this part shall not affect the availability of a waiver under section 121(d)(4) of the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (CERCLA).

(e) The following hazardous wastes are not subject to any provision of part 268:

(1) Waste generated by very small quantity generators, as defined in § 260.10 of this chapter;

(2) Waste pesticides that a farmer disposes of pursuant to § 262.70;

(3) Wastes identified or listed as hazardous after November 8, 1984 for which 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 40 CFR 260.10) are exempt from 40 CFR 268.7 and 268.50 for the hazardous wastes listed below. These handlers are subject to regulation under 40 CFR part 273.

(1) Batteries as described in 40 CFR 273.2;

(2) Pesticides as described in § 273.3 of this chapter;

(3) Mercury-containing equipment as described in § 273.4 of this chapter;

(4) Lamps as described in § 273.5 of this chapter; and

(5) Aerosol cans as described in § 273.6 of this chapter.

§ 268.2 Definitions applicable in this part.

When used in this part the following terms have the meanings given below:

(a) Halogenated organic compounds or HOCs means those compounds having a carbon-halogen bond which are listed under appendix III to this part.

(b) Hazardous constituent or constituents means those constituents listed in appendix VIII to part 261 of this chapter.

(c) Land disposal means placement in or on the land, except in a corrective action management unit or 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.

(d) Nonwastewaters are wastes that do not meet the criteria for wastewaters in paragraph (f) of this section.

(e) Polychlorinated biphenyls or PCBs are halogenated organic compounds defined in accordance with 40 CFR 761.3.

(f) Wastewaters are wastes that contain less than 1% by weight total organic carbon (TOC) and less than 1% by weight total suspended solids (TSS).

(g) Debris means solid material exceeding a 60 mm particle size that is intended for disposal and that is: A manufactured object; or plant or animal matter; or natural geologic material. However, the following materials are not debris: any material for which a specific treatment standard is provided in Subpart D, Part 268, namely lead acid batteries, cadmium batteries, and radioactive lead solids; process residuals such as smelter slag and residues from the treatment of waste, wastewater, sludges, or air emission residues; and intact containers of hazardous waste that are not ruptured and that retain at least 75% of their original volume. A mixture of debris that has not been treated to the standards provided by § 268.45 and other material is subject to regulation as debris if the mixture is comprised primarily of debris, by volume, based on visual inspection.

(h) Hazardous debris means debris that contains a hazardous waste listed in subpart D of part 261 of this chapter, or that exhibits a characteristic of hazardous waste identified in subpart C of part 261 of this chapter. 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 § 268.3.

(i) Underlying hazardous constituent means any constituent listed in § 268.48, Table UTS—Universal Treatment Standards, 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 UTS treatment standards.

(j) Inorganic metal-bearing waste is one for which EPA has established treatment standards for metal hazardous constituents, and which does not otherwise contain significant organic or cyanide content as described in § 268.3(c)(1), and is specifically listed in appendix XI of this part.

(k) 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 § 268.3.

§ 268.3 Dilution prohibited as a substitute for treatment.

(a) Except as provided in paragraph (b) of this section, no generator, transporter, handler, or owner or operator of a treatment, storage, or disposal facility shall 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 subpart D of this part, to circumvent the effective date of a prohibition in subpart C of this part, to otherwise avoid a prohibition in subpart C of this part, or to circumvent a land disposal prohibition imposed by RCRA section 3004.

(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 the purposes of pretreatment requirements under section 307 of the CWA is not impermissible dilution for purposes of this section unless a method other than DEACT has been specified in § 268.40 as the treatment standard, or unless the waste is a D003 reactive cyanide wastewater or nonwastewater.

(c) Combustion of the hazardous waste codes listed in Appendix XI of this part 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 found in § 268.48;

(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 5000 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 1% Total Organic Carbon (TOC).

(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.

§ 268.4 Treatment surface impoundment exemption.

(a) Wastes which are otherwise prohibited from land disposal under this part 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:

(i) Sampling and testing. For wastes with treatment standards in subpart D of this part and/or prohibition levels in subpart C of this part or RCRA section 3004(d), the residues from treatment are analyzed, as specified in § 268.7 or § 268.32, 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 § 264.13 or § 265.13, must be designed such that representative samples of the sludge and the supernatant are tested separately rather than mixed to form homogeneous samples.

(ii) 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 subpart D of this part; residues which do not meet the prohibition levels established under subpart C of this part or imposed by statute (where no treatment standards have been established); residues which are from the treatment of wastes prohibited from land disposal under subpart C of this part (where no treatment standards have been established and no prohibition levels apply); or residues from managing listed wastes which are not delisted under § 260.22 of this chapter. 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.

(iii) Subsequent management. Treatment residues may not be placed in any other surface impoundment for subsequent management.

(iv) Recordkeeping. Sampling and testing and recordkeeping provisions of §§ 264.13 and 265.13 of this chapter apply.

(3) The impoundment meets the design requirements of § 264.221(c) or § 265.221(a) of this chapter, regardless that the unit may not be new, expanded, or a replacement, and be in compliance with applicable ground water monitoring requirements of subpart F of part 264 or part 265 of this chapter unless:

(i) Exempted pursuant to § 264.221 (d) or (e) of this chapter, or to § 265.221 (c) or (d) of this chapter; or,

(ii) Upon application by the owner or operator, the Administrator, after notice and an opportunity to comment, has granted a waiver of the requirements on the basis that the surface impoundment:

(A) Has at least one liner, for which there is no evidence that such liner is leaking;

(B) Is located more than one-quarter mile from an underground source of drinking water; and

(C) Is in compliance with generally applicable ground water monitoring requirements for facilities with permits; or,

(iii) Upon application by the owner or operator, the Administrator, 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 Regional Administrator a written certification that the requirements of § 268.4(a)(3) have been met. The following certification is required:

I certify under penalty of law that the requirements of 40 CFR 268.4(a)(3) 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 section.

§ 268.5 Procedures for case-by-case extensions to an effective date.

(a) Any person who generates, treats, stores, or disposes of a hazardous waste may submit an application to the Administrator for an extension to the effective date of any applicable restriction established under subpart C of this part. The applicant must demonstrate the following:

(1) He has made a good-faith effort to locate and contract with treatment, recovery, or disposal facilities nationwide to manage his waste in accordance with the effective date of the applicable restriction established under subpart C of this part;

(2) He has entered into a binding contractual commitment to construct or otherwise provide alternative treatment, recovery (e.g., recycling), or disposal capacity that meets the treatment standards specified in subpart D or, where treatment standards have not been specified, such treatment, recovery, or disposal capacity is protective of human health and the environment.

(3) Due to circumstances beyond the applicant's control, such alternative capacity cannot reasonably be made available by the applicable effective date. This demonstration may include a showing that the technical and practical difficulties associated with providing the alternative capacity will result in the capacity not being available by the applicable effective date;

(4) The capacity being constructed or otherwise provided by the applicant will be sufficient to manage the entire quantity of waste that is the subject of the application;

(5) He provides a detailed schedule for obtaining required operating and construction permits or an outline of how and when alternative capacity will be available;

(6) He has arranged for adequate capacity to manage his waste during an extension and has documented in the application the location of all sites at which the waste will be managed; and

(7) Any waste managed in a surface impoundment or landfill during the extension period will meet the requirements of paragraph (h)(2) of this section.

(b) An authorized representative signing an application described under paragraph (a) of this section shall make the following certification:

I certify under penalty of law that I have personally examined and am familiar with the information submitted in this document and all attachments and that, based on my inquiry of those individuals immediately responsible for obtaining the information, I believe that the 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.

(c) After receiving an application for an extension, the Administrator may request any additional information which he deems as necessary to evaluate the application.

(d) An extension will apply only to the waste generated at the individual facility covered by the application and will not apply to restricted waste from any other facility.

(e) On the basis of the information referred to in paragraph (a) of this section, after notice and opportunity for comment, and after consultation with appropriate State agencies in all affected States, the Administrator may grant an extension of up to 1 year from the effective date. The Administrator may renew this extension for up to 1 additional year upon the request of the applicant if the demonstration required in paragraph (a) of this section can still be made. In no event will an extension extend beyond 24 months from the applicable effective date specified in subpart C of part 268. The length of any extension authorized will be determined by the Administrator based on the time required to construct or obtain the type of capacity needed by the applicant as described in the completion schedule discussed in paragraph (a)(5) of this section. The Administrator will give public notice of the intent to approve or deny a petition and provide an opportunity for public comment. The final decision on a petition will be published in the Federal Register.

(f) Any person granted an extension under this section must immediately notify the Administrator as soon as he has knowledge of any change in the conditions certified to in the application.

(g) Any person granted an extension under this section shall submit written progress reports at intervals designated by the Administrator. Such reports must describe the overall progress made toward constructing or otherwise providing alternative treatment, recovery or disposal capacity; must identify any event which may cause or has caused a delay in the development of the capacity; and must summarize the steps taken to mitigate the delay. The Administrator can revoke the extension at any time if the applicant does not demonstrate a good-faith effort to meet the schedule for completion, if the Agency denies or revokes any required permit, if conditions certified in the application change, or for any violation of this chapter.

(h) Whenever the Administrator establishes an extension to an effective date under this section, during the period for which such extension is in effect:

(1) The storage restrictions under § 268.50(a) do not apply; and

(2) Such hazardous waste may be disposed in a landfill or surface impoundment only if such unit is in compliance with the technical requirements of the following provisions regardless of whether such unit is existing, new, or a replacement or lateral expansion.

(i) The landfill, if in interim status, is in compliance with the requirements of subpart F of part 265 and § 265.301 (a), (c), and (d) of this chapter; or,

(ii) The landfill, if permitted, is in compliance with the requirements of subpart F of part 264 and § 264.301 (c), (d) and (e) of this chapter; or

(iii) The surface impoundment, if in interim status, is in compliance with the requirements of subpart F of part 265, § 265.221 (a), (c), and (d) of this chapter, and RCRA section 3005(j)(1); or

(iv) The surface impoundment, if permitted, is in compliance with the requirements of subpart F of part 264 and § 264.221 (c), (d) and (e) of this chapter; or

(v) The surface impoundment, if newly subject to RCRA section 3005(j)(1) due to the promulgation of additional listings or characteristics for the identification of hazardous waste, is in compliance with the requirements of subpart F of part 265 of this chapter within 12 months after the promulgation of additional listings or characteristics of hazardous waste, and with the requirements of § 265.221 (a), (c) and (d) of this chapter within 48 months after the promulgation of additional listings or characteristics of hazardous waste. If a national capacity variance is granted, during the period the variance is in effect, the surface impoundment, if newly subject to RCRA section 3005(j)(1) due to the promulgation of additional listings or characteristics of hazardous waste, is in compliance with the requirements of subpart F of part 265 of this chapter within 12 months after the promulgation of additional listings or characteristics of hazardous waste, and with the requirements of § 265.221 (a), (c) and (d) of this chapter within 48 months after the promulgation of additional listings or characteristics of hazardous waste; or

(vi) The landfill, if disposing of containerized liquid hazardous wastes containing PCBs at concentrations greater than or equal to 50 ppm but less than 500 ppm, is also in compliance with the requirements of 40 CFR 761.75 and parts 264 and 265.

(i) Pending a decision on the application the applicant is required to comply with all restrictions on land disposal under this part once the effective date for the waste has been reached.

§ 268.6 Petitions to allow land disposal of a waste prohibited under subpart C of part 268.

(a) Any person seeking an exemption from a prohibition under subpart C of this part for the disposal of a restricted hazardous waste in a particular unit or units must submit a petition to the Administrator demonstrating, to a reasonable degree of certainty, that there will be no migration of hazardous constituents from the disposal unit or injection zone for as long as the wastes remain hazardous. The demonstration must include the following components:

(1) An identification of the specific waste and the specific unit for which the demonstration will be made;

(2) A waste analysis to describe fully the chemical and physical characteristics of the subject waste;

(3) A comprehensive characterization of the disposal unit site including an analysis of background air, soil, and water quality.

(4) A monitoring plan that detects migration at the earliest practicable time;

(5) Sufficient information to assure the Administrator that the owner or operator of a land disposal unit receiving restricted waste(s) will comply with other applicable Federal, State, and local laws.

(b) The demonstration referred to in paragraph (a) of this section must meet the following criteria:

(1) All waste and environmental sampling, test, and analysis data must be accurate and reproducible to the extent that state-of-the-art techniques allow;

(2) All sampling, testing, and estimation techniques for chemical and physical properties of the waste and all environmental parameters must have been approved by the Administrator;

(3) Simulation models must be calibrated for the specific waste and site conditions, and verified for accuracy by comparison with actual measurements;

(4) A quality assurance and quality control plan that addresses all aspects of the demonstration must be approved by the Administrator; and,

(5) An analysis must be performed to identify and quantify any aspects of the demonstration that contribute significantly to uncertainty. This analysis must include an evaluation of the consequences of predictable future events, including, but not limited to, earthquakes, floods, severe storm events, droughts, or other natural phenomena.

(c) Each petition referred to in paragraph (a) of this section must include the following:

(1) A monitoring plan that describes the monitoring program installed at and/or around the unit to verify continued compliance with the conditions of the variance. This monitoring plan must provide information on the monitoring of the unit and/or the environment around the unit. The following specific information must be included in the plan:

(i) The media monitored in the cases where monitoring of the environment around the unit is required;

(ii) The type of monitoring conducted at the unit, in the cases where monitoring of the unit is required;

(iii) The location of the monitoring stations;

(iv) The monitoring interval (frequency of monitoring at each station);

(v) The specific hazardous constituents to be monitored;

(vi) The implementation schedule for the monitoring program;

(vii) The equipment used at the monitoring stations;

(viii) The sampling and analytical techniques employed; and

(ix) The data recording/reporting procedures.

(2) Where applicable, the monitoring program described in paragraph (c)(1) of this section must be in place for a period of time specified by the Administrator, as part of his approval of the petition, prior to receipt of prohibited waste at the unit.

(3) The monitoring data collected according to the monitoring plan specified under paragraph (c)(1) of this section must be sent to the Administrator according to a format and schedule specified and approved in the monitoring plan, and

(4) A copy of the monitoring data collected under the monitoring plan specified under paragraph (c)(1) of this section must be kept on-site at the facility in the operating record.

(5) The monitoring program specified under paragraph (c)(1) of this section meets the following criteria:

(i) All sampling, testing, and analytical data must be approved by the Administrator and must provide data that is accurate and reproducible.

(ii) All estimation and monitoring techniques must be approved by the Administrator.

(iii) A quality assurance and quality control plan addressing all aspects of the monitoring program must be provided to and approved by the Administrator.

(d) Each petition must be submitted to the Administrator.

(e) After a petition has been approved, the owner or operator must report any changes in conditions at the unit and/or the environment around the unit that significantly depart from the conditions described in the variance and affect the potential for migration of hazardous constituents from the units as follows:

(1) If the owner or operator plans to make changes to the unit design, construction, or operation, such a change must be proposed, in writing, and the owner or operator must submit a demonstration to the Administrator at least 30 days prior to making the change. The Administrator will determine whether the proposed change invalidates the terms of the petition and will determine the appropriate response. Any change must be approved by the Administrator prior to being made.

(2) If the owner or operator discovers that a condition at the site which was modeled or predicted in the petition does not occur as predicted, this change must be reported, in writing, to the Administrator within 10 days of discovering the change. The Administrator will determine whether the reported change from the terms of the petition requires further action, which may include termination of waste acceptance and revocation of the petition, petition modifications, or other responses.

(f) If the owner or operator determines that there is migration of hazardous constituent(s) from the unit, the owner or operator must:

(1) Immediately suspend receipt of prohibited waste at the unit, and

(2) Notify the Administrator, in writing, within 10 days of the determination that a release has occurred.

(3) Following receipt of the notification the Administrator will determine, within 60 days of receiving notification, whether the owner or operator can continue to receive prohibited waste in the unit and whether the variance is to be revoked. The Administrator shall also determine whether further examination of any migration is warranted under applicable provisions of part 264 or part 265.

(g) Each petition must include the following statement signed by the petitioner or an authorized representative:

I certify under penalty of law that I have personally examined and am familiar with the information submitted in this petition and all attached documents, and that, based on my inquiry of those individuals immediately responsible for obtaining the information, I believe that 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.

(h) After receiving a petition, the Administrator may request any additional information that reasonably may be required to evaluate the demonstration.

(i) If approved, the petition will apply to land disposal of the specific restricted waste at the individual disposal unit described in the demonstration and will not apply to any other restricted waste at that disposal unit, or to that specific restricted waste at any other disposal unit.

(j) The Administrator will give public notice in the Federal Register of the intent to approve or deny a petition and provide an opportunity for public comment. The final decision on a petition will be published in the Federal Register.

(k) The term of a petition granted under this section shall be no longer than the term of the RCRA permit if the disposal unit is operating under a RCRA permit, or up to a maximum of 10 years from the date of approval provided under paragraph (g) of this section if the unit is operating under interim status. In either case, the term of the granted petition shall expire upon the termination or denial of a RCRA permit, or upon the termination of interim status or when the volume limit of waste to be land disposed during the term of petition is reached.

(l) Prior to the Administrator's decision, the applicant is required to comply with all restrictions on land disposal under this part once the effective date for the waste has been reached.

(m) The petition granted by the Administrator does not relieve the petitioner of his responsibilities in the management of hazardous waste under 40 CFR part 260 through part 271.

(n) Liquid hazardous wastes containing polychlorinated biphenyls at concentrations greater than or equal to 500 ppm are not eligible for an exemption under this section.

§ 268.7 Testing, tracking, and recordkeeping requirements for generators, reverse distributors, treaters, and disposal facilities.

(a) Requirements for generators and reverse distributors —(1) A generator of 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 § 268.40, 268.45, or § 268.49. This determination can be made concurrently with the hazardous waste determination required in § 262.11 of this chapter, in either of two ways: testing the waste or using knowledge of the waste. 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 of Evaluating Solid Waste, Physical/Chemical Methods,” EPA Publication SW-846, (incorporated by reference, see § 260.11 of this chapter), depending on whether the treatment standard for the waste is expressed as a total concentration or concentration of hazardous constituent in the waste's extract. (Alternatively, the generator must send the waste to a RCRA-permitted hazardous waste treatment facility, where the waste treatment facility must comply with the requirements of § 264.13 of this chapter and paragraph (b) of this section.) In addition, some hazardous wastes must be treated by particular treatment methods before they can be land disposed and some soils are contaminated by such hazardous wastes. These treatment standards are also found in § 268.40, and are described in detail in § 268.42, Table 1. 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). If a generator determines they are managing a waste or soil contaminated with a waste, that displays a hazardous characteristic of ignitability, corrosivity, reactivity, or toxicity, they must comply with the special requirements of § 268.9 of this part in addition to any applicable requirements in this section.

(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 file. The notice must include the information in column “268.7(a)(2)” of the Generator Paperwork Requirements Table in paragraph (a)(4) of this section. (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 the determination.”) No further notification is necessary until such time that the waste or facility change, in which case a new notification must be sent and a copy placed in the generator's file.

(3) If the waste or contaminated soil meets the treatment standard at the original point of generation:

(i) 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 file. The notice must include the information indicated in column “268.7(a)(3)” of the Generator Paperwork Requirements Table in § 268.7(a)(4) 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 40 CFR part 268 subpart D. 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 a fine and imprisonment.

(ii) 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 file. The notice must include the information in column “268.7(a)(3)” of the Generator Paperwork Requirements Table in § 268.7(a)(4).

(iii) 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 § 261.3(f) of this chapter 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 requirement 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 § 268.5, disposal in a no-migration unit under § 268.6, or a national capacity variance or case-by-case capacity variance under subpart C of this part. 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 indicated in column “268.7(a)(4)” of the Generator Paperwork Requirements Table below. If the waste changes, the generator must send a new notice to the receiving facility, and place a copy in their files.

Generator Paperwork Requirements Table

Required information

§ 268.7 (a)(2)

§ 268.7 (a)(3)

§ 268.7 (a)(4)

§ 268.7 (a)(9)

1. EPA Hazardous Waste Numbers and Manifest Number of first shipment

✔

✔

✔

✔

2. Statement: this waste is not prohibited from land disposal

✔

3. The waste is subject to the LDRs. The constituents of concern for F001-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

✔

✔

4. The notice must include the applicable wastewater/ nonwastewater category (see §§ 268.2(d) and (f)) and subdivisions made within a waste code based on waste-specific criteria (such as D003 reactive cyanide)

✔

✔

5. Waste analysis data (when available)

✔

✔

✔

6. Date the waste is subject to the prohibition

✔

7. For hazardous debris, when treating with the alternative treatment technologies provided by § 268.45: the contaminants subject to treatment, as described in § 268.45(b); and an indication that these contaminants are being treated to comply with § 268.45

✔

✔

8. For contaminated soil subject to LDRs as provided in § 268.49(a), the constituents subject to treatment as described in § 268.49(d), 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 § 268.49(c) or the universal treatment standards

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9. A certification is needed (see applicable section for exact wording)

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(5) If a generator is managing and treating prohibited waste or contaminated soil in tanks, containers, or containment buildings regulated under 40 CFR 262.15, 262.16, and 262.17 to meet applicable LDR treatment standards found at § 268.40, the generator must develop and follow a written waste analysis plan which describes the procedures they will carry out to comply with the treatment standards. (Generators treating hazardous debris under the alternative treatment standards of Table 1 to § 268.45, however, are not subject to these waste analysis requirements.) The plan must be kept on site in the generator's records, and the following requirements must be met:

(i) 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 this part, including the selected testing frequency.

(ii) Such plan must be kept in the facility's on-site files and made available to inspectors.

(iii) Wastes shipped off-site pursuant to this paragraph must comply with the notification requirements of § 268.7(a)(3).

(6) 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. 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,” EPA Publication SW-846, as referenced in § 260.11 of this chapter, 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 or solid waste or is exempted from Subtitle C regulation under 40 CFR 261.2 through 261.6 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 at 40 CFR 261.4(a)(2) or that are CWA-equivalent, or are managed in an underground injection well regulated by the SDWA), he must place a one-time notice describing such generation, subsequent exclusion from the definition of hazardous or solid waste or exemption from RCRA Subtitle C regulation, and the disposition of the waste, in the facility's on-site files.

(8) Generators must retain on-site a copy of all notices, certifications, waste analysis data, and other documentation produced pursuant to this section 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 Administrator. The requirements of this paragraph apply to solid wastes even when the hazardous characteristic is removed prior to disposal, or when the waste is excluded from the definition of hazardous or solid waste under 40 CFR 261.2 through 261.6, or exempted from Subtitle C regulation, 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 found at § 268.42(c):

(i) With the initial shipment of waste to a treatment facility, the generator must submit a notice that provides the information in column “§ 268.7(a)(9)” in the Generator Paperwork Requirements Table of paragraph (a)(4) of this section, 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 IV to 40 CFR part 268 and that this lab pack will be sent to a combustion facility in compliance with the alternative treatment standards for lab packs at 40 CFR 268.42(c). I am aware that there are significant penalties for submitting a false certification, including the possibility of fine or imprisonment.

(ii) 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 and a copy placed in the generator's file.

(iii) If the lab pack contains characteristic hazardous wastes (D001-D043), underlying hazardous constituents (as defined in § 268.2(i)) need not be determined.

(iv) The generator must also comply with the requirements in paragraphs (a)(6) and (a)(7) of this section.

(10) Small quantity generators with tolling agreements pursuant to 40 CFR 262.20(e) must comply with the applicable notification and certification requirements of paragraph (a) of this section 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 Administrator.

(b) Treatment facilities must test their wastes according to the frequency specified in their waste analysis plans as required by 40 CFR 264.13 (for permitted TSDs) or 40 CFR 265.13 (for interim status facilities). Such testing must be performed as provided in paragraphs (b)(1), (b)(2) and (b)(3) of this section.

(1) For wastes or contaminated soil with treatment standards expressed 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 (the Toxicity Characteristic Leaching Procedure, described in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” EPA Publication SW-846 as incorporated by reference in § 260.11 of this chapter) to assure that the treatment residues extract meet the applicable treatment standards.

(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.

(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.

(i) No further notification is necessary until such time that the waste or receiving facility change, in which case a new notice must be sent and a copy placed in the treatment facility's file.

(ii) The one-time notice must include these requirements:

Treatment Facility Paperwork Requirements Table

Required information

§ 268.7(b)

1. EPA Hazardous Waste Numbers and Manifest Number of first shipment

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2. The waste is subject to the LDRs. The constituents of concern for F001-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.

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3. The notice must include the applicable wastewater/ nonwastewater category (see §§ 268.2(d) and (f)) and subdivisions made within a waste code based on waste-specific criteria (such as D003 reactive cyanide)

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4. Waste analysis data (when available)

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5. For contaminated soil subject to LDRs as provided in 268.49(a), the constituents subject to treatment as described in 268.49(d) and the following statement, “this contaminated soil [does/does not] exhibit a characteristic of hazardous waste and [is subject to/complies with] the soil treatment standards as provided by 268.49(c)”.

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6. A certification is needed (see applicable section for exact wording)

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(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 40 CFR 268.40 without impermissible dilution of the prohibited waste. I am aware 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 have personally 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 40 CFR 268.49 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.

(i) A copy of the certification must be placed in the treatment facility's on-site files. If the waste or treatment residue changes, or the receiving facility changes, a new certification must be sent to the receiving facility, and a copy placed in the file.

(ii) Debris excluded from the definition of hazardous waste under § 261.3(f) of this chapter ( i.e. , debris treated by an extraction or destruction technology provided by Table 1, § 268.45, and debris that the Director has determined does not contain hazardous waste), however, is subject to the notification and certification requirements of paragraph (d) of this section rather than the certification requirements of this paragraph.

(iii) 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 § 268.40(d), 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 268.42, Table 1. 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 there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.

(iv) For characteristic wastes that are subject to the treatment standards in § 268.40 (other than those expressed as a method of treatment), or § 268.49, and that contain underlying hazardous constituents as defined in § 268.2(i); 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 40 CFR 268.40 or 268.49 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.

(v) For characteristic wastes that contain underlying hazardous constituents as defined § 268.2(i) that are treated on-site to remove the hazardous characteristic to treat underlying hazardous constituents to levels in § 268.48 Universal Treatment Standards, the certification must state the following:

I certify under penalty of law that the waste has been treated in accordance with the requirements of 40 CFR 268.40 to remove the hazardous characteristic and that underlying hazardous constituents, as defined in § 268.2(i) have been treated on-site to meet the § 268.48 Universal Treatment Standards. 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 section.

(6) Where the wastes are recyclable materials used in a manner constituting disposal subject to the provisions of § 266.20(b) of this chapter regarding treatment standards and prohibition levels, the owner or operator of a treatment facility ( i.e. , the recycler) must, for the initial shipment of waste, prepare a one-time certification described in paragraph (b)(4) of this section, and a one-time notice which includes the information in paragraph (b)(3) of this section (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 must also 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 40 CFR 266.20(b), the owner or operator of any land disposal facility disposing any waste subject to restrictions under this part must:

(1) Have copies of the notice and certifications specified in paragraph (a) or (b) of this section.

(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,” EPA Publication SW-846 as incorporated by reference in § 260.11 of this chapter), to assure that the wastes or treatment residues are in compliance with the applicable treatment standards set forth in subpart D of this part. Such testing must be performed according to the frequency specified in the facility's waste analysis plan as required by § 264.13 or § 265.13 of this chapter.

(d) Generators or treaters who first claim that hazardous debris is excluded from the definition of hazardous waste under § 261.3(f) of this chapter ( i.e. , debris treated by an extraction or destruction technology provided by Table 1, § 268.45, and debris that the EPA Regional Administrator (or his designated representative) or State authorized to implement part 268 requirements 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 EPA Regional hazardous waste management division director (or his designated representative) or State authorized to implement part 268 requirements:

(i) The name and address of the Subtitle D facility receiving the treated debris;

(ii) A description of the hazardous debris as initially generated, including the applicable EPA Hazardous Waste Number(s); and

(iii) For debris excluded under § 261.3(f)(1) of this chapter, the technology from Table 1, § 268.45, 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 § 261.2(f)(1) of this chapter, if a different type of debris is treated or if a different technology is used to treat the debris.

(3) For debris excluded under § 261.3(f)(1) of this chapter, the owner or operator of the treatment facility must document and certify compliance with the treatment standards of Table 1, § 268.45, as follows:

(i) Records must be kept of all inspections, evaluations, and analyses of treated debris that are made to determine compliance with the treatment standards;

(ii) 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

(iii) 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 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 40 CFR 268.45. 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 EPA or an authorized state a determination that a given contaminated soil subject to LDRs as provided in § 268.49(a) no longer contains a listed hazardous waste and generators and treaters who first determine that a contaminated soil subject to LDRs as provided in § 268.49(a) 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.

§ 268.9 Special rules regarding wastes that exhibit a characteristic.

(a) The initial generator of a solid waste must determine each EPA Hazardous Waste Number (waste code) applicable to the waste in order to determine the applicable treatment standards under subpart D of this part. This determination may be made concurrently with the hazardous waste determination required in § 262.11 of this chapter. For purposes of part 268, the waste will carry the waste code for any applicable listed waste (40 CFR part 261, subpart D). In addition, where the waste exhibits a characteristic, the waste will carry one or more of the characteristic waste codes (40 CFR part 261, subpart C), 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 section. If the generator determines that their waste displays a hazardous characteristic (and is not D001 nonwastewaters treated by CMBST, RORGS, OR POLYM of § 268.42, Table 1), the generator must determine the underlying hazardous constituents (as defined at § 268.2(i)) in the characteristic waste.

(b) Where a prohibited waste is both listed under 40 CFR part 261, subpart D and exhibits a characteristic under 40 CFR part 261, subpart C, the treatment standard for the waste code listed in 40 CFR part 261, subpart D will operate in lieu of the standard for the waste code under 40 CFR part 261, subpart C, 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 waste codes.

(c) In addition to any applicable standards determined from the initial point of generation, no prohibited waste which exhibits a characteristic under 40 CFR part 261, subpart C may be land disposed unless the waste complies with the treatment standards under subpart D of this part.

(d) Wastes that exhibit a characteristic are also subject to § 268.7 requirements, 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 subtitle D facility receiving the waste changes.

(1) The notification must include the following information:

(i) Name and address of the RCRA Subtitle D facility receiving the waste shipment; and

(ii) A description of the waste as initially generated, including the applicable EPA hazardous waste code(s), treatability group(s), and underlying hazardous constituents (as defined in § 268.2(i)), 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 found in § 268.7(b)(4).

(i) If treatment removes the characteristic but does not meet standards applicable to underlying hazardous constituents, then the certification found in § 268.7(b)(4)(iv) applies.

(ii) [Reserved]

§ 268.13 Schedule for wastes identified or listed after November 8, 1984.

In the case of any hazardous waste identified or listed under section 3001 after November 8, 1984, the Administrator shall make a land disposal prohibition determination within 6 months after the date of identification or listing.

§ 268.14 Surface impoundment exemptions.

(a) This section defines additional circumstances under which an otherwise prohibited waste may continue to be placed in a surface impoundment.

(b) Wastes which are newly identified or listed under section 3001 after November 8, 1984, and stored in a surface impoundment that is newly subject to subtitle C of RCRA as a result of the additional identification or listing, may continue to be stored in the surface impoundment for 48 months after the promulgation of the additional listing or characteristic, notwithstanding that the waste is otherwise prohibited from land disposal, provided that the surface impoundment is in compliance with the requirements of subpart F of part 265 of this chapter within 12 months after promulgation of the new listing or characteristic.

(c) Wastes which are newly identified or listed under section 3001 after November 8, 1984, and treated in a surface impoundment that is newly subject to subtitle C of RCRA as a result of the additional identification or listing, may continue to be treated in that surface impoundment, notwithstanding that the waste is otherwise prohibited from land disposal, provided that surface impoundment is in compliance with the requirements of subpart F of part 265 of this chapter within 12 months after the promulgation of the new listing or characteristic. In addition, if the surface impoundment continues to treat hazardous waste after 48 months from promulgation of the additional listing or characteristic, it must then be in compliance with § 268.4.

§ 268.20 Waste specific prohibitions—Dyes and/or pigments production wastes.

(a) Effective August 23, 2005, the waste specified in 40 CFR part 261 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 section do not apply if:

(1) The wastes meet the applicable treatment standards specified in subpart D of this Part;

(2) Persons have been granted an exemption from a prohibition pursuant to a petition under § 268.6, 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 § 268.44;

(4) Hazardous debris has met the treatment standards in § 268.40 or the alternative treatment standards in § 268.45; or

(5) Persons have been granted an extension to the effective date of a prohibition pursuant to § 268.5, with respect to these wastes covered by the extension.

(c) To determine whether a hazardous waste identified in this section exceeds the applicable treatment standards specified in § 268.40, 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 subpart D levels, the waste is prohibited from land disposal, and all requirements of part 268 are applicable, except as otherwise specified.

§ 268.30 Waste specific prohibitions—wood preserving wastes.

(a) Effective August 11, 1997, the following wastes are prohibited from land disposal: the wastes specified in 40 CFR part 261 as EPA Hazardous Waste numbers F032, F034, and F035.

(b) Effective May 12, 1999, the following wastes are prohibited from land disposal: soil and debris contaminated with F032, F034, F035; and radioactive wastes mixed with EPA Hazardous waste numbers F032, F034, and F035.

(c) Between May 12, 1997 and May 12, 1999, soil and debris contaminated with F032, F034, F035; and radioactive waste mixed with F032, F034, and F035 may be disposed in a landfill or surface impoundment only if such unit is in compliance with the requirements specified in § 268.5(h)(2) of this part.

(d) The requirements of paragraphs (a) and (b) of this section do not apply if:

(1) The wastes meet the applicable treatment standards specified in Subpart D of this part;

(2) Persons have been granted an exemption from a prohibition pursuant to a petition under § 268.6, 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 § 268.44; or

(4) Persons have been granted an extension to the effective date of a prohibition pursuant to § 268.5, with respect to those wastes covered by the extension.

(e) To determine whether a hazardous waste identified in this section exceeds the applicable treatment standards specified in § 268.40, 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 constituents in excess of the applicable Universal Treatment Standard levels of § 268.48 of this part, the waste is prohibited from land disposal, and all requirements of part 268 are applicable, except as otherwise specified.

§ 268.31 Waste specific prohibitions—Dioxin-containing wastes.

(a) Effective November 8, 1988, the dioxin-containing wastes specified in 40 CFR 261.31 as EPA Hazardous Waste Nos. F020, F02l, F022, F023, F026, F027, and F028, are prohibited from land disposal unless the following condition applies:

(1) The F020-F023 and F026-F028 dioxin-containing waste is contaminated soil and debris resulting from a response action taken under section 104 or 106 of the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (CERCLA) or a corrective action taken under subtitle C of the Resource Conservation and Recovery Act (RCRA).

(b) Effective November 8, 1990, the F020-F023 and F026-F028 dioxin-containing wastes listed in paragraph (a)(1) of this section are prohibited from land disposal.

(c) Between November 8, 1988, and November 8, 1990, wastes included in paragraph (a)(1) of this section may be disposed in a landfill or surface impoundment only if such unit is in compliance with the requirements specified in § 268.5(h)(2) and all other applicable requirements of parts 264 and 265 of this chapter.

(d) The requirements of paragraphs (a) and (b) of this section do not apply if:

(1) The wastes meet the standards of subpart D of this part; or

(2) Persons have been granted an exemption from a prohibition pursuant to a petition under § 268.6, 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 § 268.5, with respect to those wastes covered by the extension.

§ 268.32 Waste specific prohibitions—Soils exhibiting the toxicity characteristic for metals and containing PCBs.

(a) Effective December 26, 2000, the following wastes are prohibited from land disposal: any volumes of soil exhibiting the toxicity characteristic solely because of the presence of metals (D004—D011) and containing PCBs.

(b) The requirements of paragraph (a) of this section do not apply if:

(1)(i) The wastes contain halogenated organic compounds in total concentration less than 1,000 mg/kg; and

(ii) The wastes meet the treatment standards specified in Subpart D of this part for EPA hazardous waste numbers D004—D011, as applicable; or

(2)(i) The wastes contain halogenated organic compounds in total concentration less than 1,000 mg/kg; and

(ii) The wastes meet the alternative treatment standards specified in § 268.49 for contaminated soil; or

(3) Persons have been granted an exemption from a prohibition pursuant to a petition under § 268.6, 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 § 268.44.

§ 268.33 Waste specific prohibitions—chlorinated aliphatic wastes.

(a) Effective May 8, 2001, the wastes specified in 40 CFR part 261 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 section do not apply if:

(1) The wastes meet the applicable treatment standards specified in subpart D of this part;

(2) Persons have been granted an exemption from a prohibition pursuant to a petition under § 268.6, 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 § 268.44;

(4) Hazardous debris has met the treatment standards in § 268.40 or the alternative treatment standards in § 268.45; or

(5) Persons have been granted an extension to the effective date of a prohibition pursuant to § 268.5, with respect to these wastes covered by the extension.

(c) To determine whether a hazardous waste identified in this section exceeds the applicable treatment standards specified in § 268.40, 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 subpart D of this part, the waste is prohibited from land disposal, and all requirements of part 268 are applicable, except as otherwise specified.

(d) Disposal of K175 wastes that have complied with all applicable 40 CFR 268.40 treatment standards must also be macroencapsulated in accordance with 40 CFR 268.45 Table 1 unless the waste is placed in:

(1) A Subtitle C monofill containing only K175 wastes that meet all applicable 40 CFR 268.40 treatment standards; or

(2) A dedicated Subtitle C landfill cell in which all other wastes being co-disposed are at pH≤6.0.

§ 268.34 Waste specific prohibitions—toxicity characteristic metal wastes.

(a) Effective August 24, 1998, the following wastes are prohibited from land disposal: the wastes specified in 40 CFR Part 261 as EPA Hazardous Waste numbers D004-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 at 40 CFR Part 261.

(b) Effective November 26, 1998, 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) Effective May 26, 2000, the following wastes are prohibited from land disposal: newly identified characteristic wastes from elemental phosphorus processing; radioactive wastes mixed with EPA Hazardous wastes D004-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) Between May 26, 1998 and May 26, 2000, newly identified characteristic wastes from elemental phosphorus processing, radioactive waste mixed with D004-D011 wastes 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 may be disposed in a landfill or surface impoundment only if such unit is in compliance with the requirements specified in § 268.5(h) of this part.

(e) The requirements of paragraphs (a) and (b) of this section do not apply if:

(1) The wastes meet the applicable treatment standards specified in subpart D of this part:

(2) Persons have been granted an exemption from a prohibition pursuant to a petition under § 268.6, 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 § 268.44; or

(4) Persons have been granted an extension to the effective date of a prohibition pursuant to § 268.5, with respect to these wastes covered by the extension.

(f) To determine whether a hazardous waste identified in this section exceeds the applicable treatment standards specified in § 268.40, the initial generator must test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentration in the waste extract or 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 of § 268.48 of this part, the waste is prohibited from land disposal, and all requirements of part 268 are applicable, except as otherwise specified.

§ 268.35 Waste specific prohibitions—petroleum refining wastes.

(a) Effective February 8, 1999, the wastes specified in 40 CFR part 261 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 section do not apply if:

(1) The wastes meet the applicable treatment standards specified in Subpart D of this part;

(2) Persons have been granted an exemption from a prohibition pursuant to a petition under § 268.6, 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 § 268.44;

(4) Hazardous debris that have met treatment standards in § 268.40 or in the alternative treatment standards in § 268.45; or

(5) Persons have been granted an extension to the effective date of a prohibition pursuant to § 268.5, with respect to these wastes covered by the extension.

(c) To determine whether a hazardous waste identified in this section exceeds the applicable treatment standards specified in § 268.40, 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 constituents in excess of the applicable Universal Treatment Standard levels of § 268.48, the waste is prohibited from land disposal, and all requirements of this part are applicable, except as otherwise specified.

§ 268.36 Waste specific prohibitions—inorganic chemical wastes.

(a) Effective May 20, 2002, the wastes specified in 40 CFR part 261 as EPA Hazardous Wastes 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 section do not apply if:

(1) The wastes meet the applicable treatment standards specified in subpart D of this part;

(2) Persons have been granted an exemption from a prohibition pursuant to a petition under § 268.6, 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 § 268.44;

(4) Hazardous debris has met the treatment standards in § 268.40 or the alternative treatment standards in § 268.45; or

(5) Persons have been granted an extension to the effective date of a prohibition pursuant to § 268.5, with respect to these wastes covered by the extension.

(c) To determine whether a hazardous waste identified in this section exceeds the applicable treatment standards specified in § 268.40, 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 subpart D levels, the waste is prohibited from land disposal, and all requirements of this part are applicable, except as otherwise specified.

§ 268.37 Waste specific prohibitions—ignitable and corrosive characteristic wastes whose treatment standards were vacated.

(a) Effective August 9, 1993, the wastes specified in 40 CFR 261.21 as D001 (and is not in the High TOC Ignitable Liquids Subcategory), and specified in § 261.22 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 (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.

(b) Effective February 10, 1994, the wastes specified in 40 CFR 261.21 as D001 (and is not in the High TOC Ignitable Liquids Subcategory), and specified in § 261.22 as D002, that are managed in systems defined in 40 CFR 144.6(e) and 146.6(e) as Class V injection wells, that do not engage in CWA-equivalent treatment before injection, are prohibited from land disposal.

§ 268.38 Waste specific prohibitions—newly identified organic toxicity characteristic wastes and newly listed coke by-product and chlorotoluene production wastes.

(a) Effective December 19, 1994, the wastes specified in 40 CFR 261.32 as EPA Hazardous Waste numbers K141, K142, K143, K144, K145, K147, K148, K149, K150, and K151 are prohibited from land disposal. In addition, debris contaminated with EPA Hazardous Waste numbers F037, F038, K107-K112, K117, K118, K123-K126, K131, K132, K136, U328, U353, U359, and soil and debris contaminated with D012-D043, K141-K145, and K147-K151 are prohibited from land disposal. The following wastes that are specified in 40 CFR 261.24, Table 1 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) On September 19, 1996, radioactive wastes that are mixed with D018-D043 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. 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. Radioactive wastes mixed with K141-K145, and K147-K151 are also prohibited from land disposal. In addition, soil and debris contaminated with these radioactive mixed wastes are prohibited from land disposal.

(c) Between December 19, 1994 and September 19, 1996, the wastes included in paragraphs (b) of this section may be disposed in a landfill or surface impoundment, only if such unit is in compliance with the requirements specified in § 268.5(h)(2) of this Part.

(d) The requirements of paragraphs (a), (b), and (c) of this section do not apply if:

(1) The wastes meet the applicable treatment standards specified in Subpart D of this part;

(2) Persons have been granted an exemption from a prohibition pursuant to a petition under § 268.6, 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 § 268.44;

(4) Persons have been granted an extension to the effective date of a prohibition pursuant to § 268.5, with respect to these wastes covered by the extension.

(e) To determine whether a hazardous waste identified in this section exceeds the applicable treatment standards specified in § 268.40, 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 constituents in excess of the applicable Subpart D levels, the waste is prohibited from land disposal, and all requirements of part 268 are applicable, except as otherwise specified.

§ 268.39 Waste specific prohibitions—spent aluminum potliners; reactive; and carbamate wastes.

(a) On July 8, 1996, the wastes specified in 40 CFR 261.32 as EPA Hazardous Waste numbers K156-K159, and K161; and in 40 CFR 261.33 as EPA Hazardous Waste numbers P127, P128, P185, P188-P192, P194, P196-P199, P201-P205, U271, U278-U280, U364, U367, U372, U373, U387, U389, U394, U395, U404, and U409-U411 are prohibited from land disposal. In addition, soil and debris contaminated with these wastes are prohibited from land disposal.

(b) On July 8, 1996, the wastes identified in 40 CFR 261.23 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 § 268.40)).

(c) On September 21, 1998, the wastes specified in 40 CFR 261.32 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) On April 8, 1998, radioactive wastes mixed with K088, K156-K159, K161, P127, P128, P185, P188-P192, P194, P196-P199, P201-P205, U271, U278-U280, U364, U367, U372, U373, U387, U389, U394, U395, U404, and U409-U411 are prohibited from land disposal. In addition, soil and debris contaminated with these radioactive mixed wastes are prohibited from land disposal.

(e) Between July 8, 1996, and April 8, 1998, the wastes included in paragraphs (a), (c), and (d) of this section may be disposed in a landfill or surface impoundment, only if such unit is in compliance with the requirements specified in § 268.5(h)(2).

(f) The requirements of paragraphs (a), (b), (c), and (d) of this section do not apply if:

(1) The wastes meet the applicable treatment standards specified in Subpart D of this part;

(2) Persons have been granted an exemption from a prohibition pursuant to a petition under § 268.6, 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 § 268.44;

(4) Persons have been granted an extension to the effective date of a prohibition pursuant to § 268.5, with respect to these wastes covered by the extension.

(g) To determine whether a hazardous waste identified in this section exceeds the applicable treatment standards specified in § 268.40, 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 constituents in excess of the applicable Subpart D levels, the waste is prohibited from land disposal, and all requirements of this part 268 are applicable, except as otherwise specified.

§ 268.40 Applicability of treatment standards.

(a) A prohibited waste identified in the table “Treatment Standards for Hazardous Wastes” may be land disposed only if it meets the requirements found in the table. For each waste, the table identifies one of three types of treatment standard requirements:

(1) All hazardous constituents in the waste or in the treatment residue must be at or below the values found in the table for that waste (“total waste standards”); or

(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 (“waste extract standards”); or

(3) The waste must be treated using the technology specified in the table (“technology standard”), which are described in detail in § 268.42, Table 1—Technology Codes and Description of Technology-Based Standards.

(b) For wastewaters, compliance with concentration level standards is based on maximums for any one day, except for D004 through D011 wastes for which the previously promulgated treatment standards based on grab samples remain in effect. For all nonwastewaters, compliance with concentration level standards is based on grab sampling. For wastes covered by the waste extract standards, the test Method 1311, the Toxicity Characteristic Leaching Procedure found in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” EPA Publication SW-846, as incorporated by reference in § 260.11, must be used to measure compliance. An exception is made for D004 and D008, for which either of two test methods may be used: Method 1311, or Method 1310B, the Extraction Procedure Toxicity Test. For wastes covered by a technology standard, the wastes may be land disposed after being treated using that specified technology or an equivalent treatment technology approved by the Administrator under the procedures set forth in § 268.42(b).

(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 section, treatment and disposal facilities may demonstrate (and certify pursuant to 40 CFR 268.7(b)(5)) compliance with the treatment standards for organic constituents specified by a footnote in the table “Treatment Standards for Hazardous Wastes” in this section, 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 40 CFR part 264, subpart O, or based on combustion in fuel substitution units operating in accordance with applicable technical requirements;

(2) The treatment or disposal facility has used the methods referenced in paragraph (d)(1) of this section 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 the treatment standards specified in this section by an order of magnitude.

(e) For characteristic wastes (D001-D043) that are subject to treatment standards in the following table “Treatment Standards for Hazardous Wastes,” and are not managed in a wastewater treatment system that is regulated under the Clean Water Act (CWA), that is CWA-equivalent, or that is injected into a Class I nonhazardous deep injection well, all underlying hazardous constituents (as defined in § 268.2(i)) must meet Universal Treatment Standards, found in § 268.48, Table Universal Treatment Standards, prior to land disposal as defined in § 268.2(c) of this part.

(f) The treatment standards for F001-F005 nonwastewater constituents carbon disulfide, cyclohexanone, and/or methanol apply to wastes which contain only one, two, or three of these constituents. Compliance is measured for these constituents in the waste extract from test Method 1311, the Toxicity Characteristic Leaching Procedure found in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, EPA Publication SW-846, as incorporated by reference in § 260.11. If the waste contains any of these three constituents along with any of the other 25 constituents found in F001-F005, then compliance with treatment standards for carbon disulfide, cyclohexanone, and/or methanol are not required.

(g) Between August 26, 1996 and March 4, 1999 the treatment standards for the wastes specified in 40 CFR 261.32 as EPA Hazardous Waste numbers K156-K161; and in 40 CFR 261.33 as EPA Hazardous Waste numbers P127, P128, P185, P188-P192, P194, P196-P199, P201-P205, U271, U277-U280, U364-U367, U372, U373, U375-U379, U381-U387, U389-U396, U400-U404, U407, and U409-U411; and soil contaminated with these wastes; may be satisfied by either meeting the constituent concentrations presented in the table “Treatment Standards for Hazardous Wastes” in this section, or by treating the waste by the following technologies: combustion, as defined by the technology code CMBST at § 268.42 Table 1, for nonwastewaters; and, biodegradation as defined by the technology code BIODG, carbon adsorption as defined by the technology code CARBN, chemical oxidation as defined by the technology code CHOXD, or combustion as defined as technology code CMBST at § 268.42 Table 1, for wastewaters.

(h) Prohibited D004-D011 mixed radioactive wastes and mixed radioactive listed wastes containing metal constituents, that were previously treated by stabilization to the treatment standards in effect at that time and then put into storage, do not have to be re-treated to meet treatment standards in this section prior to land disposal.

(i) [Reserved]

(j) Effective September 4, 1998, the treatment standards for the wastes specified in 40 CFR 261.33 as EPA Hazardous Waste numbers P185, P191, P192, P197, U364, U394, and U395 may be satisfied by either meeting the constituent concentrations presented in the table “Treatment Standards for Hazardous Wastes” in this section, or by treating the waste by the following technologies: combustion, as defined by the technology code CMBST at § 268.42 Table 1 of this Part, for nonwastewaters; and, biodegradation as defined by the technology code BIODG, carbon adsorption as defined by the technology code CARBN, chemical oxidation as defined by the technology code CHOXD, or combustion as defined as technology code CMBST at § 268.42 Table 1 of this Part, for wastewaters.

Treatment Standards For Hazardous Wastes

[Note: NA means not applicable]

Waste code

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 § 261.21(a)(1) High TOC Subcategory.

NA

NA

DEACT and meet § 268.48 standards 8 ; or RORGS; or CMBST

DEACT and meet § 268.48 standards 8 ; or RORGS; or CMBST

High TOC Ignitable Characteristic Liquids Subcategory based on 40 CFR 261.21(a)(1)—Greater than or equal to 10% total organic carbon. (Note: This subcategory consists of nonwastewaters only.)

NA

NA

NA

RORGS; CMBST; or POLYM

D002 9

Corrosive Characteristic Wastes.

NA

NA

DEACT and meet § 268.48 standards 8

DEACT and meet § 268.48 standards 8

D002, D004, D005, D006, D007, D008, D009, D010, D011

Radioactive high level wastes generated during the reprocessing of fuel rods. (Note: This subcategory consists of nonwastewaters only.)

Corrosivity (pH) Arsenic Barium Cadmium Chromium (Total) Lead Mercury Selenium Silver

NA 7440-38-2 7440-39-3 7440-43-9 7440-47-3 7439-92-1 7439-97-6 7782-49-2 7440-22-4

NA NA NA NA NA NA NA NA NA

HLVIT HLVIT HLVIT HLVIT HLVIT HLVIT HLVIT HLVIT HLVIT

D003 9

Reactive Sulfides Subcategory based on 261.23(a)(5).

NA

NA

DEACT

DEACT

Explosives Subcategory based on 261.23(a)(6),(7), and (8).

NA

NA

DEACT and meet § 268.48 standards 8

DEACT and meet § 268.48 standards 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 261.23(a)(1).

NA

NA

DEACT and meet § 268.48 standards 8

DEACT and meet § 268.48 standards 8

Water Reactive Subcategory based on 261.23(a)(2), (3), and (4). (Note: This subcategory consists of nonwastewaters only).

NA

NA

NA

DEACT and meet § 268.48 standards 8

Reactive Cyanides Subcategory based on 261.23(a)(5).

Cyanides (Total) 7

57-12-5

Reserved

590

Cyanides (Amenable) 7

57-12-5

0.86

30

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 SW846.

Arsenic

7440-38-2

1.4 and meet § 268.48 standards 8

5.0 mg/L TCLP and meet § 268.48 standards 8

D005 9

Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for barium based on the toxicity characteristic leaching procedure (TCLP) in SW846.

Barium

7440-39-3

1.2 and meet § 268.48 standards 8

21 mg/L TCLP and meet § 268.48 standards 8

D006 9

Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for cadmium based on the toxicity characteristic leaching procedure (TCLP) in SW846.

Cadmium

7440-43-9

0.69 and meet § 268.48 standards 8

0.11 mg/L TCLP and meet § 268.48 standards 8

Cadmium Containing Batteries Subcategory. (Note: This subcategory consists of nonwastewaters only).

Cadmium

7440-43-9

NA

RTHRM

Radioactively contaminated cadmium containing batteries. ( Note: This subcategory consists of nonwastewaters only)

Cadmium

7440-43-9

NA

Macroencapsulation in accordance with 40 CFR 268.45.

D007 9

Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for chromium based on the toxicity characteristic leaching procedure (TCLP) in SW846.

Chromium (Total)

7440-47-3

2.77 and meet § 268.48 standards 8

0.60 mg/L TCLP and meet § 268.48 standards 8

D008 9

Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for lead based on the toxicity characteristic leaching procedure (TCLP) in SW846.

Lead

7439-92-1

0.69 and meet § 268.48 standards 8

0.75 mg/L TCLP and meet § 268.48 standards 8

Lead Acid Batteries Subcategory (Note: This standard only applies to lead acid batteries that are identified as RCRA hazardous wastes and that are not excluded elsewhere from regulation under the land disposal restrictions of 40 CFR 268 or exempted under other EPA regulations (see 40 CFR 266.80). This subcategory consists of nonwastewaters only.)

Lead

7439-92-1

NA

RLEAD

Radioactive Lead Solids Subcategory (Note: These lead solids include, but are not limited to, all forms of lead shielding and other elemental forms of lead. These lead solids do not include treatment residuals such as hydroxide sludges, other wastewater treatment residuals, or incinerator ashes that can undergo conventional pozzolanic stabilization, nor do they include organo-lead materials that can be incinerated and stabilized as ash. This subcategory consists of nonwastewaters only.)

Lead

7439-92-1

NA

MACRO

D009 9

Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the toxicity characteristic leaching procedure (TCLP) in SW846; and contain greater than or equal to 260 mg/kg total mercury that also contain organics and are not incinerator residues. (High Mercury-Organic Subcategory)

Mercury

7439-97-6

NA

IMERC; OR RMERC

Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the toxicity characteristic leaching procedure (TCLP) in SW846; and contain greater than or equal to 260 mg/kg total mercury that are inorganic, including incinerator residues and residues from RMERC. (High Mercury-Inorganic Subcategory)

Mercury

7439-97-6

NA

RMERC

Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the toxicity characteristic leaching procedure (TCLP) in SW846; and contain less than 260 mg/kg total mercury and that are residues from RMERC only. (Low Mercury Subcategory)

Mercury

7439-97-6

NA

0.20 mg/L TCLP and meet § 268.48 standards 8

All other nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the toxicity characteristic leaching procedure (TCLP) in SW846; and contain less than 260 mg/kg total mercury and that are not residues from RMERC. (Low Mercury Subcategory)

Mercury

7439-97-6

NA

0.025 mg/L TCLP and meet § 268.48 standards 8

All D009 wastewaters.

Mercury

7439-97-6

0.15 mg/L TCLP and meet § 268.48 standards 8

NA

Elemental mercury contaminated with radioactive materials. (Note: This subcategory consists of nonwastewaters only.)

Mercury

7439-97-6

NA

AMLGM

Hydraulic oil contaminated with Mercury Radioactive Materials Subcategory. (Note: This subcategory consists of nonwastewaters only.)

Mercury

7439-97-6

NA

IMERC

Radioactively contaminated mercury containing batteries. (Note: This subcategory consists of nonwastewaters only)

Mercury

7439-97-6

NA

Macroencapsulation in accordance with 40 CFR 268.45.

D010 9

Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for selenium based on the toxicity characteristic leaching procedure (TCLP) in SW846.

Selenium

7782-49-2

0.82 and meet § 268.48 standards 8

5.7 mg/L TCLP and meet § 268.48 standards 8

D011 9

Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for silver based on the toxicity characteristic leaching procedure (TCLP) in SW846.

Silver

7440-22-4

0.43 and meet § 268.48 standards 8

0.14 mg/L TCLP and meet § 268.48 standards 8

Radioactively contaminated silver containing batteries. Note: This subcategory consists of nonwastewaters only)

Silver

7440-22-4

NA

Macroencapsulation in accordance with 40 CFR 268.45.

D012 9

Wastes that are TC for Endrin based on the TCLP in SW846 Method 1311.

Endrin

72-20-8

BIODG; or CMBST

0.13 and meet § 268.48 standards 8

Endrin aldehyde

7421-93-4

BIODG; or CMBST

0.13 and meet § 268.48 standards 8

D013 9

Wastes that are TC for Lindane based on the TCLP in SW846 Method 1311.

alpha-BHC

319-84-6

CARBN; or CMBST

0.066 and meet § 268.48 standards 8

beta-BHC

319-85-7

CARBN; or CMBST

0.066 and meet § 268.48 standards 8

delta-BHC

319-86-8

CARBN; or CMBST

0.066 and meet § 268.48 standards 8

gamma-BHC (Lindane)

58-89-9

CARBN; or CMBST

0.066 and meet § 268.48 standards 8

D014 9

Wastes that are TC for Methoxychlor based on the TCLP in SW846 Method 1311.

Methoxychlor

72-43-5

WETOX or CMBST

0.18 and meet § 268.48 standards 8

D015 9

Wastes that are TC for Toxaphene based on the TCLP in SW846 Method 1311.

Toxaphene

8001-35-2

BIODG or CMBST

2.6 and meet § 268.48 standards 8

D016 9

Wastes that are TC for 2,4-D (2,4-Dichlorophenoxyacetic acid) based on the TCLP in SW846 Method 1311.

2,4,-D (2,4-Dichlorophenoxyacetic acid)

94-75-7

CHOXD, BIODG, or CMBST

10 and meet § 268.48 standards 8

D017 9

Wastes that are TC for 2,4,5-TP (Silvex) based on the TCLP in SW846 Method 1311.

2,4,5-TP (Silvex)

93-72-1

CHOXD or CMBST

7.9 and meet § 268.48 standards 8

D018 9

Wastes that are TC for Benzene based on the TCLP in SW846 Method 1311.

Benzene

71-43-2

0.14 and meet § 268.48 standards 8

10 and meet § 268.48 standards 8

D019 9

Wastes that are TC for Carbon tetrachloride based on the TCLP in SW846 Method 1311.

Carbon tetrachloride

56-23-5

0.057 and meet § 268.48 standards 8

6.0 and meet § 268.48 standards 8

D020 9

Wastes that are TC for Chlordane based on the TCLP in SW846 Method 1311.

Chlordane (alpha and gamma isomers)

57-74-9

0.0033 and meet § 268.48 standards 8

0.26 and meet § 268.48 standards 8

D021 9

Wastes that are TC for Chlorobenzene based on the TCLP in SW846 Method 1311.

Chlorobenzene

108-90-7

0.057 and meet § 268.48 standards 8

6.0 and meet § 268.48 standards 8

D022 9

Wastes that are TC for Chloroform based on the TCLP in SW846 Method 1311.

Chloroform

67-66-3

0.046 and meet § 268.48 standards 8

6.0 and meet § 268.48 standards 8

D023 9

Wastes that are TC for o-Cresol based on the TCLP in SW846 Method 1311.

o-Cresol

95-48-7

0.11 and meet § 268.48 standards 8

5.6 and meet § 268.48 standards 8

D024 9

Wastes that are TC for m-Cresol based on the TCLP in SW846 Method 1311.

m-Cresol (difficult to distinguish from p-cresol)

108-39-4

0.77 and meet § 268.48 standards 8

5.6 and meet § 268.48 standards 8

D025 9

Wastes that are TC for p-Cresol based on the TCLP in SW846 Method 1311.

p-Cresol (difficult to distinguish from m-cresol)

106-44-5

0.77 and meet § 268.48 standards 8

5.6 and meet § 268.48 standards 8

D026 9

Wastes that are TC for Cresols (Total) based on the TCLP in SW846 Method 1311.

Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations)

1319-77-3

0.88 and meet § 268.48 standards 8

11.2 and meet § 268.48 standards 8

D027 9

Wastes that are TC for p-Dichlorobenzene based on the TCLP in SW846 Method 1311.

p-Dichlorobenzene (1,4-Dichlorobenzene)

106-46-7

0.090 and meet § 268.48 standards 8

6.0 and meet § 268.48 standards 8

D028 9

Wastes that are TC for 1,2-Dichloroethane based on the TCLP in SW846 Method 1311.

1,2-Dichloroethane

107-06-2

0.21 and meet § 268.48 standards 8

6.0 and meet § 268.48 standards 8

D029 9

Wastes that are TC for 1,1-Dichloroethylene based on the TCLP in SW846 Method 1311.

1,1-Dichloroethylene

75-35-4

0.025 and meet § 268.48 standards 8

6.0 and meet § 268.48 standards 8

D030 9

Wastes that are TC for 2,4-Dinitrotoluene based on the TCLP in SW846 Method 1311.

2,4-Dinitrotoluene

121-14-2

0.32 and meet § 268.48 standards 8

140 and meet § 268.48 standards 8

D031 9

Wastes that are TC for Heptachlor based on the TCLP in SW846 Method 1311.

Heptachlor

76-44-8

0.0012 and meet § 268.48 standards 8

0.066 and meet § 268.48 standards 8

Heptachlor epoxide

1024-57-3

0.016 and meet § 268.48 standards 8

0.066 and meet § 268.48 standards 8

D032 9

Wastes that are TC for Hexachlorobenzene based on the TCLP in SW846 Method 1311.

Hexachlorobenzene

118-74-1

0.055 and meet § 268.48 standards 8

10 and meet § 268.48 standards 8

D033 9

Wastes that are TC for Hexachlorobutadiene based on the TCLP in SW846 Method 1311.

Hexachlorobutadiene

87-68-3

0.055 and meet § 268.48 standards 8

5.6 and meet § 268.48 standards 8

D034 9

Wastes that are TC for Hexachloroethane based on the TCLP in SW846 Method 1311.

Hexachloroethane

67-72-1

0.055 and meet § 268.48 standards 8

30 and meet § 268.48 standards 8

D035 9

Wastes that are TC for Methyl ethyl ketone based on the TCLP in SW846 Method 1311.

Methyl ethyl ketone

78-93-3

0.28 and meet § 268.48 standards 8

36 and meet § 268.48 standards 8

D036 9

Wastes that are TC for Nitrobenzene based on the TCLP in SW846 Method 1311.

Nitrobenzene

98-95-3

0.068 and meet § 268.48 standards 8

14 and meet § 268.48 standards 8

D037 9

Wastes that are TC for Pentachlorophenol based on the TCLP in SW846 Method 1311.

Pentachlorophenol

87-86-5

0.089 and meet § 268.48 standards 8

7.4 and meet § 268.48 standards 8

D038 9

Wastes that are TC for Pyridine based on the TCLP in SW846 Method 1311.

Pyridine

110-86-1

0.014 and meet § 268.48 standards 8

16 and meet § 268.48 standards 8

D039 9

Wastes that are TC for Tetrachloroethylene based on the TCLP in SW846 Method 1311.

Tetrachloroethylene

127-18-4

0.056 and meet § 268.48 standards 8

6.0 and meet § 268.48 standards 8

D040 9

Wastes that are TC for Trichloroethylene based on the TCLP in SW846 Method 1311.

Trichloroethylene

79-01-6

0.054 and meet § 268.48 standards 8

6.0 and meet § 268.48 standards 8

D041 9

Wastes that are TC for 2,4,5-Trichlorophenol based on the TCLP in SW846 Method 1311.

2,4,5-Trichlorophenol

95-95-4

0.18 and meet § 268.48 standards 8

7.4 and meet § 268.48 standards 8

D042 9

Wastes that are TC for 2,4,6-Trichlorophenol based on the TCLP in SW846 Method 1311.

2,4,6-Trichlorophenol

88-06-2

0.035 and meet § 268.48 standards 8

7.4 and meet § 268.48 standards 8

D043 9

Wastes that are TC for Vinyl chloride based on the TCLP in SW846 Method 1311.

Vinyl chloride

75-01-4

0.27 and meet § 268.48 standards 8

6.0 and meet § 268.48 standards 8

F001, F002, F003, F004, & F005

F001, F002, F003, F004 and/or F005 solvent wastes that contain any combination of one or more of the following spent solvents: acetone, benzene, n-butyl alcohol, carbon disulfide, carbon tetrachloride, chlorinated fluorocarbons, chlorobenzene, o-cresol, m-cresol, p-cresol, cyclohexanone, o-dichlorobenzene, 2-ethoxyethanol, ethyl acetate, ethyl benzene, ethyl ether, isobutyl alcohol, methanol, methylene chloride, methyl ethyl ketone, methyl isobutyl ketone, nitrobenzene, 2-nitropropane, pyridine, tetrachloroethylene, toluene, 1,1,1-trichloroethane, 1,1,2-trichloroethane, 1,1,2-trichloro-1,2,2-trifluoroethane, trichloroethylene, trichlorofluoromethane, and/or xylenes [except as specifically noted in other subcategories]. See further details of these listings in § 261.31.

Acetone Benzene n-Buthyl alcohol Carbon disulfide Carbon tetrachloride Chlorobenzene o-Cresol m-Cresol (difficult to distinguish from p-cresol) p-Cresol (difficult to distinguish from m-cresol) Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations)

67-64-1 71-43-2 71-36-3 75-15-0 56-23-5 108-90-7 95-48-7 108-39-4 106-44-5 1319-77-3

0.28 0.14 5.6 3.8 0.057 0.057 0.11 0.77 0.77 0.88

160 10 2.6 NA 6.0 6.0 5.6 5.6 5.6 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

Ethyl benzene

100-41-4

0.057

10

Ethyl ether

60-29-7

0.12

160

Isobutyl alcohol

78-83-1

5.6

170

Methanol

67-56-1

5.6

NA

Methylene chloride

75-9-2

0.089

30

Methyl ethyl ketone

78-93-3

0.28

36

Methyl isobutyl ketone

108-10-1

0.14

33

Nitrobenzene

98-95-3

0.068

14

Pyridine

110-86-1

0.014

16

Tetrachloroethylene

127-18-4

0.056

6.0

Toluene

108-88-3

0.080

10

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

Trichloroethylene

79-01-6

0.054

6.0

Trichlorofluoromethane

75-69-4

0.020

30

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

F003 and/or F005 solvent wastes that contain any combination of one or more of the following three solvents as the only listed F001-5 solvents: carbon disulfide, cyclohexanone, and/or methanol. (formerly 268.41(c))

Carbon disulfide Cyclohexanone Methanol

75-15-0 108-94-1 67-56-1

3.8 0.36 5.6

4.8 mg/L TCLP 0.75 mg/L TCLP 0.75 mg/L TCLP

F005 solvent waste containing 2-Nitropropane as the only listed F001-5 solvent.

2-Nitropropane

79-46-9

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

F005 solvent waste containing 2-Ethoxyethanol as the only listed F001-5 solvent.

2-Ethoxyethanol

110-80-5

BIODG; or CMBST

CMBST

F006

Wastewater treatment sludges from electroplating operations except from the following processes: (1) Sulfuric acid anodizing of aluminum; (2) tin plating on carbon steel; (3) zinc plating (segregated basis) on carbon steel; (4) aluminum or zinc-aluminum plating on carbon steel; (5) cleaning/stripping associated with tin, zinc and aluminum plating on carbon steel; and (6) chemical etching and milling of aluminum.

Cadmium Chromium (Total) Cyanides (Total) 7 Cyanides (Amenable) 7 Lead Nickel Silver

7440-43-9 7440-47-3 57-12-5 57-12-5 7439-92-1 7440-02-0 7440-22-4

0.69 2.77 1.2 0.86 0.69 3.98 NA

0.11 mg/L TCLP 0.60 mg/L TCLP 590 30 0.75 mg/L TCLP 11 mg/L TCLP 0.14 mg/L TCLP

F007

Spent cyanide plating bath solutions from electroplating operations.

Cadmium Chromium (Total)

7440-43-9 7440-47-3

NA 2.77

0.11 mg/L TCLP 0.60 mg/L TCLP

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 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 Chromium (Total) Cyanides (Total) 7

7440-43-9 7440-47-3 57-12-5

NA 2.77 1.2

0.11 mg/L TCLP 0.60 mg/L TCLP 590

Cyanides (Amenable) 7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 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 Chromium (Total)

7440-43-9 7440-47-3

NA 2.77

0.11 mg/L TCLP 0.60 mg/L TCLP

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 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 Cyanides (Amenable) 7

57-12-5 57-12-5

1.2 0.86

590 NA

F011

Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations.

Cadmium Chromium (Total)

7440-43-9 7440-47-3

NA 2.77

0.11 mg/L TCLP 0.60 mg/L TCLP

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 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 Chromium (Total)

7440-43-9 7440-47-3

NA 2.77

0.11 mg/L TCLP 0.60 mg/L TCLP

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 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) Cyanides (Total) 7 Cyanides (Amendable) 7

7440-47-3 57-12-5 57-12-5

2.77 1.2 0.86

0.60 mg/L TCLP 590 30

F020, F021, F022, F023, F026

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of: (1) tri- or tetrachlorophenol, or of intermediates used to produce their pesticide derivatives, excluding wastes from the production of Hexachlorophene from highly purified, 2,4,5-trichlorophenol (F020); (2) pentachlorophenol, or of intermediates used to produce its derivatives ( i.e. , F021); (3) tetra-, penta-, or hexachlorobenzenes under alkaline conditions ( i.e. , F022); and from the production of materials on equipment previously used for the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of: (1) tri- or tetrachlorophenols, excluding wastes from equipment used only for the production of Hexachlorophene from highly purified 2,4,5-trichlorophenol (F023); (2) tetra- penta, or hexachlorobenzenes under alkaline conditions ( i.e. , F026).

HxCDDs (All Hexachlorodibenzo-p-dioxins) Hx CDFs (All Hexachlorodibenzofurans) PeCDDs (All Pentachlorodibenzo-p-dioxins) PeCDFs (All Pentachlorodibenzofurans) Pentachlorophenol TCDDs (All Tetrachlorodibenzo-p-dioxins) TCDFs (All Tetrachlorodibenzofurans) 2,4,5-Trichlorophenol 2,4-6-Trichlorophenol 2,3,4,6-Tetrachlorophenol

NA NA NA NA 87-86-5 NA NA 95-95-4 88-06-2 58-90-2

0.000063 0.000063 0.000063 0.000035 0.089 0.000063 0.000063 0.18 0.035 0.030

0.001 0.001 0.001 0.001 7.4 0.001 0.001 7.4 7.4 7.4

F024

Process wastes, including but not limited to, distillation residues, heavy ends, tars, and reactor clean-out wastes, from the production of certain chlorinated aliphatic hydrocarbons by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. (This listing does not include wastewaters, wastewater treatment sludges, spent catalysts, and wastes listed in § 261.31 or § 261.32).

All F024 wastes 2-Chloro-1,3-butadiene 3-Chloropropylene 1,1-Dichloroethane 1,2-Dichloroethane 1,2-Dichloropropane cis-1,3-Dichloropropylene trans-1-3-Dichloropropylene bis(2-Ethylhexyl)phthalate Hexachloroethane Chromium (Total) Nickel

NA 126-99-8 107-05-1 75-34-3 107-06-2 78-87-5 10061-01-5 10061-02-6 117-81-7 67-72-1 7440-47-3 7440-02-0

CMBST 11 0.057 0.036 0.059 0.21 0.85 0.036 0.036 0.28 0.055 2.77 3.98

CMBST 11 0.28 30 6.0 6.0 18 18 18 28 30 0.60 mg/L TCLP 11 mg/L TCLP

F025

Condensed light ends from the production of certain chlorinated aliphatic hydrocarbons, by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. F025—Light Ends Subcategory

Carbon tetrachloride Chloroform 1,2-Dichloroethane 1,1-Dichloroethylene Methylene chloride 1,1,2-Trichloroethane Trichloroethylene Vinyl chloride

56-23-5 67-66-3 107-06-2 75-35-4 75-9-2 79-00-5 79-01-6 75-01-4

0.057 0.046 0.21 0.025 0.089 0.054 0.054 0.27

6.0 6.0 6.0 6.0 30 6.0 6.0 6.0

Spent filters and filter aids, and spent desiccant wastes from the production of certain chlorinated aliphatic hydrocarbons, by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. F025—Spent Filters/Aids and Desiccants Subcategory

Carbon tetrachloride Chloroform Hexachlorobenzene Hexachlorobutadiene Hexachloroethane Methylene chloride 1,1,2-Trichloroethane Trichloroethylene Vinyl chloride

56-23-5 67-66-3 118-74-1 87-68-3 67-72-1 75-9-2 79-00-5 79-01-6 75-01-4

0.057 0.046 0.055 0.055 0.055 0.089 0.054 0.054 0.27

6.0 6.0 10 5.6 30 30 6.0 6.0 6.0

F027

Discarded unused formulations containing tri-, tetra-, or pentachlorophenol or discarded unused formulations containing compounds derived from these chlorophenols. (This listing does not include formulations containing hexachlorophene synthesized from prepurified 2,4,5-trichlorophenol as the sole component.)

HxCDDs (All Hexachlorodibenzo-p-dioxins) HxCDFs (All Hexachlorodibenzofurans) PeCDDs (All Pentachlorodibenzo-p-dioxins) PeCDFs (All Pentachlorodibenzofurans) Pentachlorophenol TCDDs (All Tetrachlorodibenzo-p-dioxins) TCDFs (All Tetrachlorodibenzofurans) 2,4,5-Trichlorophenol 2,4,6-Trichlorophenol 2,3,4,6-Tetrachlorophenol

NA NA NA NA 87-86-5 NA NA 95-95-4 88-06-2 58-90-2

0.000063 0.000063 0.000063 0.000035 0.089 0.000063 0.000063 0.18 0.035 0.030

0.001 0.001 0.001 0.001 7.4 0.001 0.001 7.4 7.4 7.4

F028

Residues resulting from the incineration or thermal treatment of soil contaminated with EPA Hazardous Wastes Nos. F020, F021, F023, F026, and F027.

HxCDDs (All Hexachlorodibenzo-p-dioxins) HxCDFs (All Hexachlorodibenzofurans) PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA NA NA

0.000063 0.000063 0.000063

0.001 0.001 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

0.030

7.4

F032

Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that currently use or have previously used chlorophenolic formulations (except potentially cross-contaminated wastes that have had the F032 waste code deleted in accordance with § 261.35 of this chapter or potentially cross-contaminated wastes that are otherwise currently regulated as hazardous wastes ( i.e. , F034 or F035), and where the generator does not resume or initiate use of chlorophenolic formulations). This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or penta-chlorophenol.

Acenaphthene Anthracene Benz(a)anthracene Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) Benzo(a)pyrene Chrysene Dibenz(a,h) anthracene 2-4-Dimethyl phenol Fluorene Hexachlorodibenzo-p-dioxins Hexachlorodibenzofurans

83-32-9 120-12-7 56-55-3 205-99-2 207-08-9 50-32-8 218-01-9 53-70-3 105-67-9 86-73-7 NA NA

0.059 0.059 0.059 0.11 0.11 0.061 0.059 0.055 0.036 0.059 0.000063, or CMBST 11 0.000063, or CMBST 11

3.4 3.4 3.4 6.8 6.8 3.4 3.4 8.2 14 3.4 0.001, or CMBST 11 0.001, or CMBST 11

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

0.00035, 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

0.030

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

F034

Wasteswaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use creosote formulations. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol.

Acenaphthene Anthracene Benz(a)anthracene Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) Benzo(a)pyrene

83-32-9 120-12-7 56-55-3 205-99-2 207-08-9 50-32-8

0.059 0.059 0.059 0.11 0.11 0.061

3.4 3.4 3.4 6.8 6.8 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

0.60 mg/L TCLP

F035

Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use inorganic preservatives containing arsenic or chromium. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol.

Arsenic Chromium (Total)

7440-38-2 7440-47-3

1.4 2.77

5.0 mg/L TCLP 0.60 mg/L TCLP

F037

Petroleum refinery primary oil/water/solids separation sludge—Any sludge generated from the gravitational separation of oil/water/solids during the storage or treatment of process wastewaters and oily cooling wastewaters from petroleum refineries. Such sludges include, but are not limited to, those generated in: oil/water/solids separators; tanks and impoundments; ditches and other conveyances; sumps; and stormwater units receiving dry weather flow. Sludge generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges generated in aggressive biological treatment units as defined in § 261.31(b)(2) (including sludges generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and K051 wastes are not included in this listing.

Acenaphthene Anthracene Benzene Benz(a)anthracene Benzo(a)pyrene bis(2-Ethylhexyl) phthalate Chrysene Di-n-butyl phthalate Ethylbenzene Fluorene Naphthalene Phenanthrene Phenol Pyrene Toluene Xylenes-mixed isomers (sum of o, m-, and p-xylene concentrations)

83-32-9 120-12-7 71-43-2 56-55-3 50-32-8 117-81-7 218-01-9 84-74-2 100-41-4 86-73-7 91-20-3 85-01-8 108-95-2 129-00-0 108-88-3 1330-20-7

0.059 0.059 0.14 0.059 0.061 0.28 0.059 0.057 0.057 0.059 0.059 0.059 0.039 0.067 0.080 0.32

NA 3.4 10 3.4 3.4 28 3.4 28 10 NA 5.6 5.6 6.2 8.2 10 30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total) 7

57-12-5

1.2

590

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

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 floatation (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 § 261.31(b)(2) (including sludges and floats generated in one or more additional units after wastewaters have been treated in aggressive biological units) and F037, K048, and K051 are not included in this listing.

Benzene Benzo(a)pyrene bis(2-Ethylhexyl) phthalate Chrysene Di-n-butyl phthalate Ethylbenzene Fluorene Naphthalene Phenanthrene Phenol Pyrene Toluene Xylenes-mixed isomers (sum of o, m-, and p-xylene concentrations) Chromium (Total) Cyanides (Total) 7 Lead

71-43-2 50-32-8 117-81-7 218-01-9 84-74-2 100-41-4 86-73-7 91-20-3 85-01-8 108-95-2 129-00-0 108-88-3 1330-20-7 7440-47-3 57-12-5 7439-92-1

0.14 0.061 0.28 0.059 0.057 0.057 0.059 0.059 0.059 0.039 0.067 0.080 0.32 2.77 1.2 0.69

10 3.4 28 3.4 28 10 NA 5.6 5.6 6.2 8.2 10 30 0.60 mg/L TCLP 590 NA

Nickel

7440-02-0

NA

11 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 subpart D of this part. (Leachate resulting from the disposal of one or more of the following EPA Hazardous Wastes and no other Hazardous Wastes retains its EPA Hazardous Waste Number(s): F020, F021, F022, F026, F027, and/or F028.)

Acenaphthylene Acenaphthene Acetone Acetonitrile Acetophenone 2-Acetylaminofluorene Acrolein

208-96-8 83-32-9 67-64-1 75-05-8 96-86-2 53-96-3 107-02-8

0.059 0.059 0.28 5.6 0.010 0.059 0.29

3,4 3.4 160 NA 9.7 140 NA

Acrylonitrile

107-13-1

0.24

84

Aldrin

309-00-2

0.021

0.066

4-Aminobiphenyl

92-67-1

0.13

NA

Aniline

62-53-3

0.81

14

o-Anisidine (2-methoxyaniline)

90-04-0

0.010

0.66

Anthracene

120-12-7

0.059

3.4

Aramite

140-57-8

0.36

NA

alpha-BHC

319-84-6

0.00014

0.066

beta-BHC

319-85-7

0.00014

0.066

delta-BHC

319-86-8

0.023

0.066

gamma-BHC

58-89-9

0.0017

0.066

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Benzo(g,h,i)perylene

191-24-2

0.0055

1.8

Benzo(a)pyrene

50-32-8

0.061

3.4

Bromodichloromethane

75-27-4

0.35

15

Methyl bromide (Bromomethane)

74-83-9

0.11

15

4-Bromophenyl phenyl ether

101-55-3

0.055

15

n-Butyl alcohol

71-36-3

5.6

2.6

Butyl benzyl phthalate

85-68-7

0.017

28

2-sec-Buty-4,6-dinitrophenol (Dinoseb)

88-85-7

0.066

2.5

Carbon disulfide

75-15-0

3.8

NA

Carbon tetrachloride

56-23-5

0.057

6.0

Chlordane (alpha and gamma isomers)

57-74-9

0.0033

0.26

p-Chloroaniline

106-47-8

0.46

16

Chlorobenzene

108-90-7

0.057

6.0

Chlorobenzilate

510-15-6

0.10

NA

2-Chloro-1,3-butadiene

126-99-8

0.057

NA

Chlorodibromomethane

124-48-1

0.057

15

Chloroethane

75-00-3

0.27

6.0

bis(2-Chloroethoxy)methane

111-91-1

0.036

7.2

bis(2-Chloroethyl)ether

111-44-4

0.033

6.0

Chloroform

67-66-3

0.046

6.0

bis(2-Chloroisopropyl)ether

39638-32-9

0.055

7.2

p-Chloro-m-cresol

59-50-7

0.018

14

Chloromethane (Methyl chloride)

74-87-3

0.19

30

2-Chloronaphthalene

91-58-7

0.055

5.6

2-Chlorophenol

95-57-8

0.044

5.7

3-Chloropropylene

107-05-1

0.036

30

Chrysene

218-01-9

0.059

3.4

o-Cresol

95-48-7

0.11

5.6

p-Cresidine

120-71-8

0.010

0.66

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

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

Dibromomethane

74-95-3

0.11

15

2,4-D (2,4-Dichlorophenoxyacetic acid)

94-75-7

0.72

10

o,p′-DD

53-19-0

0.023

0.087

p,p′-DDD

72-54-8

0.023

0.087

o,p′-DDE

3424-82-6

0.031

0.087

p,p′-DDE

72-55-9

0.031

0.087

o,p′-DDT

789-02-6

0.0039

0.087

p,p′-DDT

50-29-3

0.0039

0.087

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Dibenz(a,e)pyrene

192-65-4

0.061

NA

m-Dichlorobenzene

541-73-1

0.036

6.0

o-Dichlorobenzene

95-50-1

0.088

6.0

p-Dichlorobenzene

106-46-7

0.090

6.0

Dichlorodifluoromethane

75-71-8

0.23

7.2

1,1-Dichloroethane

75-34-3

0.059

6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

1,1-Dichloroethylene

75-35-4

0.025

6.0

trans-1,2-Dichloroethylene

156-60-5

0.054

30

2,4-Dichlorophenol

120-83-2

0.044

14

2,6-Dichlorophenol

87-65-0

0.044

14

1,2-Dichloropropane

78-87-5

0.85

18

cis-1,3-Dichloropropylene

10061-01-5

0.036

18

trans-1,3-Dichloropropylene

10061-02-6

0.036

18

Dieldrin

60-57-1

0.017

0.13

Diethyl phthalate

84-66-2

0.20

28

2,4-Dimethylaniline (2,4-xylidine)

95-68-1

0.010

0.66

2-4-Dimethyl phenol

105-67-9

0.036

14

Dimethyl phthalate

131-11-3

0.047

28

Di-n-butyl phthalate

84-74-2

0.057

28

1,4-Dinitrobenzene

100-25-4

0.32

2.3

4,6-Dinitro-o-cresol

534-52-1

0.28

160

2,4-Dinitrophenol

51-28-5

0.12

160

2,4-Dinitrotoluene

121-14-2

0.32

140

2,6-Dinitrotoluene

606-20-2

0.55

28

Di-n-octyl phthalate

117-84-0

0.017

28

Di-n-propylnitrosamine

621-64-7

0.40

14

1,4-Dioxane

123-91-1

12.0

170

Diphenylamine (difficult to distinguish from diphenylnitrosamine)

122-39-4

0.92

NA

Diphenylnitrosamine (difficult to distinguish from diphenylamine)

86-30-6

0.92

NA

1,2-Diphenylhydrazine

122-66-7

0.087

NA

Disulfoton

298-04-4

0.017

6.2

Endosulfan I

939-98-8

0.023

0.066

Endosulfan II

33213-6-5

0.029

0.13

Endosulfan sulfate

1031-07-8

0.029

0.13

Endrin

72-20-8

0.0028

0.13

Endrin aldehyde

7421-93-4

0.025

0.13

Ethyl acetate

141-78-6

0.34

33

Ethyl cyanide (Propanenitrile)

107-12-0

0.24

360

Ethyl benzene

100-41-4

0.057

10

Ethyl ether

60-29-7

0.12

160

bis(2-Ethylhexyl) phthalate

117-81-7

0.28

28

Ethyl methacrylate

97-63-2

0.14

160

Ethylene oxide

75-21-8

0.12

NA

Famphur

52-85-7

0.017

15

Fluoranthene

206-44-0

0.068

3.4

Fluorene

86-73-7

0.059

3.4

Heptachlor

76-44-8

0.0012

0.066

Heptachlor epoxide

1024-57-3

0.016

0.066

1,2,3,4,6,7,8-Heptachlorodibenzo- p -dioxin (1,2,3,4,6,7,8-HpCDD)

35822-46-9

0.000035

0.0025

1, 2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF)

67562-39-4

0.000035

0.0025

1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF)

55673-89-7

0.000035

0.0025

Hexachlorobenzene

118-74-1

0.055

10

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

Hexachloroethane

67-72-1

0.055

30

Hexachloropropylene

1888-71-7

0.035

30

Indeno (1,2,3-c,d) pyrene

193-39-5

0.0055

3.4

Indomethane

74-88-4

0.019

65

Isobutyl alcohol

78-83-1

5.6

170

Isodrin

465-73-6

0.021

0.066

Isosafrole

120-58-1

0.081

2.6

Kepone

143-50-8

0.0011

0.13

Methacylonitrile

126-98-7

0.24

84

Methanol

67-56-1

5.6

NA

Methapyrilene

91-80-5

0.081

1.5

Methoxychlor

72-43-5

0.25

0.18

3-Methylcholanthrene

56-49-5

0.0055

15

4,4-Methylene bis(2-chloroaniline)

101-14-4

0.50

30

Methylene chloride

75-09-2

0.089

30

Methyl ethyl ketone

78-93-3

0.28

36

Methyl isobutyl ketone

108-10-1

0.14

33

Methyl methacrylate

80-62-6

0.14

160

Methyl methanesulfonate

66-27-3

0.018

NA

Methyl parathion

298-00-0

0.014

4.6

Naphthalene

91-20-3

0.059

5.6

2-Naphthylamine

91-59-8

0.52

NA

p-Nitroaniline

100-01-6

0.028

28

Nitrobenzene

98-95-3

0.068

14

5-Nitro-o-toluidine

99-55-8

0.32

28

p-Nitrophenol

100-02-7

0.12

29

N-Nitrosodiethylamine

55-18-5

0.40

28

N-Nitrosodimethylamine

62-75-9

0.40

NA

N-Nitroso-di-n-butylamine

924-16-3

0.40

17

N-Nitrosomethylethylamine

10595-95-6

0.40

2.3

N-Nitrosomorpholine

59-89-2

0.40

2.3

N-Nitrosopiperidine

100-75-4

0.013

35

N-Nitrosopyrrolidine

930-55-2

0.013

35

1,2,3,4,6,7,8,9-Octachlorodibenzo- p -dioxin (OCDD)

3268-87-9

0.000063

0.005

1,2,3,4,6,7,8,9-Octachlorodibenzofuran (OCDF)

39001-02-0

0.000063

0.005

Parathion

56-38-2

0.014

4.6

Total PCBs (sum of all PCB isomers, or all Aroclors)

1336-36-3

0.10

10

Pentachlorobenzene

608-93-5

0.055

10

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

Pentachloronitrobenzene

82-68-8

0.055

4.8

Pentachlorophenol

87-86-5

0.089

7.4

Phenacetin

62-44-2

0.081

16

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

2,4-Dimethylaniline (2,4-xylidine)

108-45-2

0.010

0.66

Phorate

298-02-2

0.021

4.6

Phthalic anhydride

85-44-9

0.055

NA

Pronamide

23950-58-5

0.093

1.5

Pyrene

129-00-0

0.067

8.2

Pyridine

110-86-1

0.014

16

Safrole

94-59-7

0.081

22

Silvex (2,4,5-TP)

93-72-1

0.72

7.9

2,4,5-T

93-76-5

0.72

7.9

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

2,3,4,6-Tetrachlorophenol

58-90-2

0.030

7.4

Toluene

108-88-3

0.080

10

Toxaphene

8001-35-2

0.0095

2.6

Bromoform (Tribromomethane)

75-25-2

0.63

15

1,2,4-Trichlorobenzene

120-82-1

0.055

19

1,1,1-Trichloroethane

71-55-6

0.054

6.0

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

Trichlorofluoromethane

75-69-4

0.020

30

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

1,2,3-Trichloropropane

96-18-4

0.85

30

1,1,2-Trichloro-1,2,2-trifluoroethane

76-13-1

0.057

30

tris(2,3-Dibromopropyl) phosphate

126-72-7

0.11

NA

Vinyl chloride

75-01-4

0.27

6.0

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Barium

7440-39-3

1.2

21 mg/L TCLP

Beryllium

7440-41-7

0.82

NA

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

NA

Fluoride

16984-48-8

35

NA

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Mercury

7439-97-6

0.15

0.25 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

Silver

7440-22-4

0.43

0.14 mg/L TCLP

Sulfide

8496-25-8

14

NA

Thallium

7440-28-0

1.4

NA

Vanadium

7440-62-2

4.3

NA

K001

Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote and/or pentachlorophenol.

Naphthalene Pentachlorophenol Phenanthrene Pyrene

91-20-3 87-86-5 85-01-8 129-00-0

0.059 0.089 0.059 0.067

5.6 7.4 5.6 8.2

Toluene

108-88-3

0.080

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

K002

Wastewater treatment sludge from the production of chrome yellow and orange pigments.

Chromium (Total) Lead

7440-47-3 7439-92-1

2.77 0.69

0.60 mg/L TCLP 0.75 mg/L TCLP

K003

Wastewater treatment sludge from the production of molybdate orange pigments.

Chromium (Total) Lead

7440-47-3 7439-92-1

2.77 0.69

0.60 mg/L TCLP 0.75 mg/L TCLP

K004

Wastewater treatment sludge from the production of zinc yellow pigments.

Chromium (Total) Lead

7440-47-3 7439-92-1

2.77 0.69

0.60 mg/L TCLP 0.75 mg/L TCLP

K005

Wastewater treatment sludge from the production of chrome green pigments.

Chromium (Total) Lead Cyanides (Total) 7

7440-47-3 7439-92-1 57-12-5

2.77 0.69 1.2

0.60 mg/L TCLP 0.75 mg/L TCLP 590

K006

Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous).

Chromium (Total) Lead

7440-47-3 7439-92-1

2.77 0.69

0.60 mg/L TCLP 0.75 mg/L TCLP

Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated).

Chromium (Total) Lead

7440-47-3 7439-92-1

2.77 0.69

0.60 mg/L TCLP NA

K007

Wastewater treatment sludge from the production of iron blue pigments.

Chromium (Total) Lead Cyanides (Total) 7

7440-47-3 7439-92-1 57-12-5

2,77 0.69 1.2

0.60 mg/L TCLP 0.75 mg/L TCLP 590

K008

Oven residue from the production of chrome oxide green pigments.

Chromium (Total) Lead

7440-47-3 7439-92-1

2.77 0.69

0.60 mg/L TCLP 0.75 mg/L TCLP

K009

Distillation bottoms from the production of acetaldehyde from ethylene.

Chloroform

67-66-3

0.046

6.0

K010

Distillation side cuts from the production of acetaldehyde from ethylene.

Chloroform

67-66-3

0.046

6.0

K011

Bottom stream from the wastewater stripper in the production of acrylonitrile.

Acetonitrile Acrylonitrile

75-05-8 107-13-1

5.6 0.24

38 84

Acrylamide

79-06-1

19

23

Benzene

71-43-2

0.14

10

Cyanide (Total)

57-12-5

1.2

590

K013

Bottom stream from the acetonitrile column in the production of acrylonitrile.

Acetonitrile Acrylonitrile

75-05-8 107-13-1

5.6 0.24

38 84

Acrylamide

79-06-1

19

23

Benzene

71-43-2

0.14

10

Cyanide (Total)

57-12-5

1.2

590

K014

Bottoms from the acetonitrile purification column in the production of acrylonitrile.

Acetonitrile Acrylonitrile

75-05-8 107-13-1

5.6 0.24

38 84

Acrylamide

79-06-1

19

23

Benzene

71-43-2

0.14

10

Cyanide (Total)

57-12-5

1.2

590

K015

Still bottoms from the distillation of benzyl chloride.

Anthracene Benzal chloride

120-12-7 98-87-3

0.059 0.055

3.4 6.0

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Phenanthrene

85-01-8

0.059

5.6

Toluene

108-88-3

0.080

10

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

K016

Heavy ends or distillation residues from the production of carbon tetrachloride.

Hexachlorobenzene Hexachlorobutadiene

118-74-1 87-68-3

0.055 0.055

10 5.6

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

Hexachloroethane

67-72-1

0.055

30

Tetrachloroethylene

127-18-4

0.056

6.0

K017

Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.

bis(2-Chloroethyl)ether 1,2-Dichloropropane 1,2,3-Trichloropropane

111-44-4 78-87-5 96-18-4

0.033 0.85 0.85

6.0 18 30

K018

Heavy ends from the fractionation column in ethyl chloride production.

Chloroethane Chloromethane 1,1-Dichloroethane

75-00-3 74-87-3 75-34-3

0.27 0.19 0.059

6.0 NA 6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

Hexachlorobenzene

118-74-1

0.055

10

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachloroethane

67-72-1

0.055

30

Pentachloroethane

76-01-7

NA

6.0

1,1,1-Trichloroethane

71-55-6

0.054

6.0

K019

Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production.

bis(2-Chloroethyl)ether Chlorobenzene

111-44-4 108-90-7

0.033 0.057

6.0 6.0

Chloroform

67-66-3

0.046

6.0

p-Dichlorobenzene

106-46-7

0.090

NA

1,2-Dichloroethane

107-06-2

0.21

6.0

Fluorene

86-73-7

0.059

NA

Hexachloroethane

67-72-1

0.055

30

Nephthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

NA

Tetrachloroethylene

127-18-4

0.056

6.0

1,2,4-Trichlorobenzene

120-82-1

0.055

19

1,1,1-Trichloroethane

71-55-6

0.054

6.0

K020

Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.

1,2-Dichloroethane 1,1,2,2-Tetrachloroethane Tetrachloroethylene

107-06-2 79-34-6 127-18-4

0.21 0.057 0.056

6.0 6.0 6.0

K021

Aqueous spent antimony catalyst waste from fluoromethanes production.

Carbon tetrachloride Chloroform Antimony

56-23-5 67-66-3 7440-36-0

0.057 0.046 1.9

6.0 6.0 1.15 mg/L TCLP

K022

Distillation bottoms tars from the production of phenol/acetone from cumene.

Toluene Acetophenone

108-88-3 96-86-2

0.080 0.010

10 9.7

Diphenylamine (difficult to distinguish from diphenylnitrosamine)

122-39-4

0.92

13

Diphenylnitrosamine (difficult to distinguish from diphenylamine)

86-30-6

0.92

13

Phenol

108-95-2

0.039

6.2

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

K023

Distillation light ends from the production of phthalic anhydride from naphthalene.

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0

0.055

28

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

85-44-9

0.055

28

K024

Distillation bottoms from the production of phthalic anhydride from naphthalene.

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0

0.055

28

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

85-44-9

0.055

28

K025

Distillation bottoms from the production of nitrobenzene by the nitration of benzene.

NA

NA

LLEXT fb SSTRP fb CARBN; or CMBST

CMBST

K026

Stripping still tails from the production of methyl ethyl pyridines.

NA

NA

CMBST

CMBST

K027

Centrifuge and distillation residues from toluene diisocyanate production.

NA

NA

CARBN; or CMBST

CMBST

K028

Spent catalyst from the hydrochlorinator reactor in the production of 1,1,1-trichloroethane.

1,1-Dichloroethane trans-1,2-Dichloroethylene

75-34-3 156-60-5

0.059 0.054

6.0 30

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachloroethane

67-72-1

0.055

30

Pentachloroethane

76-01-7

NA

6.0

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

1,1,1-Trichloroethane

71-55-6

0.054

6.0

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Cadmium

7440-43-9

0.69

NA

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

K029

Waste from the product steam stripper in the production of 1,1,1-trichloroethane.

Chloroform 1,2-Dichloroethane

67-66-3 107-06-2

0.046 0.21

6.0 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 p-Dichlorobenzene

95-50-1 106-46-7

0.088 0.090

NA NA

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachloroethane

67-72-1

0.055

30

Hexachloropropylene

1888-71-7

NA

30

Pentachlorobenzene

608-93-5

NA

10

Pentachloroethane

76-01-7

NA

6.0

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

Tetrachloroethylene

127-18-4

0.056

6.0

1,2,4-Trichlorobenzene

120-82-1

0.055

19

K031

By-product salts generated in the production of MSMA and cacodylic acid.

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

K032

Wastewater treatment sludge from the production of chlordane.

Hexachlorocyclopentadiene Chlordane (alpha and gamma isomers)

77-47-4 57-74-9

.057 0.0033

2.4 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 clorination of cyclopentadiene in the production of chlordane.

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

K034

Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

K035

Wastewater treatment sludges generated in the production of cresote.

Acenaphthene Anthracene

83-32-9 120-12-7

NA NA

3.4 3.4

Benz(a)anthracene

56-55-3

0.059

3.4

Bemzo(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

85-01-1

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 Toluene

298-04-4 108-88-3

0.017 0.080

6.2 10

K038

Wastewater from the washing and stripping of phorate production.

Phorate

298-02-2

0.021

4.6

K039

Filter cake from the filtration of diethylphorphorodithioic 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 p-Dichlorobenzene Pentachlorobenzene

95-50-1 106-46-7 608-93-5

0.088 0.090 0.055

6.0 6.0 10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

1,2,4-Trichlorobenzene

120-82-1

0.055

19

K043

2,6-Dichlorophenol waste from the production of 2,4-D.

2,4-Dichlorophenol

120-83-2

0.044

14

2,6-Dichlorophenol

187-65-0

0.044

14

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

2,3,4,6-Tetrachlorophenol

58-90-2

0.030

7.4

Pentachlorophenol

87-86-5

0.089

7.4

Tetrachloroethylene

127-18-4

0.056

6.0

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

PeCDDs (All 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 Benzo(a)pyrene

71-43-2 50-32-8

0.14 0.061

10 3.4

bis(2-Ethylhexyl)phthalate

117-81-7

0.28

28

Chrysene

218-01-9

0.059

3.4

Di-n-butyl phthalate

84-74-2

0.057

28

Ethylbenzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

NA

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-33

0.080

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Chanides (Total) 7

57-12-5

1.2

590

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K049

Slop oil emulsion solids from the petroleum refining industry.

Anthracene Benzene

120-12-7 71-43-2

0.059 0.14

3.4 10

Benzo(a)pyrene

50-32-8

0.061

3.4

bis(2-Ethylhexyl)phthalate

117-81-7

0.28

28

Carbon disulfide

75-15-0

3.8

NA

Chrysene

218-01-9

0.059

3.4

2,4-Dimethylphenol

105-67-9

0.036

NA

Ethylbenzene

100-41-4

0.057

10

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.080

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Cyanides (Total) 7

57-12-5

1.2

590

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K050

Heat exchanger bundle cleaning sludge from the petroleum refining industry.

Benzo(a)pyrene Phenol

50-32-8 108-95-2

0.061 0.039

3.4 6.2

Cyanides (Total) 7

57-12-5

1.2

590

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K051

API separator sludge from the petroleum refining industry.

Acenaphthene Anthracene

83-32-9 120-12-7

0.059 0.059

NA 3.4

Benz(a)anthracene

56-55-3

0.059

3.4

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

bis(2-Ethylhexyl)phthalate

117-81-7

0.28

28

Chrysene

218-01-9

0.059

3.4

Di-n-butyl phthalate

105-67-9

0.057

28

Ethylbenzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

NA

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Cyanides (Total) 7

57-12-5

1.2

590

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K052

Tank bottoms (leaded) from the petroleum refining industry.

Benzene Benzo(a)pyrene

71-43-2 50-32-8

0.14 0.061

10 3.4

o-Cresol

95-48-7

0.11

5.6

m-Cresol (difficult to distinguish from p-cresol)

108-39-4

0.77

5.6

p-Cresol (difficult to distinguish from m-cresol)

106-44-5

0.77

5.6

2,4-Dimethylphenol

105-67-9

0.036

NA

Ethylbenzene

100-41-4

0.057

10

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total) 7

57-12-5

1.2

590

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K060

Ammonia still lime sludge from coking operations.

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

Naphthalene

91-20-3

0.059

5.6

Phenol

108-95-2

0.039

6.2

Cyanides (Total) 7

57-12-5

1.2

590

K061

Emission control dust/sludge from the primary production of steel in electric furnaces.

Antimony Arsenic

7440-36-0 7440-38-2

NA NA

1.15 mg/L TCLP 5.0 mg/L TCLP

Barium

7440-39-3

NA

21 mg/L TCLP

Beryllium

7440-41-7

NA

1.22 mg/L TCLP

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Mercury

7439-97-6

NA

0.025 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Selenium

7782-49-2

NA

5.7 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

Thallium

7440-28-0

NA

0.20 mg/L TCLP

Zinc

7440-66-6

NA

4.3 mg/L TCLP

K062

Spent pickle liquor generated by steel finishing operations of facilities within the iron and steel industry (SIC Codes 331 and 332).

Chromium (Total) Lead Nickel

7440-47-3 7439-92-1 7440-02-0

2.77 0.69 3.98

0.60 mg/L TCLP 0.75 mg/L TCLP NA

K069

Emission control dust/sludge from secondary lead smelting—Calcium Sulfate (Low Lead) Subcategory

Cadmium Lead

7440-43-9 7439-92-1

0.69 0.69

0.11 mg/L TCLP 0.75 mg/L TCLP

Emission control dust/sludge from secondary lead smelting—Non-Calcium Sulfate (High Lead) Subcategory

NA

NA

NA

RLEAD

K071

K071 (Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used) nonwastewaters that are residues from RMERC.

Mercury

7439-97-6

NA

0.20 mg/L TCLP

K071 (Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used.) nonwastewaters that are not residues from RMERC.

Mercury

7439-97-6

NA

0.025 mg/L TCLP

All K071 wastewaters.

Mercury

7439-97-6

0.15

NA

K073

Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production.

Carbon tetrachloride Chloroform Hexachloroethane

56-23-5 67-66-3 67-72-1

0.057 0.046 0.055

6.0 6.0 30

Tetrachloroethylene

127-18-4

0.056

6.0

1,1,1-Trichloroethane

71-55-6

0.054

6.0

K083

Distillation bottoms from aniline production.

Aniline

62-53-3

0.81

14

Benzene

71-43-2

0.14

10

Cyclohexanone

108-94-1

0.36

NA

Diphenylamine (difficult to distinguish from diphenylnitrosamine

122-39-4

0.92

13

Diphenylnitrosamine (difficult to distinguish from diphenylamine)

86-30-6

0.92

13

Nitrobenzene

98-95-3

0.068

14

Phenol

108-95-2

0.039

6.2

Nickel

7440-02-0

3.98

11 mg/L TCLP

K084

Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

K085

Distillation or fractionation column bottoms from the production of chlorobenzenes.

Benzene Chlorobenzene m-Dichlorobenzene

71-43-2 108-90-7 541-73-1

0.14 0.057 0.036

10 6.0 6.0

o-Dichlorobenzene

95-50-1

0.088

6.0

p-Dichlorobenzene

106-46-7

0.090

6.0

Hexachlorobenzene

118-74-1

0.055

10

Total PCBs (sum of all PCB isomers, or all Aroclors)

1336-36-3

0.10

10

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

1,2,4-Trichlorobenzene

120-82-1

0.055

19

K086

Solvent wastes and sludges, caustic washes and sludges, or water washes and sludges from cleaning tubs and equipment used in the formulation of ink from pigments, driers, soaps, and stabilizers containing chromium and lead.

Acetone Acetophenone bis(2-Ethylhexyl) phthalate n-Butyl alcohol

67-64-1 96-86-2 117-81-7 71-36-3

0.28 0.010 0.28 5.6

160 9.7 28 2.6

Butylbenzyl phthalate

85-68-7

0.017

28

Cyclohexanone

108-94-1

0.36

NA

o-Dichlorobenzene

95-50-1

0.088

6.0

Diethyl phthalate

84-66-2

0.20

28

Dimethyl phthalate

131-11-3

0.047

28

Di-n-butyl phthalate

84-74-2

0.057

28

Di-n-octyl phthalate

117-84-0

0.017

28

Ethyl acetate

141-78-6

0.34

33

Ethylbenzene

100-41-4

0.057

10

Methanol

67-56-1

5.6

NA

Methyl ethyl ketone

78-93-3

0.28

36

Methyl isobutyl ketone

108-10-1

0.14

33

Methylene chloride

75-09-2

0.089

30

Naphthalene

91-20-3

0.059

5.6

Nitrobenzene

98-95-3

0.068

14

Toluene

108-88-3

0.080

10

1,1,1-Trichloroethane

71-55-6

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total) 7

57-12-5

1.2

590

Lead

7439-92-1

0.69

0.75 mg/L TCLP

K087

Decanter tank tar sludge from coking operations.

Acenaphthylene

208-96-8

0.059

3.4

Benzene

71-43-2

0.14

10

Chrysene

218-01-9

0.059

3.4

Fluoranthene

206-44-0

0.068

3.4

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Toluene

108-88-3

0.080

10

Xylenes-mixed isomers (sum of o, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

K088

Spent potliners from primary aluminum reduction.

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 mg/L TCLP

Beryllium

7440-41-7

0.82

1.22 mg/L TCLP

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Mercury

7439-97-6

0.15

0.025 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

Silver

7440-22-4

0.43

0.14 mg/L TCLP

Cyanide (Total) 7

57-12-5

1.2

590

Cyanide (Amenable) 7

57-12-5

0.86

30

Fluoride

16984-48-8

35

NA

K093

Distillation light ends from the production of phthalic anhydride from ortho-xylene

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0

0.055

28

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

85-44-9

0.055

28

K094

Distillation bottoms from the production of phthalic anhydride from ortho-xylene.

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0

0.055

28

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

85-44-9

0.055

28

K095

Distillation bottoms from the production of 1,1,1-trichloroethane.

Hexachloroethane Pentachloroethane

67-72-1 76-01-7

0.055 0.055

30 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

79-01-1

0.054

6.0

K096

Heavy ends from the heavy ends column from the production of 1,1,1-trichloroethane.

m-Dichlorobenzene Pentachloroethane

541-73-1 76-01-1

0.036 0.055

6.0 6.0

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

1,2,4-Trichlorobenzene

120-82-1

0.055

19

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

K097

Vacuum stripper discharge from the chlordane clorinator in the production of chlordane.

Chlordane (alpha and gamma isomers) Heptachlor

57-74-9 76-44-8

0.0033 0.0012

0.26 0.066

Heptachlor epoxide

1024-57-3

0.016

0.066

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

K098

Untreated process wastewater from the production of toxaphene.

Toxaphene

8001-35-2

0.0095

2.6

K099

Untreated wastewater from the production of 2,4-D.

2,4-Dichlorophenoxyacetic acid

94-75-7

0.72

10

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

K100

Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting.

Cadmium Chromium (Total) Lead

7440-43-9 7440-47-3 7439-92-1

0.69 2.77 0.69

0.11 mg/L TCLP 0.60 mg/L TCLP 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 Arsenic Cadmium

88-74-4 7440-38-2 7440-43-9

0.27 1.4 0.69

14 5.0 mg/L TCLP NA

Lead

7439-92-1

0.69

NA

Mercury

7439-97-6

0.15

NA

K102

Residue from the use of activated carbon for decolorization in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.

o-Nitrophenol Arsenic Cadmium

88-75-5 7440-38-2 7440-43-9

0.028 1.4 0.69

13 5.0 mg/L TCLP 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 Benzene

62-53-3 71-43-2

0.81 0.14

14 10

2,4-Dinitrophenol

51-28-5

0.12

160

Nitrobenzene

98-95-3

0.068

14

Phenol

108-95-2

0.039

6.2

K104

Combined wastewater streams generated from nitrobenzene/aniline production.

Aniline Benzene

62-53-3 71-43-2

0.81 0.14

14 10

2,4-Dinitrophenol

51-28-5

0.12

160

Nitrobenzene

98-95-3

0.068

14

Phenol

108-95-2

0.039

6.2

Cyanides (Total) 7

57-12-5

1.2

590

K105

Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes.

Benzene Chlorobenzene

71-43-2 108-90-7

0.14 0.057

10 6.0

2-Chlorophenol

95-57-8

0.044

5.7

o-Dichlorobenzene

95-50-1

0.088

6.0

p-Dichlorobenzene

106-46-7

0.090

6.0

Phenol

108-95-2

0.039

6.2

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

K106

K106 (wastewater treatment sludge from the mercury cell process in chlorine production) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.

Mercury

7439-97-6

NA

RMERC

K106 (wastewater treatment sludge from the mercury cell process in chlorine production) nonwastewaters that contain less than 260 mg/kg total mercury that are residues from RMERC.

Mercury

7439-97-6

NA

0.20 mg/L TCLP

Other K106 nonwastewaters that contain less than 260 mg/kg total mercury and are not residues from RMERC.

Mercury

7439-97-6

NA

0.025 mg/L TCLP

All K106 wastewaters.

Mercury

7439-97-6

0.15

NA

K107

Column bottoms from production separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

NA

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K108

Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

NA

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K109

Spent filter cartridges from product purification from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

NA

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K110

Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

NA

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K111

Product washwaters from the production of dinitrotoluene via nitration of toluene.

2,4-Dinitrotoluene 2,6-Dinitrotoluene

121-14-2 606-20-2

0.32 0.55

140 28

K112

Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene.

NA

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K113

Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

NA

NA

CARBN; or CMBST

CMBST

K114

Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

NA

NA

CARBN; or CMBST

CMBST

K115

Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

Nickel NA

7440-02-2 NA

3.98 CARBN; or CMBST

11 mg/L TCLP 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) Chloroform

74-83-9 67-66-3

0.11 0.046

15 6.0

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

K118

Spent absorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.

Methyl bromide (Bromomethane) Chloroform

74-83-9 67-66-3

0.11 0.046

15 6.0

Ethylene dibromide (1,2,-Dibromoethane)

106-93-4

0.028

15

K123

Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salts.

NA

NA

CMBST; or CHOXD fb (BIODG or CARBN)

CMBST

K124

Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.

NA

NA

CMBST; or CHOXD fb (BIODG or CARBN)

CMBST

K125

Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts.

NA

NA

CMBST; or CHOXD fb (BIODG or CARBN)

CMBST

K126

Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts.

NA

NA

CMBST; or CHOXD fb (BIODG or CARBN)

CMBST

K131

Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide.

Methyl bromide (Bromomethane)

74-83-9

0.11

15

K132

Spent absorbent and wastewater separator solids from the production of methyl bromide.

Methyl bromide (Bromomethane)

74-83-9

0.11

15

K136

Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.

Methyl bromide (Bromomethane) Chloroform

74-83-9 67-66-3

0.11 0.46

15 6.0

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

K141

Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the production of coke or the recovery of coke by-products produced from coal. This listing does not include K087 (decanter tank tar sludge from coking operations).

Benzene Benz(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

71-43-2 56-55-3 50-2-8 205-99-2

0.14 0.059 0.061 0.11

10 3.4 3.4 6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

K142

Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal.

Benzene Benz(a)anthracene

71-43-2 56-55-3

0.14 0.059

10 3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

K143

Process residues from the recovery of light oil, including, but not limited to, those generated in stills, decanters, and wash oil recovery units from the recovery of coke by-products produced from coal.

Benzene Benz(a)anthracene Benzo(a)pyrene

71-43-2 56-55-3 50-32-8

0.14 0.059 0.061

10 3.4 3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)flouranthene (difficult to distinguish from benzo(b)fluoranthene

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

K144

Wastewater sump residues from light oil refining, including, but not limited to, intercepting or contamination sump sludges from the recovery of coke by-products produced from coal.

Benzene Benz(a)pyrene Benzo(a)anthracene

71-43-2 56-55-3 50-32-8

0.14 0.059 0.061

10 3.4 3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

K145

Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal.

Benzene Benz(a)anthracene

71-43-2 56-55-3

0.14 0.059

10 3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Naphthalene

91-20-3

0.059

5.6

K147

Tar storage tank residues from coal tar refining.

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

K148

Residues from coal tar distillation, including, but not limited to, still bottoms.

Benz(a)anthracene Benzo(a)pyrene

56-55-3 50-32-8

0.059 0.061

3.4 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 Chloroform Chloromethane p-Dichlorobenzene Hexachlorobenzene

108-90-7 67-66-3 74-87-3 106-46-7 118-74-1

0.057 0.046 0.19 0.090 0.055

6.0 6.0 30 6.0 10

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

Toluene

108-88-3

0.080

10

K150

Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydrochloric acid recovery processes associated with the production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.

Carbon tetrachloride Chloroform Chloromethane p-Dichlorobenzene Hexachlorobenzene

56-23-5 67-66-3 74-87-3 106-46-7 118-74-1

0.057 0.046 0.019 0.090 0.055

6.0 6.0 30 6.0 10

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

1,1,2,2-Tetrachloroethane

79-34-5

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

1,2,4-Trichlorobenzene

120-82-1

0.055

19

K151

Wastewater treatment sludges, excluding neutralization and biological sludges, generated during the treatment of wastewaters from the production of alpha- or (methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.

Benzene Carbon tetrachloride Chloroform Hexachlorobenzene Pentachlorobenzene

71-43-2 56-23-5 67-66-3 118-74-1 608-93-5

0.14 0.057 0.046 0.055 0.055

10 6.0 6.0 10 10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

Tetrachloroethylene

127-18-4

0.056

6.0

Toluene

108-88-3

0.080

10

K156

Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes

Acetonitrile

75-05-8

5.6

1.8

Acetophenone

98-86-2

0.010

9.7

Aniline

62-53-3

0.81

14

Benomyl 10

17804-35-2

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

Benzene

71-43-2

0.14

10

Carbaryl 10

63-25-2

0.006; or CMBST, CHOXD, BIODG or CARBN

0.14; or CMBST

Carbenzadim 10

10605-21-7

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

Carbofuran 10

1563-66-2

0.006; or CMBST, CHOXD, BIODG or CARBN

0.14; or CMBST

Carbosulfan 10

55285-14-8

0.028; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

Chlorobenzene

108-90-7

0.057

6.0

Chloroform

67-66-3

0.046

6.0

o-Dichlorobenzene

95-50-1

0.088

6.0

Methomyl 10

16752-77-5

0.028; or CMBST, CHOXD, BIODG or CARBN

0.14; or CMBST

Methylene chloride

75-09-2

0.089

30

Methyl ethyl ketone

78-93-3

0.28

36

Naphthalene

91-20-3

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyridine

110-86-1

0.014

16

Toluene

108-88-3

0.080

10

Triethylamine

121-44-8

0.081; or CMBST, CHOXD, BIODG or CARBN

1.5; or CMBST

K157

Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Chloromethane

74-87-3

0.19

30

Methomyl 10

16752-77-5

0.028; or CMBST, CHOXD, BIODG or CARBN

0.14; or CMBST

Methylene chloride

75-09-2

0.089

30

Methylethyl ketone

78-93-3

0.28

36

Pyridine

110-86-1

0.014

16

Triethylamine

121-44-8

0.081 or CMBST, CHOXD, BIODG or CARBN

1.5; or CMBST

K158

Bag house dusts and filter/separation solids from the production of carbamates and carbamoyl oximes

Benzene

71-43-2

0.14

10

Carbenzadim 10

10605-21-7

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

Carbofuran 10

1563-66-2

0.006; or CMBST, CHOXD, BIODG or CARBN

0.14; or CMBST

Carbosulfan 10

55285-14-8

0.028; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

Chloroform

67-66-3

0.046

6.0

Methylene chloride

75-09-2

0.089

30

Phenol

108-95-2

0.039

6.2

K159

Organics from the treatment of thiocarbamate wastes

Benzene

71-43-2

0.14

10

Butylate 10

2008-41-5

0.042; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

EPTC (Eptam) 10

759-94-4

0.042; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

Molinate 10

2212-67-1

0.042; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

Pebulate 10

1114-71-2

0.042; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

Vernolate 10

1929-77-7

0.042; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

K161

Purification solids (including filtration, evaporation, and centrifugation solids), baghouse dust and floor sweepings from the production of dithiocarbamate acids and their salts

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Carbon disulfide

75-15-0

3.8

4.8 mg/L TCLP

Dithiocarbamates (total) 10

NA

0.028; or CMBST, CHOXD, BIODG or CARBN

28; or CMBST

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11.0 mg/L TCLP

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

K169

Crude oil tank sediment from petroleum refining operations.

Benz(a)anthracene

56-55-3

0.059

3.4

Benzene

71-43-2

0.14

10

Benzo(g,h,i)perylene

191-24-2

0.0055

1.8

Chrysene

218-01-9

0.059

3.4

Ethyl benzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

3.4

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

0.080

10

Xylene(s) (Total)

1330-20-7

0.32

30

K170

Clarified slurry oil sediment from petroleum refining operations.

Benz(a)anthracene Benzene

56-55-3 71-43-2

0.059 0.14

3.4 10

Benzo(g,h,i)perylene

191-24-2

0.0055

1.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Ethyl benzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

3.4

Indeno(1,3,4-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

0.080

10

Xylene(s) (Total)

1330-20-7

0.32

30

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 Benzene Chrysene Ethyl benzene

56-55-3 71-43-2 218-01-9 100-41-4

0.059 0.14 0.059 0.057

3.4 10 3.4 10

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

81-05-8

0.059

5.6

Pyrene

129-00-0

0.67

8.2

Toluene (Methyl Benzene)

108-88-3

0.080

10

Xylene(s) (Total)

1330-20-7

0.32

30

Arsenic

7740-38-2

1.4

5 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 Ethyl benzene Toluene (Methyl Benzene) Xylene(s) (Total)

71-43-2 100-41-4 108-88-3 1330-20-7

0.14 0.57 0.080 0.32

10 10 10 30

Antimony

7740-36-0

1.9

1.15 mg/L TCLP

Arsenic

7740-38-2

1.4

5 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-HpCDD)

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

0.005 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 tetachlorodibenzo- 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

Mercury 12 pH 12

7438-97-6

NA NA

0.025 mg/L TCLP pH≤6.0

All K175 wastewaters

Mercury

7438-97-6

0.15

NA

K176

Baghouse filters from the production of antimony oxide, including filters from the production of intermediates (e.g., antimony metal or crude antimony oxide)

Antimony Arsenic Cadmium Lead Mercury

7440-36-0 7440-38-2 7440-43-9 7439-92-1 7439-97-6

1.9 1.4 0.69 0.69 0.15

1.15 mg/L TCLP 5.0 mg/L TCLP 0.11 mg/L TCLP 0.75 mg/L TCLP 0.025 mg/L TCLP

K177

Slag from the production of antimony oxide that is speculatively accumulated or disposed, including slag from the production of intermediates (e.g., antimony metal or crude antimony oxide)

Antimony Arsenic Lead

7440-36-0 7440-38-2 7439-92-1

1.9 1.4 0.69

1.15 mg/L TCLP 5.0 mg/L TCLP 0.75 mg/L TCLP

K178

Residues from manufacturing and manufacturing-site storage of ferric chloride from acids formed during the production of titanium dioxide using the chloride-ilmenite process.

1,2,3,4,6,7,8- Heptachlorodibenzo- p -dioxin (1,2,3,4,6,7,8-HpCDD) 1,2,3,4,6,7,8- Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF) 1,2,3,4,7,8,9- Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF)

35822-39-4 67562-39-4 55673-89-7

0.000035 or CMBST 11 0.000035 or CMBST 11 0.000035 or CMBST 11

0.0025 or CMBST 11 0.0025 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 Hexachlorodibenzo-furans)

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 Pentachlorodibenzo-furans)

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 tetrachlorodibenzo-furans)

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 commingled at the point of generation with nonwastewaters from other processes) that, at the point of generation, contain mass loadings of any of the constituents identified in paragraph (c) of section 261.32 that are equal to or greater than the corresponding paragraph (c) levels, as determined on a calendar year basis

Aniline o-Anisidine (2-methoxyaniline) 4-Chloroaniline p-Cresidine 2,4-Dimethylaniline (2,4-xylidine) 1,2-Phenylenediamine

62-53-3 90-04-0 106-47-8 120-71-8 95-68-1 95-54-5

0.81 0.010 0.46 0.010 0.010 CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN

14 0.66 16 0.66 0.66 CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN

1,3-Phenylenediamine

108-45-2

0.010

0.66

P001

Warfarin, & salts, when present at concentrations greater than 0.3%

Warfarin

81-81-2

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P002

1-Acetyl-2-thiourea

1-Acetyl-2-thiourea

591-08-2

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P003

Acrolein

Acrolein

107-02-8

0.29

CMBST

P004

Aldrin

Aldrin

309-00-2

0.021

0.066

P005

Allyl alcohol

Allyl alcohol

107-18-6

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P006

Aluminum phosphide

Aluminum phosphide

20859-73-8

CHOXD; CHRED; or CMBST

CHOXD; CHRED; or CMBST

P007

5-Aminomethyl 3-isoxazolol

5-Aminomethyl 3-isoxazolol

2763-96-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P008

4-Aminopyridine

4-Aminopyridine

504-24-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P009

Ammonium picrate

Ammonium picrate

131-74-8

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P010

Arsenic acid

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

P011

Arsenic pentoxide

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

P012

Arsenic trioxide

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

P013

Barium cyanide

Barium

7440-39-3

NA

21 mg/L TCLP

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

P014

Thiophenol (Benzene thiol)

Thiophenol (Benzene thiol)

108-98-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P015

Beryllium 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

Cyanides (Amenable) 7

57-12-5

0.86

30

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

P026

1-(o-Chlorophenyl)thiourea

1-(o-Chlorophenyl)thiourea

5344-82-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P027

3-Chloropropionitrile

3-Chloropropionitrile

542-76-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P028

Benzyl chloride

Benzyl chloride

100-44-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P029

Copper cyanide

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

P030

Cyanides (soluble salts and complexes)

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

P031

Cyanogen

Cyanogen

460-19-5

CHOXD; WETOX; or CMBST

CHOXD; WETOX; or CMBST

P033

Cyanogen chloride

Cyanogen chloride

506-77-4

CHOXD; WETOX; or CMBST

CHOXD; WETOX; or CMBST

P034

2-Cyclohexyl-4,6-dinitrophenol

2-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)

Diisopropylfluorophosphate (DFP)

55-91-4

CARBN; or CMBST

CMBST

P044

Dimethoate

Dimethoate

60-51-5

CARBN; or CMBST

CMBST

P045

Thiofanox

Thiofanox

39196-18-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P046

alpha, alpha-Dimethylphenethylamine

alpha, alpha-Dimethylphenethylamine

122-09-8

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P047

4,6-Dinitro-o-cresol

4,6-Dinitro-o-cresol

543-52-1

0.28

160

4,6-Dinitro-o-cresol salts

NA

NA

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P048

2,4-Dinitrophenol

2,4-Dinitrophenol

51-28-5

0.12

160

P049

Dithiobiuret

Dithiobiuret

541-53-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P050

Endosulfan

Endosulfan I

939-98-8

0.023

0.066

Endosulfan II

33213-6-5

0.029

0.13

Endosulfan sulfate

1031-07-8

0.029

0.13

P051

Endrin

Endrin

72-20-8

0.0028

0.13

Endrin aldehyde

7421-93-4

0.025

0.13

P054

Aziridine

Aziridine

151-56-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P056

Fluorine

Fluoride (measured in wastewaters only)

16984-48-8

35

ADGAS fb NEUTR

P057

Fluoroacetamide

Fluoroacetamide

640-19-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P058

Fluoroacetic acid, sodium salt

Fluoroacetic acid, sodium salt

62-74-8

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P059

Heptachlor

Heptachlor

76-44-8

0.0012

0.066

Heptachlor epoxide

1024-57-3

0.016

0.066

P060

Isodrin

Isodrin

465-73-6

0.021

0.066

P062

Hexaethyl tetraphosphate

Hexaethyl tetraphosphate

757-58-4

CARBN; or CMBST

CMBST

P063

Hydrogen cyanide

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

P064

Isocyanic acid, ethyl ester

Isocyanic acid, ethyl ester

624-83-9

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P065

Mercury fulminate nonwastewaters, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC.

Mercury

7439-97-6

NA

IMERC

Mercury fulminate nonwastewaters that are either incinerator residues or are residues from RMERC; and contain greater than or equal to 260 mg/kg total mercury.

Mercury

7439-97-6

NA

RMERC

Mercury fulminate nonwastewaters that are residues from RMERC and contain less than 260 mg/kg total mercury.

Mercury

7439-97-6

NA

0.20 mg/L TCLP

Mercury fulminate nonwastewaters that are incinerator residues and contain less than 260 mg/kg total mercury.

Mercury

7439-97-6

NA

0.025 mg/L TCLP

All mercury fulminate wastewaters.

Mercury

7439-97-6

0.15

NA

P066

Methomyl

Methomyl

16752-77-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P067

2-Methyl-aziridine

2-Methyl-aziridine

75-55-8

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P068

Methyl hydrazine

Methyl hydrazine

60-34-4

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P069

2-Methyllactonitrile

2-Methyllactonitrile

75-86-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P070

Aldicarb

Aldicarb

116-06-3

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P071

Methyl parathion

Methyl parathion

298-00-0

0.014

4.6

P072

1-Naphthyl-2-thiourea

1-Naphthyl-2-thiourea

86-88-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P073

Nickel carbonyl

Nickel

7440-02-0

3.98

11 mg/L TCLP

P074

Nickel cyanide

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

Nickel

7440-02-0

3.98

11 mg/L TCLP

P075

Nicotine and salts

Nicotine and salts

54-11-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P076

Nitric oxide

Nitric oxide

10102-43-9

ADGAS

ADGAS

P077

p-Nitroaniline

p-Nitroaniline

100-01-6

0.028

28

P078

Nitrogen dioxide

Nitrogen dioxide

10102-44-0

ADGAS

ADGAS

P081

Nitroglycerin

Nitroglycerin

55-63-0

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P082

N-Nitrosodimethylamine

N-Nitrosodimethylamine

62-75-9

0.40

2.3

P084

N-Nitrosomethylvinylamine

N-Nitrosomethylvinylamine

4549-40-0

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P085

Octamethylpyrophosphoramide

Octamethylpyrophosphoramide

152-16-9

CARBN; or CMBST

CMBST

P087

Osmium tetroxide

Osmium tetroxide

20816-12-0

RMETL; or RTHRM

RMETL; or RTHRM

P088

Endothall

Endothall

145-73-3

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P089

Parathion

Parathion

56-38-2

0.014

4.6

P092

Phenyl mercuric acetate nonwastewaters, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC.

Mercury

7439-97-6

NA

IMERC; or RMERC

Phenyl mercuric acetate nonwastewaters that are either incinerator residues or are residues from RMERC; and still contain greater than or equal to 260 mg/kg total mercury.

Mercury

7439-97-6

NA

RMERC

Phenyl mercuric acetate nonwastewaters that are residues from RMERC and contain less than 260 mg/kg total mercury.

Mercury

7439-97-6

NA

0.20 mg/L TCLP

Phenyl mercuric acetate nonwastewaters that are incinerator residues and contain less than 260 mg/kg total mercury.

Mercury

7439-97-6

NA

0.025 mg/L TCLP

All phenyl mercuric acetate wastewaters.

Mercury

7439-97-6

0.15

NA

P093

Phenylthiourea

Phenylthiourea

103-85-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P094

Phorate

Phorate

298-02-2

0.021

4.6

P095

Phosgene

Phosgene

75-44-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P096

Phosphine

Phosphine

7803-51-2

CHOXD; CHRED; or CMBST

CHOXD; CHRED; or CMBST

P097

Famphur

Famphur

52-85-7

0.017

15

P098

Potassium cyanide.

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

P099

Potassium silver cyanide

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

Silver

7440-22-4

0.43

0.14 mg/L TCLP

P101

Ethyl cyanide (Propanenitrile)

Ethyl cyanide (Propanenitrile)

107-12-0

0.24

360

P102

Propargyl alcohol

Propargyl alcohol

107-19-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P103

Selenourea

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

P104

Silver cyanide

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

Silver

7440-22-4

0.43

0.14 mg/L TCLP

P105

Sodium azide

Sodium azide

26628-22-8

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P106

Sodium cyanide

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

P108

Strychnine and salts

Strychnine and salts

57-24-9

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P109

Tetraethyldithiopyrophosphate

Tetraethyldithiopyrophosphate

3689-24-5

CARBN; or CMBST

CMBST

P110

Tetraethyl lead

Lead

7439-92-1

0.69

0.75 mg/L TCLP

P111

Tetraethylpyrophosphate

Tetraethylpyrophosphate

107-49-3

CARBN; or CMBST

CMBST

P112

Tetranitromethane

Tetranitromethane

509-14-8

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P113

Thallic oxide

Thallium (measured in wastewaters only)

7440-28-0

1.4

RTHRM; or STABL

P114

Thallium selenite

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

P115

Thallium (I) sulfate

Thallium (measured in wastewaters only)

7440-28-0

1.4

RTHRM; or STABL

P116

Thiosemicarbazide

Thiosemicarbazide

79-19-6

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P118

Trichloromethanethiol

Trichloromethanethiol

75-70-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

P119

Ammonium vanadate

Vanadium (measured in wastewaters only)

7440-62-2

4.3

STABL

P120

Vanadium pentoxide

Vanadium (measured in wastewaters only)

7440-62-2

4.3

STABL

P121

Zinc cyanide

Cyanides (Total) 7

57-12-5

1.2

590

Cyanides (Amenable) 7

57-12-5

0.86

30

P122

Zinc phosphide Zn 3 P 2 , when present at concentrations greater than 10%.

Zinc Phosphide

1314-84-7

CHOXD; CHRED; or CMBST

CHOXD; CHRED; or CMBST

P123

Toxaphene

Toxaphene

8001-35-2

0.0095

2.6

P127

Carbofuran 10

Carbofuran

1563-66-2

0.006; or CMBST, CHOXD, BIODG or CARBN

0.14; or CMBST

P128

Mexacarbate 10

Mexacarbate

315-18-4

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

P185

Tirpate 10

Tirpate

26419-73-8

0.056; or CMBST, CHOXD, BIODG or CARBN

0.28; or CMBST

P188

Physostigmine salicylate 10

Physostigmine salicylate

57-64-7

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

P189

Carbosulfan 10

Carbosulfan

55285-14-8

0.028; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

P190

Metolcarb 10

Metolcarb

1129-41-5

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

P191

Dimetilan 10

Dimetilan

644-64-4

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

P192

Isolan 10

Isolan

119-38-0

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

P194

Oxamyl 10

Oxamyl

23135-22-0

0.056; or CMBST, CHOXD, BIODG or CARBN

0.28; or CMBST

P196

Manganese dimethyldithio-carbamate 10

Dithiocarbamates (total)

NA

0.028; or CMBST, CHOXD, BIODG or CARBN

28; or CMBST

P197

Formparanate 10

Formparante

17702-57-7

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

P198

Formetanate hydrochloride 10

Formetanate hydrochloride

23422-53-9

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

P199

Methiocarb 10

Methiocarb

2032-65-7

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

P201

Promecarb 10

Promecarb

2631-37-0

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

P202

m-Cumenyl methylcarbamate 10

m-Cumenyl methylcarbamate

64-00-6

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

P203

Aldicarb sulfone 10

Aldicarb sulfone

1646-88-4

0.056; or CMBST, CHOXD, BIODG or CARBN

0.28; or CMBST

P204

Physostigmine 10

Physostigmine

57-47-6

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

P205

Ziram 10

Dithiocarbamates (total)

NA

0.028; or CMBST, CHOXD, BIODG or CARBN

28; or CMBST

U001

Acetaldehyde

Acetaldehyde

75-07-0

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U002

Acetone

Acetone

67-64-1

0.28

160

U003

Acetonitrile

Acetonitrile

75-05-8

5.6

CMBST

Acetonitrile; alternate 6 standard for nonwastewaters only

75-05-8

NA

38

U004

Acetophenone

Acetophenone

98-86-2

0.010

9.7

U005

2-Acetylaminofluorene

2-Acetylaminofluorene

53-96-3

0.059

140

U006

Acetyl chloride

Acetyl Chloride

75-36-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U007

Acrylamide

Acrylamide

79-06-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U008

Acrylic acid

Acrylic acid

79-10-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U009

Acrylonitrile

Acrylonitrile

107-13-1

0.24

84

U010

Mitomycin C

Mitomycin C

50-07-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U011

Amitrole

Amitrole

61-82-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U012

Aniline

Aniline

62-53-3

0.81

14

U014

Auramine

Auramine

492-80-8

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U015

Azaserine

Azaserine

115-02-6

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U016

Benz(c)acridine

Benz(c)acridine

225-51-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U017

Benzal chloride

Benzal chloride

98-87-3

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U018

Benz(a)anthracene

Benz(a)anthracene

56-55-3

0.059

3.4

U019

Benzene

Benzene

71-43-2

0.14

10

U020

Benzenesulfonyl chloride

Benzenesulfonyl chloride

98-09-9

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U021

Benzidine

Benzidine

92-87-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U022

Benzo(a)pyrene

Benzo(a)pyrene

50-32-8

0.061

3.4

U023

Benzotrichloride

Benzotrichloride

98-07-7

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOCS; CHRED; or CMBST

U024

bis(2-Chloroethoxy)methane

bis(2)Chloroethoxy)methane

111-91-1

0.036

7.2

U025

bis(2-Chloroethyl)ether

bis(2-Chloroethyl)ether

111-44-4

0.033

6.0

U026

Chlornaphazine

Chlornaphazine

494-03-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U027

bis(2-Chloroisopropyl)ether

bis(2-Chloroisopropyl)ether

39638-32-9

0.055

7.2

U028

bis(2-Ethylhexyl) phthalate

bis(2-Ethylhexyl) phthalate

117-81-7

0.28

28

U029

Methyl bromide (Bromomethane)

Methyl bromide (Bromomethane)

74-83-9

0.11

15

U030

4-Bromophenyl phenyl ether

4-Bromophenyl phenyl ether

101-55-3

0.055

15

U031

n-Butyl alcohol

n-Butyl alcohol

71-36-3

5.6

2.6

U032

Calcium chromate

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

U033

Carbon oxyfluoride

Carbon oxyfluoride

353-50-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U034

Trichloroacetaldehyde (Chloral)

Trichloroacetaldehyde (Chloral)

75-87-6

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U035

Chlorambucil

Chlorambucil

305-03-3

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U036

Chlordane

Chlordane (alpha and gamma isomers)

57-74-9

0.0033

0.26

U037

Chlorobenzene

Chlorobenzene

108-90-7

0.057

60

U038

Chlorobenzilate

Chlorobenzilate

510-15-6

0.10

CMBST

U039

p-Chloro-m-cresol

p-Chloro-m-cresol

59-50-7

0.018

14

U041

Epichlorohydrin (1-Chloro-2,3-epoxypropane)

Epichlorohydrin (1-Chloro-2,3-epoxypropane)

106-89-8

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U042

2-Chloroethyl vinyl ether

2-Chloroethyl vinyl ether

110-75-8

0.062

CMBST

U043

Vinyl chloride

Vinyl chloride

75-01-4

0.27

6.0

U044

Chloroform

Chloroform

67-66-3

0.046

6.0

U045

Chloromethane (Methyl chloride)

Chloromethane (Methyl chloride)

74-87-3

0.19

30

U046

Chloromethyl methyl ether

Chloromethyl methyl ether

107-30-2

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U047

2-Chloronaphthalene

2-Chloronaphthalene

91-58-7

0.055

5.6

U048

2-Chlorophenol

2-Chlorophenol

95-57-8

0.044

5.7

U049

4-Chloro-o-toluidine hydrochloride

4-Chloro-o-toluidine hydrochloride

3165-93-3

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U050

Chrysene

Chrysene

218-01-9

0.059

3.4

U051

Creosote

Naphthalene

91-20-3

0.059

5.6

Pentachlorophenol

87-86-5

0.089

7.4

Phenanthrene

85-01-8

0.059

5.6

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.080

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

U052

Cresols (Cresylic acid)

o-Cresol

95-48-7

0.11

5.6

m-Cresol (difficult to distinguish from p-cresol)

108-39-4

0.77

5.6

p-Cresol (difficult to distinguish from m-cresol)

106-44-5

0.77

5.6

Cresol-mixed isomers (Cresylic acid) (sum of o- m-, and p-cresol concentrations)

1319-77-3

0.88

11.2

U053

Crotonaldehyde

Crotonaldehyde

4170-30-3

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U055

Cumene

Cumene

98-82-8

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U056

Cyclohexane

Cyclohexane

110-82-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U057

Cyclohexanone

Cyclohexanone

108-94-1

0.36

CMBST

Cyclohexanone; 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

U067

Ethylene dibromide (1,2-Dibromoethane)

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

U068

Dibromomethane

Dibromomethane

74-95-3

0.11

15

U069

Di-n-butyl phthalate

Di-n-butyl phthalate

84-74-2

0.057

28

U070

o-Dichlorobenzene

o-Dichlorobenzene

95-50-1

0.088

6.0

U071

m-Dichlorobenzene

m-Dichlorobenzene

541-73-1

0.036

6.0

U072

p-Dichlorobenzene

p-Dichlorobenzene

106-46-7

0.090

6.0

U073

3,3′-Dichlorobenzidine

3,3′-Dichlorobenzidine

91-94-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U074

1,4-Dichloro-2-butene

cis,1,4-Dichloro-2-butene

1476-11-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

trans-1,4-Dichloro-2-butene

764-41-0

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U075

Dichlorodifluoromethane

Dichlorodifluoromethane

75-71-8

0.23

7.2

U076

1,1-Dichloroethane

1,1-Dichloroethane

75-34-3

0.059

6.0

U077

1,2-Dichloroethane

1,2-Dichloroethane

107-06-2

0.21

6.0

U078

1,1-Dichloroethylene

1,1-Dichloroethylene

75-35-4

0.025

6.0

U079

1,2-Dichloroethylene

trans-1,2-Dichloroethylene

156-60-5

0.054

30

U080

Methylene chloride

Methylene chloride

75-09-2

0.089

30

U081

2,4-Dichlorophenol

2,4-Dichlorophenol

120-83-2

0.044

14

U082

2,6-Dichlorophenol

2,6-Dichlorophenol

87-65-0

0.044

14

U083

1,2-Dichloropropane

1,2-Dichloropropane

78-87-5

0.85

18

U084

1,3-Dichloropropylene

cis-1,3-Dichloropropylene

10061-01-5

0.036

18

trans-1,3-Dichloropropylene

10061-02-6

0.036

18

U085

1,2:3,4-Diepoxybutane

1,2,3,4-Diepoxybutane

1464-53-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U086

N,N′-Diethylhydrazine

N,N′-Diethylhydrazine

1615-80-1

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U087

O,O-Diethyl S-methyldithiophosphate

O,O-Diethyl S-methyldithiophosphate

3288-58-2

CARBN; or CMBST

CMBST

U088

Diethyl phthalate

Diethyl phthalate

84-66-2

0.20

28

U089

Diethyl stilbestrol

Diethyl stilbestrol

56-53-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U090

Dihydrosafrole

Dihydrosafrole

94-58-6

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U091

3,3′-Dimethoxybenzidine

3,3′-Dimethoxybenzidine

119-90-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U092

Dimethylamine

Dimethylamine

124-40-3

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U093

p-Dimethylaminoazobenzene

p-Dimethylaminoazobenzene

60-11-7

0.13

CMBST

U094

7,12-Dimethylbenz(a)anthracene

7,12-Dimethylbenz(a)anthracene

57-97-6

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U095

3,3′-Dimethylbenzidine

3,3′-Dimethylbenzidine

119-93-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U096

alpha, alpha-Dimethyl benzyl hydroperoxide

alpha, alpha-Dimethyl benzyl hydroperoxide

80-15-9

CHOXD; CHRED; CARBN; BIODG; or CMBSt

CHOXD, CHRED; or CMBST

U097

Dimethylcarbamoyl chloride

Dimethylcarbamoyl chloride

79-44-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U098

1,1-Dimethylhydrazine

1,1-Dimethylhydrazine

57-14-7

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U099

1,2-Dimethylhydrazine

1,2-Dimethylhydrazine

540-73-8

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U101

2,4-Dimethylphenol

2,4-Dimethylphenol

105-67-9

0.036

14

U102

Dimethyl phthalate

Dimethyl phthalate

131-11-3

0.047

28

U103

Dimethyl sulfate

Dimethyl sulfate

77-78-1

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U105

2,4-Dinitrotoluene

2,4-Dinitrotoluene

121-14-2

0.32

140

U106

2,6-Dinitrotoluene

2,6-Dinitrotoluene

606-20-2

0.55

28

U107

Di-n-octyl phthalate

Di-n-octyl phthalate

117-84-0

0.017

28

U108

1,4-Dioxane

1,4-Dioxane

123-91-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

1,4-Dioxane, alternate 6

123-91-1

12.0

170

U109

1,2-Diphenylhydrazine

1,2-Diphenylhydrazine

122-66-7

CHOXD; CHRED; CARBN; BIODG; 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

0.40

14

U112

Ethyl acetate

Ethyl acetate

141-78-6

0.34

33

U113

Ethyl acrylate

Ethyl acrylate

140-88-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U114

Ethylenebisdithiocarbamic acid salts and esters

Ethylenebisdithiocarbamic acid

111-54-6

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U115

Ethylene oxide

Ethylene oxide

75-21-8

(WETOX or CHOXD) fb CARBN; or CMBST

CHOXD; or CMBST

Ethylene oxide; 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

U118

Ethyl methacrylate

Ethyl methacrylate

97-63-2

0.14

160

U119

Ethyl methane sulfonate

Ethyl methane sulfonate

62-50-0

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U120

Fluoranthene

Fluoranthene

206-44-0

0.068

3.4

U121

Trichlorofluoromethane

Trichlorofluoromethane

75-69-4

0.020

30

U122

Formaldehyde

Formaldehyde

50-00-0

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U123

Formic acid

Formic acid

64-18-6

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U124

Furan

Furan

110-00-9

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U125

Furfural

Furfural

98-01-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U126

Gylcidyaldehyde

Glycidyaldehyde

765-34-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U127

Hexachlorobenzene

Hexachlorobenzene

118-74-1

0.055

10

U128

Hexachlorobutadiene

Hexachlorobutadiene

87-68-3

0.055

5.6

U129

Lindane

alpha-BHC

319-84-6

0.00014

0.066

beta-BHC

319-85-7

0.00014

0.066

delta-BHC

319-86-8

0.023

0.066

gamma-BHC (Lindane)

58-89-9

0.0017

0.066

U130

Hexachlorocyclopentadiene

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

U131

Hexachloroethane

Hexachloroethane

67-72-1

0.055

30

U132

Hexachlorophene

Hexachlorophene

70-30-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U133

Hydrazine

Hydrazine

302-01-2

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U134

Hydrogen fluoride

Fluoride (measured in wastewaters only)

7664-39-3

35

ADGAS fb NEUTR; or NEUTR

U135

Hydrogen Sulfide

Hydrogen Sulfide

7783-06-4

CHOXD; CHRED; or CMBST

CHOXD; CHRED; or CMBST

U136

Cacodylic acid

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

U137

Indeno(1,2,3-c,d)pyrene

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

U138

Iodomethane

Iodomethane

74-88-4

0.19

65

U140

Isobutyl alcohol

Isobutyl alcohol

78-83-1

5.6

170

U141

Isosafrole

Isosafrole

120-58-1

0.081

2.6

U142

Kepone

Kepone

143-50-8

0.0011

0.13

U143

Lasiocarpine

Lasiocarpine

303-34-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U144

Lead acetate

Lead

7439-92-1

0.69

0.75 mg/L TCLP

U145

Lead phosphate

Lead

7439-92-1

0.69

0.75 mg/L TCLP

U146

Lead subacetate

Lead

7439-92-1

0.69

0.75 mg/L TCLP

U147

Maleic anhydride

Maleic anhydride

108-31-6

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U148

Maleic hydrazide

Maleic hydrazide

123-33-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U149

Malononitrile

Malononitrile

109-77-3

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U150

Melphalan

Malphalan

148-82-3

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U151

U151 (mercury) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.

Mercury

7439-97-6

NA

RMERC

U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are residues from RMERC only.

Mercury

7439-97-6

NA

0.20 mg/L TCLP

U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are not residues from RMERC.

Mercury

7439-97-6

NA

0.025 mg/L TCLP

All U151 (mercury) wastewaters.

Mercury

7439-97-6

0.15

NA

Elemental Mercury Contaminated with Radioactive Materials

Mercury

7439-97-6

NA

AMLGM

U152

Methacrylonitrile

Methacrylonitrile

126-98-7

0.24

84

U153

Methanethiol

Methanethiol

74-93-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U154

Methanol

Methanol

67-56-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

Methanol; alternate 6 set of standards for both wastewaters and nonwastewaters

67-56-1

5.6

0.75 mg/L TCLP

U155

Methapyrilene

Methapyrilene

91-80-5

0.081

1.5

U156

Methyl chlorocarbonate

Methyl chlorocarbonate

79-22-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U157

3-Methylcholanthrene

3-Methylcholanthrene

56-49-5

0.0055

15

U158

4,4′-Methylene bis(2-chloroaniline)

4,4′-Methylene bis(2-chloroaniline)

101-14-4

0.50

30

U159

Methyl ethyl ketone

Methyl ethyl ketone

78-93-3

0.28

36

U160

Methyl ethyl ketone peroxide

Methyl ethyl ketone peroxide

1338-23-4

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U161

Methyl isobutyl ketone

Methyl isobutyl ketone

108-10-1

0.14

33

U162

Methyl methacrylate

Methyl methacrylate

80-62-6

0.14

160

U163

N-Methyl N′-nitro N-nitrosoguanidine

N-Methyl N′-nitro N-nitrosoguanidine

70-25-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U164

Methylthiouracil

Methylthiouracil

56-04-2

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U165

Naphthalene

Naphthalene

91-20-3

0.059

5.6

U166

1,4-Naphthoquinone

1,4-Naphthoquinone

130-15-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U167

1-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

U170

p-Nitrophenol

p-Nitrophenol

100-02-7

0.12

29

U171

2-Nitropropane

2-Nitropropane

79-46-9

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U172

N-Nitrosodi-n-butylamine

N-Nitrosodi-n-butylamine

924-16-3

0.040

17

U173

N-Nitrosodiethanolamine

N-Nitrosodiethanolamine

1116-54-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U174

N-Nitrosodiethylamine

N-Nitrosodiethylamine

55-18-5

0.40

28

U176

N-Nitroso-N-ethylurea

N-Nitroso-N-ethylurea

759-73-9

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U177

N-Nitroso-N-methylurea

N-Nitroso-N-methylurea

684-93-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U178

N-Nitroso-N-methylurethane

N-Nitroso-N-methylurethane

615-53-2

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U179

N-Nitrosopiperidine

N-Nitrosopiperidine

100-75-4

0.013

35

U180

N-Nitrosopyrrolidine

N-Nitrosopyrrolidine

930-55-2

0.013

35

U181

5-Nitro-o-toluidine

5-Nitro-o-toluidine

99-55-8

0.32

28

U182

Paraldehyde

Paraldehyde

123-63-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U183

Pentachlorobenzene

Pentachlorobenzene

608-93-5

0.055

10

U184

Pentachloroethane

Pentachloroethane

76-01-7

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

Pentachloroethane; 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

U188

Phenol

Phenol

108-95-2

0.039

6.2

U189

Phosphorus sulfide

Phosphorus sulfide

1314-80-3

CHOXD; CHRED; or CMBST

CHOXd; CHRED; or CMBST

U190

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0

0.055

28

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

85-44-9

0.055

28

U191

2-Picoline

2-Picoline

109-06-8

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U192

Pronamide

Pronamide

23950-58-5

0.093

1.5

U193

1,3-Propane sultone

1,3-Propane sultone

1120-71-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U194

n-Propylamine

n-Propylamine

107-10-8

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U196

Pyridine

Pyridine

110-86-1

0.014

16

U197

p-Benzoquinone

p-Benzoquinone

106-51-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U200

Reserpine

Reserpine

50-55-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U201

Resorcinol

Resorcinol

108-46-3

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U203

Safrole

Safrole

94-59-7

0.081

22

U204

Selenium dioxide

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

U205

Selenium sulfide

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

U206

Streptozotocin

Streptozotocin

18883-66-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U207

1,2,4,5-Tetrachlorobenzene

1,2,4,5-Tetrachlorobenzene

95-94-5

0.055

14

U208

1,1,1,2-Tetrachloroethane

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

U209

1,1,2,2-Tetrachloroethane

1,1,2,2-Tetrachloroethane

79-34-5

0.057

6.0

U210

Tetrachloroethylene

Tetrachloroethylene

127-18-4

0.056

6.0

U211

Carbon tetrachloride

Carbon tetrachloride

56-23-5

0.057

6.0

U213

Tetrahydrofuran

Tetrahydrofuran

109-99-9

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U214

Thallium (I) acetate

Thallium (measured in wastewaters only)

7440-28-0

1.4

RTHRM; or STABL

U215

Thallium (I) carbonate

Thallium (measured in wastewaters only)

7440-28-0

1.4

RTHRM; or STABL

U216

Thallium (I) chloride

Thallium (measured in wastewaters only)

7440-28-0

1.4

RTHRM; or STABL

U217

Thallium (I) nitrate

Thallium (measured in wastewaters only)

7440-28-0

1.4

RTHRM; or STABL

U218

Thioacetamide

Thioacetamide

62-55-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U219

Thiourea

Thiourea

62-56-6

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U220

Toluene

Toluene

108-88-3

0.080

10

U221

Toluenediamine

Toluenediamine

25376-45-8

CARBN; or CMBST

CMBST

U222

o-Toluidine hydrochloride

o-Toluidine hydrochloride

636-21-5

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U223

Toluene diisocyanate

Toluene diisocyanate

26471-62-5

CARBN; or CMBST

CMBST

U225

Bromoform (Tribromomethane)

Bromoform (Tribromomethane)

75-25-2

0.63

15

U226

1,1,1-Trichloroethane

1,1,1-Trichloroethane

71-55-6

0.054

6.0

U227

1,1,2-Trichloroethane

1,1,2-Trichloroethane

79-00-5

0.054

6.0

U228

Trichloroethylene

Trichloroethylene

79-01-6

0.054

6.0

U234

1,3,5-Trinitrobenzene

1,3,5-Trinitrobenzene

99-35-4

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U235

tris-(2,3-Dibromopropyl)-phosphate

tris-(2,3-Dibromopropyl)-phosphate

126-72-7

0.11

0.10

U236

Trypan Blue

Trypan Blue

72-57-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U237

Uracil mustard

Uracil mustard

66-75-1

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U238

Urethane (Ethyl carbamate)

Urethane (Ethyl carbamate)

51-79-6

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U239

Xylenes

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

U240

2,4-D (2,4-Dichlorophenoxyacetic acid)

2,4-D(2,4-Dichlorophenoxyacetic acid)

94-75-7

0.72

10

2,4-D (2,4-Dichlorophenoxyacetic acid) salts and esters

NA

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U243

Hexachloropropylene

Hexachloropropylene

1888-71-7

0.035

30

U244

Thiram

Thiram

137-26-8

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U246

Cyanogen bromide

Cyanogen bromide

506-68-3

CHOXD; WETOX; or CMBST

CHOXD; WETOX; or CMBST

U247

Methoxychlor

Methoxychlor

72-43-5

0.25

0.18

U248

Warfarin, & salts, when present at concentrations of 0.3% or less

Warfarin

81-81-2

(WETOX or CHOXD) fb CARBN; or CMBST

CMBST

U249

Zinc phosphide, Zn 3 ,P 2 , when present at concentrations of 10% or less

Zinc Phosphide

1314-84-7

CHOXD; CHRED; or CMBST

CHOXD; CHRED; or CMBST

U271

Benomyl 10

Benomyl

17804-35-2

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U278

Bendiocarb 10

Bendiocarb

22781-23-3

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U279

Carbaryl 10

Carbaryl

63-25-2

0.006; or CMBST, CHOXD, BIODG or CARBN

0.14; or CMBST

U280

Barban 10

Barban

101-27-9

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U328

o-Toluidine

o-Toluidine

95-53-4

CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN

CMBST

U353

p-Toluidine

p-Toluidine

106-49-0

CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN

CMBST

U359

2-Ethoxyethanol

2-Ethoxyethanol

110-80-5

CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN

CMBST

U364

Bendiocarb phenol 10

Bendiocarb phenol

22961-82-6

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U367

Carbofuran phenol 10

Carbofuran phenol

1563-38-8

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U372

Carbendazim 10

Carbendazim

10605-21-7

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U373

Propham 10

Propham

122-42-9

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U387

Prosulfocarb 10

Prosulfocarb

52888-80-9

0.042; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U389

Triallate 10

Triallate

2303-17-5

0.042; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U394

A2213 10

A2213

30558-43-1

0.042; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U395

Diethylene glycol, dicarbamate 10

Diethylene glycol, dicarbamate

5952-26-1

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U404

Triethylamine 10

Triethylamine

121-44-8

0.081; or CMBST, CHOXD, BIODG or CARBN

1.5; or CMBST

U409

Thiophanate-methyl 10

Thiophanate-methyl

23564-05-8

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U410

Thiodicarb 10

Thiodicarb

59669-26-0

0.019; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

U411

Propoxur 10

Propoxur

114-26-1

0.056; or CMBST, CHOXD, BIODG or CARBN

1.4; or CMBST

Footnotes to Treatment Standard Table 268.40

1

The waste descriptions provided in this table do not replace waste descriptions in 40 CFR 261. Descriptions of Treatment/Regulatory Subcategories are provided, as needed, to distinguish between applicability of different standards.

2

CAS means Chemical Abstract Services. When the waste code and/or regulated constituents are described as a combination of a chemical with its salts and/or esters, the CAS number is given for the parent compound only.

3

Concentration standards for wastewaters are expressed in mg/L and are based on analysis of composite samples.

4

All treatment standards expressed as a Technology Code or combination of Technology Codes are explained in detail in 40 CFR 268.42 Table 1—Technology Codes and Descriptions of Technology-Based Standards.

5

Except for Metals (EP or TCLP) and Cyanides (Total and Amenable) the nonwastewater treatment standards expressed as a concentration were established, in part, based upon incineration in units operated in accordance with the technical requirements of 40 CFR Part 264 Subpart O or Part 265 Subpart O, 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 40 CFR 268.40(d). All concentration standards for nonwastewaters are based on analysis of grab samples.

6

[Reserved]

7

Both Cyanides (Total) and Cyanides (Amenable) for nonwastewaters are to be analyzed using Method 9010C or 9012B, found in “Test Methods' for Evaluating Solid Waste, Physical/Chemical Methods,” EPA Publication SW-846, as incorporated by reference in 40 CFR 260.11, with a sample size of 10 grams and a distillation time of one hour and 15 minutes.

8

These wastes, when rendered nonhazardous and then subsequently managed in CWA, or CWA-equivalent systems are not subject to treatment standards. (See § 268.1(c0(3) and (4)).

9

These wastes, when rendered nonhazardous and then subsequently injected in a Class SDWA well, are not subject to treatment standards. (See § 148.1(d)).

10

The treatment standard for this waste may be satisfied by either meeting the constituent concentrations in this table or by treating the waste by the specified technologies: combustion, as defined by the technology code CMBST at § 268.42 Table 1 of this Part, for nonwastewaters; and biodegradation as defined by the technology code BIODG, carbon adsorption as defined by the technology code CARBN, chemical oxidation as defined by the technology code CHOXD, or combustion as defined as technology code CMBST at § 268.42 Table 1 of this Part, for wastewaters.

11

For these wastes, the definition of CMBST is limited to: (1) combustion units operating under 40 CFR 266, (2) combustion units permitted under 40 CFR Part 264, Subpart O, or (3) combustion units operating under 40 CFR 265, Subpart O, which have obtained a determination of equivalent treatment under 268.42(b).

12

Disposal of K175 wastes that have complied with all applicable 40 CFR 268.40 treatment standards must also be macroencapsulated in accordance with 40 CFR 268.45 Table 1 unless the waste is placed in:

(1) A Subtitle C monofill containing only K175 wastes that meet all applicable 40 CFR 268.40 treatment standards; or

(2) A dedicated Subtitle C landfill cell in which all other wastes being co-disposed are at pH≤6.0.

§ 268.41 Treatment standards expressed as concentrations in waste extract.

For the requirements previously found in this section and for treatment standards in Table CCWE—Constituent Concentrations in Waste Extracts, refer to § 268.40.

§ 268.42 Treatment standards expressed as specified technologies.

Note:

For the requirements previously found in this section in Table 2—Technology-Based Standards By RCRA Waste Code, and Table 3—Technology-Based Standards for Specific Radioactive Hazardous Mixed Waste, refer to § 268.40.

(a) The following wastes in the table in § 268.40 “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 entitled “Technology Codes and Description of Technology-Based Standards” in this section.

Table 1—Technology Codes and Description of Technology-Based Standards

Technology code

Description of technology-based standards

ADGAS:

Venting of compressed gases into an absorbing or reacting media ( i.e. , solid or liquid)—venting can be accomplished through physical release utilizing valves/piping; physical penetration of the container; and/or penetration through detonation.

AMLGM:

Amalgamation of liquid, elemental mercury contaminated with radioactive materials utilizing inorganic reagents such as copper, zinc, nickel, gold, and sulfur that result in a nonliquid, semi-solid amalgam and thereby reducing potential emissions of elemental mercury vapors to the air.

BIODG:

Biodegradation of organics or non-metallic inorganics ( i.e. , degradable inorganics that contain the elements of phosphorus, nitrogen, and sulfur) in units operated under either aerobic or anaerobic conditions such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., Total Organic Carbon can often be used as an indicator parameter for the biodegradation of many organic constituents that cannot be directly analyzed in wastewater residues).

CARBN:

Carbon adsorption (granulated or powdered) of non-metallic inorganics, organo-metallics, and/or organic constituents, operated such that a surrogate compound or indicator parameter has not undergone breakthrough (e.g., Total Organic Carbon can often be used as an indicator parameter for the adsorption of many organic constituents that cannot be directly analyzed in wastewater residues). Breakthrough occurs when the carbon has become saturated with the constituent (or indicator parameter) and substantial change in adsorption rate associated with that constituent occurs.

CHOXD:

Chemical or electrolytic oxidation utilizing the following oxidation reagents (or waste reagents) or combinations of reagents: (1) Hypochlorite (e.g., bleach); (2) chlorine; (3) chlorine dioxide; (4) ozone or UV (ultraviolet light) assisted ozone; (5) peroxides; (6) persulfates; (7) perchlorates; (8) permangantes; and/or (9) other oxidizing reagents of equivalent efficiency, performed in units operated such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., Total Organic Carbon can often be used as an indicator parameter for the oxidation of many organic constituents that cannot be directly analyzed in wastewater residues). Chemical oxidation specifically includes what is commonly referred to as alkaline chlorination.

CHRED:

Chemical reduction utilizing the following reducing reagents (or waste reagents) or combinations of reagents: (1) Sulfur dioxide; (2) sodium, potassium, or alkali salts or sulfites, bisulfites, metabisulfites, and polyethylene glycols (e.g., NaPEG and KPEG); (3) sodium hydrosulfide; (4) ferrous salts; and/or (5) other reducing reagents of equivalent efficiency, performed in units operated such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., Total Organic Halogens can often be used as an indicator parameter for the reduction of many halogenated organic constituents that cannot be directly analyzed in wastewater residues). Chemical reduction is commonly used for the reduction of hexavalent chromium to the trivalent state.

CMBST:

High temperature organic destruction technologies, such as combustion in incinerators, boilers, or industrial furnaces operated in accordance with the applicable requirements of 40 CFR part 264, subpart O, or 40 CFR part 265, subpart O, or 40 CFR part 266, subpart H, and in other units operated in accordance with applicable technical operating requirements; and certain non-combustive technologies, such as the Catalytic Extraction Process.

DEACT:

Deactivation to remove the hazardous characteristics of a waste due to its ignitability, corrosivity, and/or reactivity.

FSUBS:

Fuel substitution in units operated in accordance with applicable technical operating requirements.

HLVIT:

Vitrification of high level mixed radioactive wastes in units in compliance with all applicable radioactive protection requirements under control of the Nuclear Regulatory Commission.

IMERC:

Incineration of wastes containing organics and mercury in units operated in accordance with the technical operating requirements of 40 CFR part 264 subpart 0 and part 265 subpart 0. All wastewater and nonwastewater residues derived from this process must then comply with the corresponding treatment standards per waste code with consideration of any applicable subcategories (e.g., High or Low Mercury Subcategories).

INCIN:

Incineration in units operated in accordance with the technical operating requirements of 40 CFR part 264 subpart 0 and part 265 subpart 0.

LLEXT:

Liquid-liquid extraction (often referred to as solvent extraction) of organics from liquid wastes into an immiscible solvent for which the hazardous constituents have a greater solvent affinity, resulting in an extract high in organics that must undergo either incineration, reuse as a fuel, or other recovery/reuse and a raffinate (extracted liquid waste) proportionately low in organics that must undergo further treatment as specified in the standard.

MACRO:

Macroencapsulation with surface coating materials such as polymeric organics (e.g., resins and plastics) or with a jacket of inert inorganic materials to substantially reduce surface exposure to potential leaching media. Macroencapsulation specifically does not include any material that would be classified as a tank or container according to 40 CFR 260.10.

NEUTR:

Neutralization with the following reagents (or waste reagents) or combinations of reagents: (1) Acids; (2) bases; or (3) water (including wastewaters) resulting in a pH greater than 2 but less than 12.5 as measured in the aqueous residuals.

NLDBR:

No land disposal based on recycling.

POLYM:

Formation of complex high-molecular weight solids through polymerization of monomers in high-TOC D001 non-wastewaters which are chemical components in the manufacture of plastics.

PRECP:

Chemical precipitation of metals and other inorganics as insoluble precipitates of oxides, hydroxides, carbonates, sulfides, sulfates, chlorides, fluorides, or phosphates. The following reagents (or waste reagents) are typically used alone or in combination: (1) Lime ( i.e. , containing oxides and/or hydroxides of calcium and/or magnesium; (2) caustic ( i.e. , sodium and/or potassium hydroxides; (3) soda ash ( i.e. , sodium carbonate); (4) sodium sulfide; (5) ferric sulfate or ferric chloride; (6) alum; or (7) sodium sulfate. Additional floculating, coagulation or similar reagents/processes that enhance sludge dewatering characteristics are not precluded from use.

RBERY:

Thermal recovery of Beryllium.

RCGAS:

Recovery/reuse of compressed gases including techniques such as reprocessing of the gases for reuse/resale; filtering/adsorption of impurities; remixing for direct reuse or resale; and use of the gas as a fuel source.

RCORR:

Recovery of acids or bases utilizing one or more of the following recovery technologies: (1) Distillation ( i.e. , thermal concentration); (2) ion exchange; (3) resin or solid adsorption; (4) reverse osmosis; and/or (5) incineration for the recovery of acid—Note: this does not preclude the use of other physical phase separation or concentration techniques such as decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies.

RLEAD:

Thermal recovery of lead in secondary lead smelters.

RMERC:

Retorting or roasting in a thermal processing unit capable of volatilizing mercury and subsequently condensing the volatilized mercury for recovery. The retorting or roasting unit (or facility) must be subject to one or more of the following: (a) a National Emissions Standard for Hazardous Air Pollutants (NESHAP) for mercury; (b) a Best Available Control Technology (BACT) or a Lowest Achievable Emission Rate (LAER) standard for mercury imposed pursuant to a Prevention of Significant Deterioration (PSD) permit; or (c) a state permit that establishes emission limitations (within meaning of section 302 of the Clean Air Act) for mercury. All wastewater and nonwastewater residues derived from this process must then comply with the corresponding treatment standards per waste code with consideration of any applicable subcategories (e.g., High or Low Mercury Subcategories).

RMETL:

Recovery of metals or inorganics utilizing one or more of the following direct physical/removal technologies: (1) Ion exchange; (2) resin or solid ( i.e. , zeolites) adsorption; (3) reverse osmosis; (4) chelation/solvent extraction; (5) freeze crystalization; (6) ultrafiltration and/or (7) simple precipitation ( i.e. , crystalization)— Note: This does not preclude the use of other physical phase separation or concentration techniques such as decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies.

RORGS:

Recovery of organics utilizing one or more of the following technologies: (1) Distillation; (2) thin film evaporation; (3) steam stripping; (4) carbon adsorption; (5) critical fluid extraction; (6) liquid-liquid extraction; (7) precipitation/crystalization (including freeze crystallization); or (8) chemical phase separation techniques ( i.e. , addition of acids, bases, demulsifiers, or similar chemicals);—Note: this does not preclude the use of other physical phase separation techniques such as a decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies.

RTHRM:

Thermal recovery of metals or inorganics from nonwastewaters in units identified as industrial furnaces according to 40 CFR 260.10 (1), (6), (7), (11), and (12) under the definition of “industrial furnaces”.

RZINC:

Resmelting in high temperature metal recovery units for the purpose of recovery of zinc.

STABL:

Stabilization with the following reagents (or waste reagents) or combinations of reagents: (1) Portland cement; or (2) lime/pozzolans (e.g., fly ash and cement kiln dust)—this does not preclude the addition of reagents (e.g., iron salts, silicates, and clays) designed to enhance the set/cure time and/or compressive strength, or to overall reduce the leachability of the metal or inorganic.

SSTRP:

Steam stripping of organics from liquid wastes utilizing direct application of steam to the wastes operated such that liquid and vapor flow rates, as well as temperature and pressure ranges, have been optimized, monitored, and maintained. These operating parameters are dependent upon the design parameters of the unit, such as the number of separation stages and the internal column design, thus, resulting in a condensed extract high in organics that must undergo either incineration, reuse as a fuel, or other recovery/reuse and an extracted wastewater that must undergo further treatment as specified in the standard.

VTD:

Vacuum thermal desorption of low-level radioactive hazardous mixed waste in units in compliance with all applicable radioactive protection requirements under control of the Nuclear Regulatory Commission.

WETOX:

Wet air oxidation performed in units operated such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., Total Organic Carbon can often be used as an indicator parameter for the oxidation of many organic constituents that cannot be directly analyzed in wastewater residues).

WTRRX:

Controlled reaction with water for highly reactive inorganic or organic chemicals with precautionary controls for protection of workers from potential violent reactions as well as precautionary controls for potential emissions of toxic/ignitable levels of gases released during the reaction.

Note 1: When a combination of these technologies ( i.e. , a treatment train) is specified as a single treatment standard, the order of application is specified in § 268.42, Table 2 by indicating the five letter technology code that must be applied first, then the designation “fb.” (an abbreviation for “followed by”), then the five letter technology code for the technology that must be applied next, and so on.

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

(b) Any person may submit an application to the Administrator 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 section for wastes or specified in Table 1 of § 268.45 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 section for wastes or in Table 1 of § 268.45 for hazardous debris. Any approval must be stated in writing and may contain such provisions and conditions as the Administrator 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 subpart D treatment standards, lab packs are eligible for land disposal provided the following requirements are met:

(1) The lab packs comply with the applicable provisions of 40 CFR 264.316 and 40 CFR 265.316;

(2) The lab pack does not contain any of the wastes listed in Appendix IV to part 268;

(3) The lab packs are incinerated in accordance with the requirements of 40 CFR part 264, subpart O or 40 CFR part 265, subpart O; 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 subpart D of this part.

(d) Radioactive hazardous mixed wastes are subject to the treatment standards in § 268.40. Where treatment standards are specified for radioactive mixed wastes in the Table of Treatment Standards, those treatment standards will govern. Where there is no specific treatment standard for radioactive mixed waste, the treatment standard for the hazardous waste (as designated by EPA waste code) applies. Hazardous debris containing radioactive waste is subject to the treatment standards specified in § 268.45.

§ 268.43 Treatment standards expressed as waste concentrations.

For the requirements previously found in this section and for treatment standards in Table CCW—Constituent Concentrations in Wastes, refer to § 268.40.

§ 268.44 Variance from a treatment standard.

(a) Based on a petition filed by a generator or treater of hazardous waste, the Administrator may approve a variance from an applicable treatment standard if:

(1) It is not physically possible to treat the waste to the level specified in the treatment standard, or by the method specified as the treatment standard. To show that this is the case, the petitioner must demonstrate that because the physical or chemical properties of the waste differ significantly from waste analyzed in developing the treatment standard, the waste cannot be treated to the specified level or by the specified method; or

(2) It is inappropriate to require the waste to be treated to the level specified in the treatment standard or by the method specified as the treatment standard, even though such treatment is technically possible. To show that this is the case, the petitioner must either demonstrate that:

(i) Treatment to the specified level or by the specified method is technically inappropriate (for example, resulting in combustion of large amounts of mildly contaminated environmental media); or

(ii) For remediation waste only, treatment to the specified level or by the specified method is environmentally inappropriate because it would likely discourage aggressive remediation.

(b) Each petition must be submitted in accordance with the procedures in § 260.20.

(c) Each petition must include the following statement signed by the petitioner or an authorized representative:

I certify under penalty of law that I have personally examined and am familiar with the information submitted in this petition and all attached documents, and that, based on my inquiry of those individuals immediately responsible for obtaining the information, I believe that the submitted information is true, accurate, and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment.

(d) After receiving a petition for variance from a treatment standard, the Administrator may request any additional information or samples which he may require to evaluate the petition. Additional copies of the complete petition may be requested as needed to send to affected states and Regional Offices.

(e) The Administrator will give public notice in the Federal Register of the intent to approve or deny a petition and provide an opportunity for public comment. The final decision on a variance from a treatment standard will be published in the Federal Register.

(f) A generator, treatment facility, or disposal facility that is managing a waste covered by a variance from the treatment standards must comply with the waste analysis requirements for restricted wastes found under § 268.7.

(g) During the petition review process, the applicant is required to comply with all restrictions on land disposal under this part once the effective date for the waste has been reached.

(h) Based on a petition filed by a generator or treater of hazardous waste, the Administrator or his or her delegated representative may approve a site-specific variance from an applicable treatment standard if:

(1) It is not physically possible to treat the waste to the level specified in the treatment standard, or by the method specified as the treatment standard. To show that this is the case, the petitioner must demonstrate that because the physical or chemical properties of the waste differ significantly from waste analyzed in developing the treatment standard, the waste cannot be treated to the specified level or by the specified method; or

(2) It is inappropriate to require the waste to be treated to the level specified in the treatment standard or by the method specified as the treatment standard, even though such treatment is technically possible. To show that this is the case, the petitioner must either demonstrate that:

(i) Treatment to the specified level or by the specified method is technically inappropriate (for example, resulting in combustion of large amounts of mildly contaminated environmental media where the treatment standard is not based on combustion of such media); or

(ii) For remediation waste only, treatment to the specified level or by the specified method is environmentally inappropriate because it would likely discourage aggressive remediation.

(3) For contaminated soil only, treatment to the level or by the method specified in the soil treatment standards would result in concentrations of hazardous constituents that are below ( i.e. , lower than) the concentrations necessary to minimize short- and long-term threats to human health and the environment. Treatment variances approved under this paragraph must:

(i) At a minimum, impose alternative land disposal restriction treatment standards that, using a reasonable maximum exposure scenario:

(A) For carcinogens, achieve constituent concentrations that result in the total excess risk to an individual exposed over a lifetime generally falling within a range from 10 −4 to 10 −6 ; and

(B) For constituents with non-carcinogenic effects, achieve constituent concentrations that an individual could be exposed to on a daily basis without appreciable risk of deleterious effect during a lifetime.

(ii) Not consider post-land-disposal controls.

(4) For contaminated soil only, treatment to the level or by the method specified in the soil treatment standards would result in concentrations of hazardous constituents that are below ( i.e. , lower than) natural background concentrations at the site where the contaminated soil will land disposed.

(5) Public notice and a reasonable opportunity for public comment must be provided before granting or denying a petition.

(i) Each application for a site-specific variance from a treatment standard must include the information in § 260.20(b)(1)-(4);

(j) After receiving an application for a site-specific variance from a treatment standard, the Assistant Administrator, or his delegated representative, may request any additional information or samples which may be required to evaluate the application.

(k) A generator, treatment facility, or disposal facility that is managing a waste covered by a site-specific variance from a treatment standard must comply with the waste analysis requirements for restricted wastes found under § 268.7.

(l) During the application review process, the applicant for a site-specific variance must comply with all restrictions on land disposal under this part once the effective date for the waste has been reached.

(m) For all variances, the petitioner must also demonstrate that compliance with any given treatment variance is sufficient to minimize threats to human health and the environment posed by land disposal of the waste. In evaluating this demonstration, EPA may take into account whether a treatment variance should be approved if the subject waste is to be used in a manner constituting disposal pursuant to 40 CFR 266.20 through 266.23.

(n) [Reserved]

(o) The following facilities are excluded from the treatment standards under § 268.40, and are subject to the following constituent concentrations:

Table—Wastes Excluded From the Treatment Standards Under § 268.40

Facility name 1 and address

Waste code

See also

Regulated hazardous constituent

Wastewaters

Nonwastewaters

Concentration (mg/l)

Notes

Concentration (mg/kg)

Notes

Craftsman Plating and Tinning, Corp., Chicago, IL

F006

Table CCWE in 268.40

Cyanides (Total)

1.2

( 2 )

1800

( 4 )

Cyanides (Amenable)

.86

( 2 and 3 )

30

( 4 )

Cadmium

1.6

NA

Chromium

.32

NA

Lead

.040

NA

Nickel

.44

NA

CWM Chemical Services, LLC, Model City, New York

K088 9

Standards under § 268.40

Arsenic

1.4

NA

5.0 mg/L TCLP

NA

DuPont Environmental Treatment Chambers Works, Deepwater, NJ

F039

Standards under § 268.40

1,3-phenylenediamine 1,3-PDA

NA

NA

CMBST; CHOXD fb BIODG or CARBN; or BIODG fb CARBN

( 13 )

Dupont Environmental Treatment—Chambers Works Wastewater Treatment Plant, Deepwater, NJ 8

K088

Standards under § 268.40

Arsenic

1.4

NA

5.0 mg/L TCLP

NA

Energy Solutions LLC, Clive, UT ( 14 )

P- and U-listed hazardous waste requiring CMBST

Standards under 268.40

NA

NA

NA

CMBST or VTD

NA

Guardian Industries Jefferson Hills, PA (6), (11), and (12)

D010 Standards under 268.40

Selenium

NA

NA

11 mg/L TCLP

NA

Owens Brockway Glass Container Company, Vernon, CA 6

D010

Standards under § 268.40

Selenium

NA

NA

51 mg/L TCLP

( 15 )

Owens Brockway Glass Container Company, Vernon, CA 6

D010

Standards under § 268.40

Selenium

NA

NA

59 mg/L TCLP

( 16 )

Northwestern Plating Works, Inc., Chicago, IL

F006

Table CCWE in 268.40

Cyanides (Total)

1.2

( 2 and 3 )

970

( 4 )

Cyanides (Amenable)

.86

( 2 )

30

( 4 )

Cadmium

1.6

NA

Chromium

.32

NA

Lead

.040

NA

Nickel

.44

NA

St. Gobain Containers, El Monte, CA 5 7

D010

Standards under § 268.40

Selenium

NA

NA

25 mg/L TCLP

NA

United States Department of Energy (Energy), Richland, WA 17

F001-F005, D001-D011, D018, D019, D022, D028-D030, D033-D036, D038-D041, and D043 18

NA

For waste codes F001-F005, the constituents are limited to those associated with spent solvent activities at the Facility documented through process knowledge.

For constituents, as applicable, associated with D waste codes under the “Waste Code” column, see 40 CFR 268.40.

NA

NA

STABL 19 20

NA.

U.S. Ecology Idaho, Incorporated, Grandview, Idaho

K088 10

Standards under § 268.40

Arsenic

1.4

NA

5.0 mg/L TCLP

NA

( 1 )—A facility may certify compliance with these treatment standards according to provisions in 40 CFR 268.7.

( 2 )—Cyanide Wastewater Standards for F006 are based on analysis of composite samples.

( 3 )—These facilities must comply with 0.86 mg/l for amenable cyanides in the wastewater exiting the alkaline chlorination system. These facilities must also comply with 40 CFR § 268.7.a.4 for appropriate monitoring frequency consistent with the facilities' waste analysis plan.

( 4 )—Cyanide nonwastewaters are analyzed using SW-846 Method 9010C or 9012B, as incorporated by reference in § 260.11 of this chapter, sample size 10 grams, distillation time, 1 hour and 15 minutes.

( 5 )—Alternative D010 selenium standard only applies to dry scrubber solid from glass manufacturing wastes.

( 6 )—Alternative D010 selenium standard only applies to electrostatic precipitator dust generated during glass manufacturing operations.

7 D010 wastes generated by this facility must be treated by Chemical Waste Management, Inc. at its Kettleman Hills facility in Kettleman City, California.

( 8 )—Dupont Environmental Treatment-Chambers Works must dispose of this waste in their on-site Subtitle C hazardous waste landfill.

( 9 )—This treatment standard applies only to K088-derived bag house dust, incinerator ash, and filtercake at this facility.

( 10 )—This treatment standard applies only to K088-derived air emission control dust generated by this facility.

( 11 )—D010 wastes generated by this facility may be treated by Heritage Environmental Services, LLC at their RCRA permitted treatment facility in Indianapolis, Indiana or by Chemical Waste Management, Chemical Services Inc. at their RCRA permitted treatment facility in Model City, New York.

( 12 )—D010 waste generated by this facility may be treated by Chemical Waste Management, Chemical Services, LLC. at their treatment facility in Model City, New York.

( 13 )—This treatment standard applies to 1,3-PDA in biosludge from treatment of F039.

( 14 )—This site-specific treatment variance applies only to solid treatment residue resulting from the vacuum thermal desorption (VTD) of P- and U-listed hazardous waste containing radioactive contamination (“mixed waste”) at the Energy Solutions ' LLC facility in Clive, Utah that otherwise requires CMBST as the LDR treatment standard. Once the P- and U-listed mixed waste are treated using VTD, the solid treatment residue can be land disposed at Energy Solutions ' onsite RCRA permitted mixed waste landfill without further treatment. This treatment variance is conditioned on Energy Solutions complying with a Waste Family Demonstration Testing Plan specifically addressing the treatment of these P- and U-listed wastes, with this plan being implemented through a RCRA Part B permit modification for the VTD unit.

15 This alternative standard applies only to D010 wastes generated by this facility and treated by Chemical Waste Management, Inc. at its Kettleman Hills facility in Kettleman City, California.

16 This alternative standard applies only to D010 wastes generated by this facility and treated by U.S. Ecology Nevada at its facility in Beatty, Nevada. This alternative treatment standard is conditioned on the waste-to-reagent ratio not exceeding 1 to 0.45.

17 The STABL treatment standard applies to the separated and pretreated tank waste under the 2,000-gallon TBI Demonstration.

18 The waste codes included in this column are those identified on the current version of the Dangerous Waste Permit Application Part A form for the Hanford Double Shell Tank System, Rev. 04 (December 14, 2009), except for F039 which has not been accepted into the Double Shell Tanks.

19 Sampling after treatment will be conducted at the treatment facility for the purpose of assessing the extent of treatment performance against the NWW numerical standards at 40 CFR 268.40 and, as applicable, at 40 CFR 268.48. Waste treated using STABL may not be land disposed until LDR constituents are below the non-wastewater numerical standards at 40 CFR 268.40 and 268.48.

20 Treatment using the STABL treatment method shall be performed, and the treated waste shall be disposed of, at Energy Solutions in Clive, Utah, and/or Waste Control Specialists in Andrews County, Texas.

Note: NA means Not Applicable.

§ 268.45 Treatment standards for hazardous debris.

(a) Treatment standards. Hazardous debris must be treated prior to land disposal as follows unless EPA determines under § 261.3(f)(2) of this chapter that the debris is no longer contaminated with hazardous waste or the debris is treated to the waste-specific treatment standard provided in this subpart 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 section using the technology or technologies identified in Table 1 of this section.

(2) Characteristic debris. Hazardous debris that exhibits the characteristic of ignitability, corrosivity, or reactivity identified under §§ 261.21, 261.22, and 261.23 of this chapter, respectively, must be deactivated by treatment using one of the technologies identified in Table 1 of this section.

(3) Mixtures of debris types. The treatment standards of Table 1 in this section 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 section must be treated for each contaminant using one or more treatment technologies identified in Table 1 of this section. If an immobilization technology is used in a treatment train, it must be the last treatment technology used.

(5) Waste 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 section, 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 (TC) by § 261.24 of this chapter are those EP constituents for which the debris exhibits the TC 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 § 268.40.

(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 specified extraction or destruction technologies in Table 1 of this section and that does not exhibit a characteristic of hazardous waste identified under subpart C, part 261, of this chapter after treatment is not a hazardous waste and need not be managed in a subtitle C facility. Hazardous debris contaminated with a listed waste that is treated by an immobilization technology specified in Table 1 is a hazardous waste and must be managed in a subtitle C facility.

(d) Treatment residuals —(1) General requirements. Except as provided by paragraphs (d)(2) and (d)(4) of this section:

(i) Residue from the treatment of hazardous debris must be separated from the treated debris using simple physical or mechanical means; and

(ii) Residue from the treatment of hazardous debris is subject to the waste-specific treatment standards provided by subpart D of this part 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 section, must be deactivated prior to land disposal and is not subject to the waste-specific treatment standards of subpart D of this part.

(3) Cyanide-reactive debris. Residue from the treatment of debris that is reactive because of cyanide must meet the treatment standards for D003 in “Treatment Standards for Hazardous Wastes” at § 268.40.

(4) Ignitable nonwastewater residue. Ignitable nonwastewaster residue containing equal to or greater than 10% 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 section.

Table 1—Alternative Treatment Standards For Hazardous Debris 1

Technology description

Performance and/or design and operating standard

Contaminant restrictions 2

A. Extraction Technologies:

1. Physical Extraction

a. Abrasive Blasting: Removal of contaminated debris surface layers using water and/or air pressure to propel a solid media (e.g., steel shot, aluminum oxide grit, plastic beads)

Glass, Metal, Plastic, Rubber: Treatment to a clean debris surface. 3 Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Removal of at least 0.6 cm of the surface layer; treatment to a clean debris surface. 3

All Debris: None.

b. Scarification, Grinding, and Planing: Process utilizing striking piston heads, saws, or rotating grinding wheels such that contaminated debris surface layers are removed

Same as above

Same as above.

c. Spalling: Drilling or chipping holes at appropriate locations and depth in the contaminated debris surface and applying a tool which exerts a force on the sides of those holes such that the surface layer is removed. The surface layer removed remains hazardous debris subject to the debris treatment standards

Same as above

Same as above.

d. Vibratory Finishing: Process utilizing scrubbing media, flushing fluid, and oscillating energy such that hazardous contaminants or contaminated debris surface layers are removed. 4

Same as above

Same as above.

e. High Pressure Steam and Water Sprays: Application of water or steam sprays of sufficient temperature, pressure, residence time, agitation, surfactants, and detergents to remove hazardous contaminants from debris surfaces or to remove contaminated debris surface layers

Same as above

Same as above.

2. Chemical Extraction

a. Water Washing and Spraying: Application of water sprays or water baths of sufficient temperature, pressure, residence time, agitation, surfactants, acids, bases, and detergents to remove hazardous contaminants from debris surfaces and surface pores or to remove contaminated debris surface layers

All Debris: Treatment to a clean debris surface 3 ; Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm ( 1 ⁄ 2 inch) in one dimension ( i.e. , thickness limit, 5 except that this thickness limit may be waived under an “Equivalent Technology” approval under § 268.42(b); 8 debris surfaces must be in contact with water solution for at least 15 minutes

Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Contaminant must be soluble to at least 5% by weight in water solution or 5% by weight in emulsion; if debris is contaminated with a dioxin-listed waste, 6 an “Equivalent Technology” approval under § 268.42(b) must be obtained. 8

b. Liquid Phase Solvent Extraction: Removal of hazardous contaminants from debris surfaces and surface pores by applying a nonaqueous liquid or liquid solution which causes the hazardous contaminants to enter the liquid phase and be flushed away from the debris along with the liquid or liquid solution while using appropriate agitation, temperature, and residence time. 4

Same as above

Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Same as above, except that contaminant must be soluble to at least 5% by weight in the solvent.

c. Vapor Phase Solvent Extraction: Application of an organic vapor using sufficient agitation, residence time, and temperature to cause hazardous contaminants on contaminated debris surfaces and surface pores to enter the vapor phase and be flushed away with the organic vapor. 4

Same as above, except that brick, cloth, concrete, paper, pavement, rock and wood surfaces must be in contact with the organic vapor for at least 60 minutes

Same as above.

3. Thermal Extraction

a. High Temperature Metals Recovery: Application of sufficient heat, residence time, mixing, fluxing agents, and/or carbon in a smelting, melting, or refining furnace to separate metals from debris

For refining furnaces, treated debris must be separated from treatment residuals using simple physical or mechanical means, 9 and, prior to further treatment, such residuals must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris

Debris contaminated with a dioxin-listed waste: 5 Obtain an “Equivalent Technology” approval under § 268.42(b). 8

b. Thermal Desorption: Heating in an enclosed chamber under either oxidizing or nonoxidizing atmospheres at sufficient temperature and residence time to vaporize hazardous contaminants from contaminated surfaces and surface pores and to remove the contaminants from the heating chamber in a gaseous exhaust gas. 7

All Debris: Obtain an “Equivalent Technology” approval under § 268.42(b); 8 treated debris must be separated from treatment residuals using simple physical or mechanical means, 9 and, prior to further treatment, such residue must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 10 cm (4 inches) in one dimension ( i.e. , thickness limit), 5 except that this thickness limit may be waived under the “Equivalent Technology” approval

All Debris: Metals other than mercury.

B. Destruction Technologies:

1. Biological Destruction (Biodegradation): Removal of hazardous contaminants from debris surfaces and surface pores in an aqueous solution and biodegradation of organic or nonmetallic inorganic compounds ( i.e. , inorganics that contain phosphorus, nitrogen, or sulfur) in units operated under either aerobic or anaerobic conditions

All Debris: Obtain an “Equivalent Technology” approval under § 268.42(b); 8 treated debris must be separated from treatment residuals using simple physical or mechanical means, 9 and, prior to further treatment, such residue must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm ( 1 ⁄ 2 inch) in one dimension ( i.e. , thickness limit), 5 except that this thickness limit may be waived under the “Equivalent Technology” approval

All Debris: Metal contaminants.

2. Chemical Destruction

a. Chemical Oxidation: Chemical or electrolytic oxidation utilizing the following oxidation reagents (or waste reagents) or combination of reagents—(1) hypochlorite (e.g., bleach); (2) chlorine; (3) chlorine dioxide; (4) ozone or UV (ultraviolet light) assisted ozone; (5) peroxides; (6) persulfates; (7) perchlorates; (8) permanganates; and/or (9) other oxidizing reagents of equivalent destruction efficiency. 4 Chemical oxidation specifically includes what is referred to as alkaline chlorination

All Debris: Obtain an “Equivalent Technology” approval under § 268.42(b); 8 treated debris must be separated from treatment residuals using simple physical or mechanical means, 9 and, prior to further treatment, such residue must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm ( 1 ⁄ 2 inch) in one dimension ( i.e. , thickness limit), 5 except that this thickness limit may be waived under the “Equivalent Technology” approval

All Debris: Metal contaminants.

b. Chemical Reduction: Chemical reaction utilizing the following reducing reagents (or waste reagents) or combination of reagents: (1) sulfur dioxide; (2) sodium, potassium, or alkali salts of sulfites, bisulfites, and metabisulfites, and polyethylene glycols (e.g., NaPEG and KPEG); (3) sodium hydrosulfide; (4) ferrous salts; and/or (5) other reducing reagents of equivalent efficiency. 4

Same as above

Same as above.

3. Thermal Destruction: Treatment in an incinerator operating in accordance with Subpart O of Parts 264 or 265 of this chapter; a boiler or industrial furnace operating in accordance with Subpart H of Part 266 of this chapter, or other thermal treatment unit operated in accordance with Subpart X, Part 264 of this chapter, or Subpart P, Part 265 of this chapter, but excluding for purposes of these debris treatment standards Thermal Desorption units

Treated debris must be separated from treatment residuals using simple physical or mechanical means, 9 and, prior to further treatment, such residue must meet the waste-specific treatment standards for organic compounds in the waste contaminating the debris

Brick, Concrete, Glass, Metal, Pavement, Rock, Metal: Metals other than mercury, except that there are no metal restrictions for vitrification. Debris contaminated with a dioxin-listed waste. 6 Obtain an “Equivalent Technology” approval under § 268.42(b), 8 except that this requirement does not apply to vitrification.

C. Immobilization Technologies:

1. Macroencapsulation: Application of surface coating materials such as polymeric organics (e.g., resins and plastics) or use of a jacket of inert inorganic materials to substantially reduce surface exposure to potential leaching media

Encapsulating material must completely encapsulate debris and be resistant to degradation by the debris and its contaminants and materials into which it may come into contact after placement (leachate, other waste, microbes)

None.

2. Microencapsulation: Stabilization of the debris with the following reagents (or waste reagents) such that the leachability of the hazardous contaminants is reduced: (1) Portland cement; or (2) lime/pozzolans (e.g., fly ash and cement kiln dust). Reagents (e.g., iron salts, silicates, and clays) may be added to enhance the set/cure time and/or compressive strength, or to reduce the leachability of the hazardous constituents. 5

Leachability of the hazardous contaminants must be reduced

None.

3. Sealing: Application of an appropriate material which adheres tightly to the debris surface to avoid exposure of the surface to potential leaching media. When necessary to effectively seal the surface, sealing entails pretreatment of the debris surface to remove foreign matter and to clean and roughen the surface. Sealing materials include epoxy, silicone, and urethane compounds, but paint may not be used as a sealant

Sealing must avoid exposure of the debris surface to potential leaching media and sealant must be resistent to degradation by the debris and its contaminants and materials into which it may come into contact after placement (leachate, other waste, microbes)

None.

1 Hazardous debris must be treated by either these standards or the waste-specific treatment standards for the waste contaminating the debris. The treatment standards must be met for each type of debris contained in a mixture of debris types, unless the debris is converted into treatment residue as a result of the treatment process. Debris treatment residuals are subject to the waste-specific treatment standards for the waste contaminating the debris.

2 Contaminant restriction means that the technology is not BDAT for that contaminant. If debris containing a restricted contaminant is treated by the technology, the contaminant must be subsequently treated by a technology for which it is not restricted in order to be land disposed (and excluded from Subtitle C regulation).

3 “Clean debris surface” means the surface, when viewed without magnification, shall be free of all visible contaminated soil and hazardous waste except that residual staining from soil and waste consisting of light shadows, slight streaks, or minor discolorations, and soil and waste in cracks, crevices, and pits may be present provided that such staining and waste and soil in cracks, crevices, and pits shall be limited to no more than 5% of each square inch of surface area.

4 Acids, solvents, and chemical reagents may react with some debris and contaminants to form hazardous compounds. For example, acid washing of cyanide-contaminated debris could result in the formation of hydrogen cyanide. Some acids may also react violently with some debris and contaminants, depending on the concentration of the acid and the type of debris and contaminants. Debris treaters should refer to the safety precautions specified in Material Safety Data Sheets for various acids to avoid applying an incompatible acid to a particular debris/contaminant combination. For example, concentrated sulfuric acid may react violently with certain organic compounds, such as acrylonitrile.

5 If reducing the particle size of debris to meet the treatment standards results in material that no longer meets the 60 mm minimum particle size limit for debris, such material is subject to the waste-specific treatment standards for the waste contaminating the material, unless the debris has been cleaned and separated from contaminated soil and waste prior to size reduction. At a minimum, simple physical or mechanical means must be used to provide such cleaning and separation of nondebris materials to ensure that the debris surface is free of caked soil, waste, or other nondebris material.

6 Dioxin-listed wastes are EPA Hazardous Waste numbers FO20, FO21, FO22, FO23, FO26, and FO27.

7 Thermal desorption is distinguished from Thermal Destruction in that the primary purpose of Thermal Desorption is to volatilize contaminants and to remove them from the treatment chamber for subsequent destruction or other treatment.

8 The demonstration “Equivalent Technology” under § 268.42(b) must document that the technology treats contaminants subject to treatment to a level equivalent to that required by the performance and design and operating standards for other technologies in this table such that residual levels of hazardous contaminants will not pose a hazard to human health and the environment absent management controls.

9 Any soil, waste, and other nondebris material that remains on the debris surface (or remains mixed with the debris) after treatment is considered a treatment residual that must be separated from the debris using, at a minimum, simple physical or mechanical means. Examples of simple physical or mechanical means are vibratory or trommel screening or water washing. The debris surface need not be cleaned to a “clean debris surface” as defined in note 3 when separating treated debris from residue; rather, the surface must be free of caked soil, waste, or other nondebris material. Treatment residuals are subject to the waste-specific treatment standards for the waste contaminating the debris.

§ 268.46 Alternative treatment standards based on HTMR.

For the treatment standards previously found in this section, refer to § 268.40.

§ 268.48 Universal treatment standards.

(a) Table UTS identifies the hazardous constituents, along with the nonwastewater and wastewater treatment standard levels, that are used to regulate most prohibited hazardous wastes with numerical limits. For determining compliance with treatment standards for underlying hazardous constituents as defined in § 268.2(i), these treatment standards may not be exceeded. Compliance with these treatment standards is measured by an analysis of grab samples, unless otherwise noted in the following Table UTS.

Universal Treatment Standards

[Note: NA means not applicable]

Regulated constituent common name

CAS 1 number

Wastewater standard

Nonwastewater standard

Concentration 2 in mg/l

Concentration 3 in mg/kg unless noted as “mg/l TCLP”

Organic Constituents

Acenaphthylene

208-96-8

0.059

3.4

Acenaphthene

83-32-9

0.059

3.4

Acetone

67-64-1

0.28

160

Acetonitrile

75-05-8

5.6

38

Acetophenone

96-86-2

0.010

9.7

2-Acetylaminofluorene

53-96-3

0.059

140

Acrolein

107-02-8

0.29

NA

Acrylamide

79-06-1

19

23

Acrylonitrile

107-13-1

0.24

84

Aldrin

309-00-2

0.021

0.066

4-Aminobiphenyl

92-67-1

0.13

NA

Aniline

62-53-3

0.81

14

o-Anisidine (2-methoxyaniline)

90-04-0

0.010

0.66

Anthracene

120-12-7

0.059

3.4

Aramite

140-57-8

0.36

NA

alpha-BHC

319-84-6

0.00014

0.066

beta-BHC

319-85-7

0.00014

0.066

delta-BHC

319-86-8

0.023

0.066

gamma-BHC

58-89-9

0.0017

0.066

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzal chloride

98-87-3

0.055

6.0

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Benzo(g,h,i)perylene

191-24-2

0.0055

1.8

Benzo(a)pyrene

50-32-8

0.061

3.4

Bromodichloromethane

75-27-4

0.35

15

Bromomethane/Methyl bromide

74-83-9

0.11

15

4-Bromophenyl phenyl ether

101-55-3

0.055

15

n-Butyl alcohol

71-36-3

5.6

2.6

Butyl benzyl phthalate

85-68-7

0.017

28

2-sec-Butyl-4,6-dinitrophenol/Dinoseb

88-85-7

0.066

2.5

Carbon disulfide

75-15-0

3.8

4.8 mg/l TCLP

Carbon tetrachloride

56-23-5

0.057

6.0

Chlordane (alpha and gamma isomers)

57-74-9

0.0033

0.26

p-Chloroaniline

106-47-8

0.46

16

Chlorobenzene

108-90-7

0.057

6.0

Chlorobenzilate

510-15-6

0.10

NA

2-Chloro-1,3-butadiene

126-99-8

0.057

0.28

Chlorodibromomethane

124-48-1

0.057

15

Chloroethane

75-00-3

0.27

6.0

bis(2-Chloroethoxy)methane

111-91-1

0.036

7.2

bis(2-Chloroethyl)ether

111-44-4

0.033

6.0

Chloroform

67-66-3

0.046

6.0

bis(2-Chloroisopropyl)ether

39638-32-9

0.055

7.2

p-Chloro-m-cresol

59-50-7

0.018

14

2-Chloroethyl vinyl ether

110-75-8

0.062

NA

Chloromethane/Methyl chloride

74-87-3

0.19

30

2-Chloronaphthalene

91-58-7

0.055

5.6

2-Chloropchenol

95-57-8

0.044

5.7

3-Chloropropylene

107-05-1

0.036

30

Chrysene

218-01-9

0.059

3.4

p-Cresidine

120-71-8

0.010

0.66

o-Cresol

95-48-7

0.11

5.6

m-Cresol (difficult to distinguish from p-cresol)

108-39-4

0.77

5.6

p-Cresol (difficult to distinguish from m-cresol)

106-44-5

0.77

5.6

Cyclohexanone

108-94-1

0.36

0.75 mg/l TCLP

o,p′-DDD

53-19-0

0.023

0.087

p,p′-DDD

72-54-8

0.023

0.087

o,p′-DDE

3424-82-6

0.031

0.087

p,p′-DDE

72-55-9

0.031

0.087

o,p′-DDT

789-02-6

0.0039

0.087

p,p′-DDT

50-29-3

0.0039

0.087

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Dibenz(a,e)pyrene

192-65-4

0.061

NA

1,2-Dibromo-3-chloropropane

96-12-8

0.11

15

1,2-Dibromoethane/Ethylene dibromide

106-93-4

0.028

15

Dibromomethane

74-95-3

0.11

15

m-Dichlorobenzene

541-73-1

0.036

6.0

o-Dichlorobenzene

95-50-1

0.088

6.0

p-Dichlorobenzene

106-46-7

0.090

6.0

Dichlorodifluoromethane

75-71-8

0.23

7.2

1,1-Dichloroethane

75-34-3

0.059

6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

1,1-Dichloroethylene

75-35-4

0.025

6.0

trans-1,2-Dichloroethylene

156-60-5

0.054

30

2,4-Dichlorophenol

120-83-2

0.044

14

2,6-Dichlorophenol

87-65-0

0.044

14

2,4-Dichlorophenoxyacetic acid/2,4-D

94-75-7

0.72

10

1,2-Dichloropropane

78-87-5

0.85

18

cis-1,3-Dichloropropylene

10061-01-5

0.036

18

trans-1,3-Dichloropropylene

10061-02-6

0.036

18

Dieldrin

60-57-1

0.017

0.13

Diethyl phthalate

84-66-2

0.20

28

p-Dimethylaminoazobenzene

60-11-7

0.13

NA

2,4-Dimethylaniline (2,4-xylidine)

95-68-1

0.010

0.66

2,4-Dimethyl phenol

105-67-9

0.036

14

Dimethyl phthalate

131-11-3

0.047

28

Di-n-butyl phthalate

84-74-2

0.057

28

1,4-Dinitrobenzene

100-25-4

0.32

2.3

4,6-Dinitro-o-cresol

534-52-1

0.28

160

2,4-Dinitrophenol

51-28-5

0.12

160

2,4-Dinitrotoluene

121-14-2

0.32

140

2,6-Dinitrotoluene

606-20-2

0.55

28

Di-n-octyl phthalate

117-84-0

0.017

28

Di-n-propylnitrosamine

621-64-7

0.40

14

1,4-Dioxane

123-91-1

12.0

170

Diphenylamine (difficult to distinguish from diphenylnitrosamine)

122-39-4

0.92

13

Diphenylnitrosamine (difficult to distinguish from diphenylamine)

86-30-6

0.92

13

1,2-Diphenylhydrazine

122-66-7

0.087

NA

Disulfoton

298-04-4

0.017

6.2

Endosulfan I

959-98-8

0.023

0.066

Endosulfan II

33213-65-9

0.029

0.13

Endosulfan sulfate

1031-07-8

0.029

0.13

Endrin

72-20-8

0.0028

0.13

Endrin aldehyde

7421-93-4

0.025

0.13

Ethyl acetate

141-78-6

0.34

33

Ethyl benzene

100-41-4

0.057

10

Ethyl cyanide/Propanenitrile

107-12-0

0.24

360

Ethyl ether

60-29-7

0.12

160

bis(2-Ethylhexyl)phthalate

117-81-7

0.28

28

Ethyl methacrylate

97-63-2

0.14

160

Ethylene oxide

75-21-8

0.12

NA

Famphur

52-85-7

0.017

15

Fluoranthene

206-44-0

0.068

3.4

Fluorene

86-73-7

0.059

3.4

Heptachlor

76-44-8

0.0012

0.066

1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD)

35822-46-9

0.000035

.0025

1,2,3,4,6,7,8-Heptachlorodibenzofluran (1,2,3,4,6,7,8-HpCDF)

67562-39-4

0.000035

.0025

1,2,3,4,7,8,9-Heptachlorodibenzofluran (1,2,3,4,7,8,9-HpCDF)

55673-89-7

0.000035

.0025

Heptachlor epoxide

1024-57-3

0.016

0.066

Hexachlorobenzene

118-74-1

0.055

10

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

Hexachloroethane

67-72-1

0.055

30

Hexachloropropylene

1888-71-7

0.035

30

Indeno(1,2,3-c,d) pyrene

193-39-5

0.0055

3.4

Iodomethane

74-88-4

0.19

65

Isobutyl alcohol

78-83-1

5.6

170

Isodrin

465-73-6

0.021

0.066

Isosafrole

120-58-1

0.081

2.6

Kepone

143-50-0

0.0011

0.13

Methacrylonitrile

126-98-7

0.24

84

Methanol

67-56-1

5.6

0.75 mg/l TCLP

Methapyrilene

91-80-5

0.081

1.5

Methoxychlor

72-43-5

0.25

0.18

3-Methylcholanthrene

56-49-5

0.0055

15

4,4-Methylene bis(2-chloroaniline)

101-14-4

0.50

30

Methylene chloride

75-09-2

0.089

30

Methyl ethyl ketone

78-93-3

0.28

36

Methyl isobutyl ketone

108-10-1

0.14

33

Methyl methacrylate

80-62-6

0.14

160

Methyl methanesulfonate

66-27-3

0.018

NA

Methyl parathion

298-00-0

0.014

4.6

Naphthalene

91-20-3

0.059

5.6

2-Naphthylamine

91-59-8

0.52

NA

o-Nitroaniline

88-74-4

0.27

14

p-Nitroaniline

100-01-6

0.028

28

Nitrobenzene

98-95-3

0.068

14

5-Nitro-o-toluidine

99-55-8

0.32

28

o-Nitrophenol

88-75-5

0.028

13

p-Nitrophenol

100-02-7

0.12

29

N-Nitrosodiethylamine

55-18-5

0.40

28

N-Nitrosodimethylamine

62-75-9

0.40

2.3

N-Nitroso-di-n-butylamine

924-16-3

0.40

17

N-Nitrosomethylethylamine

10595-95-6

0.40

2.3

N-Nitrosomorpholine

59-89-2

0.40

2.3

N-Nitrosopiperidine

100-75-4

0.013

35

N-Nitrosopyrrolidine

930-55-2

0.013

35

1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (OCDD)

3268-87-9

0.000063

0.005

1,2,3,4,6,7,8,9-Octachlorodibenzofluran (OCDF)

39001-02-0

0.000063

0.005

Parathion

56-38-2

0.014

4.6

Total PCBs (sum of all PCB isomers, or all Aroclors) 8

1336-36-3

0.10

10

Pentachlorobenzene

608-93-5

0.055

10

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

Pentachloroethane

76-01-7

0.055

6.0

Pentachloronitrobenzene

82-68-8

0.055

4.8

Pentachlorophenol

87-86-5

0.089

7.4

Phenacetin

62-44-2

0.081

16

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

1,3-Phenylenediamine

108-45-2

0.010

0.66

Phorate

298-02-2

0.021

4.6

Phthalic acid

100-21-0

0.055

28

Phthalic anhydride

85-44-9

0.055

28

Pronamide

23950-58-5

0.093

1.5

Pyrene

129-00-0

0.067

8.2

Pyridine

110-86-1

0.014

16

Safrole

94-59-7

0.081

22

Silvex/2,4,5-TP

93-72-1

0.72

7.9

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

1,1,2,2-Tetrachloroethane

79-34-5

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

2,3,4,6-Tetrachlorophenol

58-90-2

0.030

7.4

Toluene

108-88-3

0.080

10

Toxaphene

8001-35-2

0.0095

2.6

Tribromomethane/Bromoform

75-25-2

0.63

15

1,2,4-Trichlorobenzene

120-82-1

0.055

19

1,1,1-Trichloroethane

71-55-6

0.054

6.0

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

Trichlorofluoromethane

75-69-4

0.020

30

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

2,4,5-Trichlorophenoxyacetic acid/2,4,5-T

93-76-5

0.72

7.9

1,2,3-Trichloropropane

96-18-4

0.85

30

1,1,2-Trichloro-1,2,2-trifluoroethane

76-13-1

0.057

30

tris-(2,3-Dibromopropyl) phosphate

126-72-7

0.11

0.10

Vinyl chloride

75-01-4

0.27

6.0

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Inorganic Constituents

Antimony

7440-36-0

1.9

1.15 mg/l TCLP

Arsenic

7440-38-2

1.4

5.0 mg/l TCLP

Barium

7440-39-3

1.2

21 mg/l TCLP

Beryllium

7440-41-7

0.82

1.22 mg/l TCLP

Cadmium

7440-43-9

0.69

0.11 mg/l TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/l TCLP

Cyanides (Total) 4

57-12-5

1.2

590

Cyanides (Amenable) 4

57-12-5

0.86

30

Fluoride 5

16984-48-8

35

NA

Lead

7439-92-1

0.69

0.75 mg/l TCLP

Mercury—Nonwastewater from Retort

7439-97-6

NA

0.20 mg/l TCLP

Mercury—All Others

7439-97-6

0.15

0.025 mg/l TCLP

Nickel

7440-02-0

3.98

11 mg/l TCLP

Selenium 7

7782-49-2

0.82

5.7 mg/l TCLP

Silver

7440-22-4

0.43

0.14 mg/l TCLP

Sulfide 5

18496-25-8

14

NA

Thallium

7440-28-0

1.4

0.20 mg/l TCLP

Vanadium 5

7440-62-2

4.3

1.6 mg/l TCLP

Zinc 5

7440-66-6

2.61

4.3 mg/l TCLP

Footnotes to Table UTS

1

CAS means Chemical Abstract Services. When the waste code 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.

2

Concentration standards for wastewaters are expressed in mg/l and are based on analysis of composite samples.

3

Except for Metals (EP or TCLP) and Cyanides (Total and Amenable) the nonwastewater treatment standards expressed as a concentration were established, inpart, based upon incineration in units operated in accordance with the technical requirements of 40 CFR part 264, subpart O or 40 CFR part 265, subpart O, 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 40 CFR 268.40(d). All concentration standards for nonwastewaters are based on analysis of grab samples.

4

Both Cyanides (Total) and Cyanides (Amenable) for nonwastewaters are to be analyzed using Method 9010C or 9012B, found in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” EPA Publication SW-846, as incorporated by reference in 40 CFR 260.11, with a sample size of 10 grams and a distillation time of one hour and 15 minutes.

5

These constituents are not “underlying hazardous constituents” in characteristic wastes, according to the definition at § 268.2(i).

6

[Reserved]

7

This constituent is not an underlying hazardous constituent as defined at § 268.2(i) of this Part because its UTS level is greater than its TC level, thus a treatment selenium waste would always be characteristically hazardous, unless it is treated to below its characteristic level.

8

This standard is temporarily deferred for soil exhibiting a hazardous characteristic due to D004-D011 only.

§ 268.49 Alternative LDR treatment standards for contaminated soil.

(a) Applicability. You must comply with LDRs prior to placing soil that exhibits a characteristic of hazardous waste, or exhibited a characteristic of hazardous waste at the time it was generated, into a land disposal unit. The following chart describes whether you must comply with LDRs prior to placing soil contaminated by listed hazardous waste into a land disposal unit:

If LDRs

And if LDRs

And if

Then you

Applied to the listed waste when it contaminated the soil*

Apply to the listed waste now

Must comply with LDRs

Didn't apply to the listed waste when it contaminated the soil*

Apply to the listed waste now

The soil is determined to contain the listed waste when the soil is first generated

Must comply with LDRs.

Didn't apply to the listed waste when it contaminated the soil*

Apply to the listed waste now

The soil is determined not to contain the listed waste when the soil is first generated

Needn't comply with LDRs.

Didn't apply to the listed waste when it contaminated the soil*

Don't apply to the listed waste now

Needn't comply with LDRs.

* For dates of LDR applicability, see 40 CFR Part 268 Appendix VII. To determine the date any given listed hazardous waste contaminated any given volume of soil, use the last date any given listed hazardous waste was placed into any given land disposal unit or, in the case of an accidental spill, the date of the spill.

(b) Prior to land disposal, contaminated soil identified by paragraph (a) of this section as needing to comply with LDRs must be treated according to the applicable treatment standards specified in paragraph (c) of this section or according to the Universal Treatment Standards specified in 40 CFR 268.48 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 section and the Universal Treatment Standards may be modified through a treatment variance approved in accordance with 40 CFR 268.44.

(c) Treatment standards for contaminated soils. Prior to land disposal, contaminated soil identified by paragraph (a) of this section as needing to comply with LDRs must be treated according to all the standards specified in this paragraph or according to the Universal Treatment Standards specified in 40 CFR 268.48.

(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 90 percent reduction in total constituent concentrations, except as provided by paragraph (c)(1)(C) of this section.

(B) For metals and carbon disulfide, cyclohexanone, and methanol, treatment must achieve 90 percent reduction in constituent concentrations as measured in leachate from the treated media (tested according to the TCLP) or 90 percent reduction in total constituent concentrations (when a metal removal treatment technology is used), except as provided by paragraph (c)(1)(C)of this section.

(C) When treatment of any constituent subject to treatment to a 90 percent reduction standard would result in a concentration less than 10 times the Universal Treatment Standard for that constituent, treatment to achieve constituent concentrations less than 10 times the universal treatment standard is not required. Universal Treatment Standards are identified in 40 CFR 268.48 Table UTS.

(2) Soils that exhibit the characteristic of ignitability, corrosivity or reactivity. In addition to the treatment required by paragraph (c)(1) of this section, 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 (2) of this section, 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 (2) of this section; or,

(B) For soil that contains only nonanalyzable constituents, treatment by the method(s) specified in § 268.42 for the waste contained in the soil.

(d) Constituents subject to treatment. When applying the soil treatment standards in paragraph (c) of this section, constituents subject to treatment are any constituents listed in § 268.48 Table UTS-Universal Treatment Standards that are reasonably expected to be present in any given volume of contaminated soil, except fluoride, selenium, sulfides, vanadium, zinc, and that are present at concentrations greater than ten times the universal treatment standard. 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 section as needing to comply with LDRs must be managed as follows:

(1) Soil residuals are subject to the treatment standards of this section;

(2) Non-soil residuals are subject to:

(A) For soils contaminated by listed hazardous waste, the RCRA Subtitle C standards 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.

§ 268.50 Prohibitions on storage of restricted wastes.

(a) Except as provided in this section, the storage of hazardous wastes restricted from land disposal under subpart C of this part of RCRA section 3004 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 §§ 262.16 and 262.17 and parts 264 and 265 of this chapter.

(2) An owner/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:

(i) Each container is clearly marked to identify its contents and with:

(A) The words “Hazardous Waste”;

(B) The applicable EPA hazardous waste number(s) (EPA hazardous waste codes) in subparts C and D of part 261 of this chapter; or use a nationally recognized electronic system, such as bar coding, to identify the EPA hazardous waste number(s);

(C) An indication of the hazards of the contents (examples include, but are not limited to, the applicable hazardous waste characteristic(s) ( i.e., ignitable, corrosive, reactive, toxic); hazard communication consistent with the Department of Transportation requirements at 49 CFR part 172 subpart E (labeling) or subpart F (placarding); a hazard statement or pictogram consistent with the Occupational Safety and Health Administration Hazard Communication Standard at 29 CFR 1910.1200; or a chemical hazard label consistent with the National Fire Protection Association code 704); and

(D) The date each period of accumulation begins.

(ii) 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/operator must comply with the operating record requirements specified in § 264.73 or § 265.73.

(3) A transporter stores manifested shipments of such wastes at a transfer facility for 10 days or less.

(4) A healthcare facility accumulates such wastes in containers on site solely for the purpose of the accumulation of such quantities of hazardous waste pharmaceuticals as necessary to facilitate proper recovery, treatment, or disposal and the healthcare facility complies with the applicable requirements in §§ 266.502 and 266.503 of this chapter.

(5) A reverse distributor accumulates such wastes in containers on site solely for the purpose of the accumulation of such quantities of hazardous waste pharmaceuticals as necessary to facilitate proper recovery, treatment, or disposal and the reverse distributor complies with § 266.510 of this chapter.

(b) An owner/operator of a treatment, storage or disposal facility may store such wastes for up to one year unless the Agency 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/operator of a treatment, storage or disposal facility may store such wastes beyond one year; however, the owner/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 § 268.5, an approved § 268.6 petition, or a national capacity variance under subpart C), the prohibition in paragraph (a) of this section does not apply during the period of such exemption.

(e) The prohibition in paragraph (a) of this section does not apply to hazardous wastes that meet the treatment standards specified under §§ 268.41, 268.42, and 268.43 or the treatment standards specified under the variance in § 268.44, or, where treatment standards have not been specified, is in compliance with the applicable prohibitions specified in § 268.32 or RCRA section 3004.

(f) Liquid hazardous wastes containing polychlorinated biphenyls (PCBs) at concentrations greater than or equal to 50 ppm 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 this part within one year of the date when such wastes are first placed into storage. The provisions of paragraph (c) of this section do not apply to such PCB wastes prohibited under § 268.32 of this part.

(g) The prohibition and requirements in this section do not apply to hazardous remediation wastes stored in a staging pile approved pursuant to § 264.554 of this chapter.

Appendix III Appendix III to Part 268—List of Halogenated Organic Compounds Regulated Under § 268.32

In determining the concentration of HOCs in a hazardous waste for purposes of the § 268.32 land disposal prohibition, EPA has defined the HOCs that must be included in a calculation as any compounds having a carbon-halogen bond which are listed in this Appendix (see § 268.2). Appendix III to Part 268 consists of the following compounds:

I. Volatiles

1. Bromodichloromethane

2. Bromomethane

3. Carbon Tetrachloride

4. Chlorobenzene

5. 2-Chloro-1,3-butadiene

6. Chlorodibromomethane

7. Chloroethane

8. 2-Chloroethyl vinyl ether

9. Chloroform

10. Chloromethane

11. 3-Chloropropene

12. 1,2-Dibromo-3-chloropropane

13. 1,2-Dibromomethane

14. Dibromomethane

15. Trans-1,4-Dichloro-2—butene

16. Dichlorodifluoromethane

17. 1,1-Dichloroethane

18. 1,2-Dichloroethane

19. 1,1-Dichloroethylene

20. Trans-1,2-Dichloroethene

21. 1,2-Dichloropropane

22. Trans-1,3-Dichloropropene

23. cis-1,3-Dichloropropene

24. Iodomethane

25. Methylene chloride

26. 1,1,1,2-Tetrachloroethane

27. 1,1,2,2-Tetrachloroethane

28. Tetrachloroethene

29. Tribromomethane

30. 1,1,1-Trichloroethane

31. 1,1,2-Trichloroethane

32. Trichlorothene

33. Trichloromonofluoromethane

34. 1,2,3-Thrichloropropane

35. Vinyl Chloride

II. Semivolatiles

1. Bis(2-chloroethoxy)ethane

2. Bis(2-chloroethyl)ether

3. Bis(2-chloroisopropyl)ether

4. p-Chloroaniline

5. Chlorobenzilate

6. p-Chloro-m-cresol

7. 2-Chloronaphthalene

8. 2-Chlorphenol

9. 3-Chloropropionitrile

10. m-Dichlorobenzene

11. o-Dichlorobenzene

12. p-Dichlorobenzene

13. 3.3′-Dichlorobenzidine

14. 2,4-Dichlorophenol

15. 2,6-Dichlorophenol

16. Hexachlorobenzene

17. Hexachlorobutadiene

18. Hexachlorocyclopentadiene

19. Hexachloroethane

20. Hexachloroprophene

21. Hexachlorpropene

22. 4,4′-Methylenebis(2-chloroanaline)

23. Pentachlorobenzene

24. Pentachloroethane

25. Pentachloronitrobenzene

26. Pentachlorophenol

27. Pronamide

28. 1,2,4,5-Tetrachlorobenzene

29. 2,3,4,6-Tetrachlorophenol

30. 1,2,4-Trichlorobenzene

31. 2,4,5-Trichlorophenol

32. 2,4,6-Trichlorophenol

33. Tris(2,3-dibromopropyl)phosphate

III. Organochlorine Pesticides

1. Aldrin

2. alpha-BHC

3. beta-BHC

4. delta-BHC

5. gamma-BHC

6. Chlorodane

7. DDD

8. DDE

9. DDT

10. Dieldrin

11. Endosulfan I

12. Endosulfan II

13. Endrin

14. Endrin aldehyde

15. Heptachlor

16. Heptachlor epoxide

17. Isodrin

18. Kepone

19. Methoxyclor

20. Toxaphene

IV. Phenoxyacetic Acid Herbicides

1. 2,4-Dichlorophenoxyacetic acid

2. Silvex

3. 2,4,5-T

V. PCBs

1. Aroclor 1016

2. Aroclor 1221

3. Aroclor 1232

4. Aroclor 1242

5. Aroclor 1248

6. Aroclor 1254

7. Aroclor 1260

8. PCBs not otherwise specified

VI. Dioxins and Furans

1. Hexachlorodibenzo-p-dioxins

2. Hexachlorodibenzofuran

3. Pentachlorodibenzo-p-dioxins

4. Pentachlorodibenzofuran

5. Tetrachlorodibenzo-p-dioxins

6. Tetrachlorodibenzofuran

7. 2,3,7,8-Tetrachlorodibenzo-p-dioxin

Appendix IV Appendix IV to Part 268—Wastes Excluded From Lab Packs Under the Alternative Treatment Standards of § 268.42( c )

Hazardous waste with the following EPA Hazardous Waste Codes may not be placed in lab packs under the alternative lab pack treatment standards of § 268.42(c): D009, F019, K003, K004, K005, K006, K062, K071, K100, K106, P010, P011, P012, P076, P078, U134, U151.

Appendix VI Appendix VI to Part 268—Recommended Technologies To Achieve Deactivation of Characteristics in Section 268.42

The treatment standard for many characteristic wastes is stated in the § 268.40 Table of Treatment Standards as “Deactivation and meet UTS.” EPA has determined that many technologies, when used alone or in combination, can achieve the deactivation portion of the treatment standard. Characteristic wastes that are not managed in a facility regulated by the Clean Water Act (CWA) or in a CWA-equivalent facility, and that also contain underlying hazardous constituents (see § 268.2(i)) must be treated not only by a “deactivating” technology to remove the characteristic, but also to achieve the universal treatment standards (UTS) for underlying hazardous constituents. The following appendix presents a partial list of technologies, utilizing the five letter technology codes established in 40 CFR 268.42 Table 1, that may be useful in meeting the treatment standard. Use of these specific technologies is not mandatory and does not preclude direct reuse, recovery, and/or the use of other pretreatment technologies, provided deactivation is achieved and underlying hazardous constituents are treated to achieve the UTS.

Waste code/subcategory

Nonwastewaters

Wastewaters

D001 Ignitable Liquids based on 261.21(a)(1)—Low TOC Nonwastewater Subcategory (containing 1% to <10% TOC)

RORGS INCIN WETOX CHOXD BIODG

n.a.

D001 Ignitable Liquids based on 261.21(a)(1)—Ignitable Wastewater Subcategory (containing <1% TOC)

n.a.

RORGS INCIN WETOX CHOXD BIODG

D001 Compressed Gases based on 261.21(A)(3)

RCGAS INCIN FSUBS ADGAS fb. INCIN ADGAS fb. (CHOXD; or CHRED)

n.a.

D001 Ignitable Reactives based on 261.21(a)(2)

WTRRX CHOXD CHRED STABL INCIN

n.a.

D001 Ignitable Oxidizers based on 261.21(a)(4)

CHRED INCIN

CHRED INCIN

D002 Acid Subcategory based on 261.22(a)(1) with pH less than or equal to 2

RCORR NEUTR INCIN

NEUTR INCIN

D002 Alkaline Subcategory based on 261.22(a)(1) with pH greater than or equal to 12.5

NEUTR INCIN

NEUTR INCIN

D002 Other Corrosives based on 261.22(a)(2)

CHOXD CHRED INCIN STABL

CHOXD CHRED INCIN

D003 Water Reactives based on 261.23(a) (2), (3), and (4)

INCIN WTRRX CHOXD CHRED

n.a.

D003 Reactive Sulfides based on 261.23(a)(5)

CHOXD CHRED INCIN STABL

CHOXD CHRED BIODG INCIN

D003 Explosives based on 261.23(a) (6), (7), and (8)

INCIN CHOXD CHRED

INCIN CHOXD CHRED BIODG CARBN

D003 Other Reactives based on 261.23(a)(1)

INCIN CHOXD CHRED

INCIN CHOXD CHRED BIODG CARBN

K044 Wastewater treatment sludges from the manufacturing and processing of explosives

CHOXD CHRED INCIN

CHOXD CHRED BIODG CARBN INCIN

K045 Spent carbon from the treatment of wastewaters containing explosives

CHOXD CHRED INCIN

CHOXD CHRED BIODG CARBN INCIN

K047 Pink/red water from TNT operations

CHOXD CHRED INCIN

CHOXD CHRED BIODG CARBN INCIN

Note: “n.a.” stands for “not applicable”; “fb.” stands for “followed by”.

Appendix VII Appendix VII to Part 268—LDR Effective Dates of Surface Disposed Prohibited Hazardous Wastes

Table 1—Effective Dates of Surface Disposed Wastes (Non-Soil and Debris) Regulated in the LDRS a —Comprehensive List

Waste code

Waste category

Effective date

D001 c

All (except High TOC Ignitable Liquids)

Aug. 9, 1993.

D001

High TOC Ignitable Liquids

Aug. 8, 1990.

D002 c

All

Aug. 9, 1993.

D003

Newly identified surface-disposed elemental phosphorus processing wastes

May 26, 2000.

D004

Newly identified D004 and mineral processing wastes

Aug. 24, 1998.

D004

Mixed radioactive/newly identified D004 or mineral processing wastes

May 26, 2000

D005

Newly identified D005 and mineral processing wastes

Aug. 24, 1998.

D005

Mixed radioactive/newly identified D005 or mineral processing wastes

May 26, 2000.

D006

Newly identified D006 and mineral processing wastes

Aug. 24, 1998.

D006

Mixed radioactive/newly identified D006 or mineral processing wastes

May 26, 2000.

D007

Newly identified D007 and mineral processing wastes

Aug. 24, 1998.

D007

Mixed radioactive/newly identified D007 or mineral processing wastes

May 26, 2000.

D008

Newly identified D008 and mineral processing waste

Aug. 24, 1998.

D008

Mixed radioactive/newly identified D008 or mineral processing wastes

May 26, 2000.

D009

Newly identified D009 and mineral processing waste

Aug. 24, 1998.

D009

Mixed radioactive/newly identified D009 or mineral processing wastes

May 26, 2000.

D010

Newly identified D010 and mineral processing wastes

Aug. 24, 1998.

D010

Mixed radioactive/newly identified D010 or mineral processing wastes

May 26, 2000.

D011

Newly identified D011 and mineral processing wastes

Aug. 24, 1998.

D011

Mixed radioactive/newly identified D011 or mineral processing wastes

May 26, 2000.

D012 (that exhibit the toxicity characteristic based on the TCLP) d

All

Dec. 14, 1994.

D013 (that exhibit the toxicity characteristic based on the TCLP) d

All

Dec. 14, 1994.

D014 (that exhibit the toxicity characteristic based on the TCLP) d

All

Dec. 14, 1994.

D015 (that exhibit the toxicity characteristic based on the TCLP) d

All

Dec. 14, 1994.

D016 (that exhibit the toxicity characteristic based on the TCLP) d

All

Dec. 14, 1994.

D017 (that exhibit the toxicity characteristic based on the TCLP) d

All

Dec. 14, 1994.

D018

Mixed with radioactive wastes

Sept. 19, 1996.

D018

All others

Dec. 19, 1994.

D019

Mixed with radioactive wastes

Sept. 19, 1996.

D019

All others

Dec. 19, 1994.

D020

Mixed with radioactive wastes

Sept. 19, 1996.

D020

All others

Dec. 19, 1994.

D021

Mixed with radioactive wastes

Sept. 19, 1996.

D021

All others

Dec. 19, 1994.

D022

Mixed with radioactive wastes

Sept. 19, 1996.

D022

All others

Dec. 19, 1994.

D023

Mixed with radioactive wastes

Sept. 19, 1996.

D023

All others

Dec. 19, 1994.

D024

Mixed with radioactive wastes

Sept. 19, 1996.

D024

All others

Dec. 19, 1994.

D025

Mixed with radioactive wastes

Sept. 19, 1996.

D025

All others

Dec. 19, 1994.

D026

Mixed with radioactive wastes

Sept. 19, 1996.

D026

All others

Dec. 19, 1994.

D027

Mixed with radioactive wastes

Sept. 19, 1996.

D027

All others

Dec. 19, 1994.

D028

Mixed with radioactive wastes

Sept. 19, 1996.

D028

All others

Dec. 19, 1994.

D029

Mixed with radioactive wastes

Sept. 19, 1996.

D029

All others

Dec. 19, 1994.

D030

Mixed with radioactive wastes

Sept. 19. 1996.

D030

All others

Dec. 19, 1994.

D031

Mixed with radioactive wastes

Sept. 19, 1996.

D031

All others

Dec. 19, 1994.

D032

Mixed with radioactive wastes

Sept. 19, 1996.

D032

All others

Dec. 19, 1994.

D033

Mixed with radioactive wastes

Sept. 19, 1996.

D033

All others

Dec. 19, 1994.

D034

Mixed with radioactive wastes

Sept. 19, 1996.

D034

All others

Dec. 19, 1994.

D035

Mixed with radioactive wastes

Sept. 19, 1996.

D035

All others

Dec. 19, 1994.

D036

Mixed with radioactive wastes

Sept. 19, 1996.

D036

All others

Dec. 19, 1994.

D037

Mixed with radioactive wastes

Sept. 19, 1996.

D037

All others

Dec. 19, 1994.

D038

Mixed with radioactive wastes

Sept. 19, 1996.

D038

All others

Dec. 19, 1994.

D039

Mixed with radioactive wastes

Sept. 19, 1996.

D039

All others

Dec. 19, 1994.

D040

Mixed with radioactive wastes

Sept. 19, 1996.

D040

All others

Dec. 19, 1994.

D041

Mixed with radioactive wastes

Sept. 19, 1996.

D041

All others

Dec. 19, 1994.

D042

Mixed with radioactive wastes

Sept. 19, 1996.

D042

All others

Dec. 19, 1994.

D043

Mixed with radioactive wastes

Sept. 19, 1996.

D043

All others

Dec. 19, 1994.

F001

Small quantity generators, CERCLA response/RCRA corrective action, initial generator's solvent-water mixtures, solvent-containing sludges and solids

Nov. 8, 1988.

F001

All others

Nov. 8, 1986.

F002 (1,1,2-trichloroethane)

Wastewater and Nonwastewater

Aug. 8, 1990.

F002

Small quantity generators, CERCLA response/RCRA corrective action, initial generator's solvent-water mixtures, solvent-containing sludges and solids

Nov. 8, 1988.

F002

All others

Nov. 8, 1986.

F003

Small quantity generators, CERCLA response/RCRA corrective action, initial generator's solvent-water mixtures, solvent-containing sludges and solids

Nov. 8, 1988.

F003

All others

Nov. 8, 1986.

F004

Small quantity generators, CERCLA response/RCRA corrective action, initial generator's solvent-water mixtures, solvent-containing sludges and solids

Nov. 8, 1988.

F004

All others

Nov. 8, 1986.

F005 (benzene, 2-ethoxy ethanol, 2-nitropropane)

Wastewater and Nonwastewater

Aug. 8, 1990.

F005

Small quantity generators, CERCLA response/RCRA corrective action, initial generator's solvent-water mixtures, solvent-containing sludges and solids

Nov. 8, 1988.

F005

All others

Nov. 8, 1986.

F006

Wastewater

Aug. 8, 1990.

F006

Nonwastewater

Aug. 8, 1988.

F006 (cyanides)

Nonwastewater

July 8, 1989.

F007

All

July 8, 1989.

F008

All

July 8, 1989.

F009

All

July 8, 1989.

F010

All

June 8, 1989.

F011 (cyanides)

Nonwastewater

Dec. 8, 1989.

F011

All others

July 8, 1989.

F012 (cyanides)

Nonwastewater

Dec. 8, 1989.

F012

All others

July 8, 1989.

F019

All

Aug. 8, 1990.

F020

All

Nov. 8, 1988.

F021

All

Nov. 8, 1988.

F025

All

Aug. 8, 1990.

F026

All

Nov. 8, 1988.

F027

All

Nov. 8, 1988.

F028

All

Nov. 8, 1988.

F032

Mixed with radioactive wastes

May 12, 1999

F032

All others

Aug. 12, 1997.

F034

Mixed with radioactive wastes

May 12, 1999

F034

All others

Aug. 12, 1997.

F035

Mixed with radioactive wastes

May 12, 1999.

F035

All others

Aug. 12, 1997.

F037

Not generated from surface impoundment cleanouts or closures

June 30, 1993.

F037

Generated from surface impoundment cleanouts or closures

June 30, 1994.

F037

Mixed with radioactive wastes

June 30, 1994.

F038

Not generated from surface impoundment cleanouts or closures

June 30, 1993.

F038

Generated from surface impoundment cleanouts or closures

June 30, 1994.

F038

Mixed with radioactive wastes

June 30, 1994.

F039

Wastewater

Aug. 8, 1990.

F039

Nonwastewater

May 8, 1992.

K001 (organics) b

All

Aug. 8, 1988.

K001

All others

Aug. 8, 1988.

K002

All

Aug. 8, 1990.

K003

All

Aug. 8, 1990.

K004

Wastewater

Aug. 8, 1990.

K004

Nonwastewater

Aug. 8, 1988.

K005

Wastewater

Aug. 8, 1990.

K005

Nonwastewater

June 8, 1989.

K006

All

Aug. 8, 1990.

K007

Wastewater

Aug. 8, 1990.

K007

Nonwastewater

June 8, 1989.

K008

Wastewater

Aug. 8, 1990.

K008

Nonwastewater

Aug. 8, 1988.

K009

All

June 8, 1989.

K010

All

June 8, 1989.

K011

Wastewater

Aug. 8, 1990.

K011

Nonwastewater

June 8, 1989.

K013

Wastewater

Aug. 8, 1990.

K013

Nonwastewater

June 8, 1989.

K014

Wastewater

Aug. 8, 1990.

K014

Nonwastewater

June 8, 1989.

K015

Wastewater

Aug. 8, 1988.

K015

Nonwastewater

Aug. 8, 1990.

K016

All

Aug. 8, 1988.

K017

All

Aug. 8, 1990.

K018

All

Aug. 8, 1988.

K019

All

Aug. 8, 1988.

K020

All

Aug. 8, 1988.

K021

Wastewater

Aug. 8, 1990.

K021

Nonwastewater

Aug. 8, 1988.

K022

Wastewater

Aug. 8, 1990.

K022

Nonwastewater

Aug. 8, 1988.

K023

All

June 8, 1989.

K024

All

Aug. 8, 1988.

K025

Wastewater

Aug. 8, 1990.

K025

Nonwastewater

Aug. 8, 1988.

K026

All

Aug. 8, 1990.

K027

All

June 8, 1989.

K028 (metals)

Nonwastewater

Aug. 8, 1990.

K028

All others

June 8, 1989.

K029

Wastewater

Aug. 8, 1990.

K029

Nonwastewater

June 8, 1989.

K030

All

Aug. 8, 1988.

K031

Wastewater

Aug. 8, 1990.

K031

Nonwastewater

May 8, 1992.

K032

All

Aug. 8, 1990.

K033

All

Aug. 8, 1990.

K034

All

Aug. 8, 1990.

K035

All

Aug. 8, 1990.

K036

Wastewater

June 8, 1989.

K036

Nonwastewater

Aug. 8, 1988.

K037 b

Wastewater

Aug. 8, 1988.

K037

Nonwastewater

Aug. 8, 1988.

K038

All

June 8, 1989.

K039

All

June 8, 1989.

K040

All

June 8, 1989.

K041

All

Aug. 8, 1990.

K042

All

Aug. 8, 1990.

K043

All

June 8, 1989.

K044

All

Aug. 8, 1988.

K045

All

Aug. 8, 1988.

K046 (Nonreactive)

Nonwastewater

Aug. 8, 1988.

K046

All others

Aug. 8, 1990.

K047

All

Aug. 8, 1988.

K048

Wastewater

Aug. 8, 1990.

K048

Nonwastewater

Nov. 8, 1990.

K049

Wastewater

Aug. 8, 1990.

K049

Nonwastewater

Nov. 8, 1990.

K050

Wastewater

Aug. 8, 1990.

K050

Nonwastewater

Nov. 8, 1990.

K051

Wastewater

Aug. 8, 1990.

K051

Nonwastewater

Nov. 8, 1990.

K052

Wastewater

Aug. 8, 1990.

K052

Nonwastewater

Nov. 8, 1990.

K060

Wastewater

Aug. 8, 1990.

K060

Nonwastewater

Aug. 8, 1988.

K061

Wastewater

Aug. 8, 1990.

K061

Nonwastewater

June 30, 1992.

K062

All

Aug. 8, 1988.

K069 (Non-Calcium Sulfate)

Nonwastewater

Aug. 8, 1988.

K069

All others

Aug. 8, 1990.

K071

All

Aug. 8, 1990.

K073

All

Aug. 8, 1990.

K083

All

Aug. 8, 1990.

K084

Wastewater

Aug. 8, 1990.

K084

Nonwastewater

May 8, 1992.

K085

All

Aug. 8, 1990.

K086 (organics) b

All

Aug. 8, 1988.

K086

All others

Aug. 8, 1988.

K087

All

Aug. 8, 1988.

K088

All others

Oct. 8, 1997.

K088

All others

Jan. 8, 1997.

K093

All

June 8, 1989.

K094

All

June 8, 1989.

K095

Wastewater

Aug. 8, 1990.

K095

Nonwastewater

June 8, 1989.

K096

Wastewater

Aug. 8, 1990.

K096

Nonwastewater

June 8, 1989.

K097

All

Aug. 8, 1990.

K098

All

Aug. 8, 1990.

K099

All

Aug. 8, 1988.

K100

Wastewater

Aug. 8, 1990.

K100

Nonwastewater

Aug. 8, 1988.

K101 (organics)

Wastewater

Aug. 8, 1988.

K101 (metals)

Wastewater

Aug. 8, 1990.

K101 (organics)

Nonwastewater

Aug. 8, 1988.

K101 (metals)

Nonwastewater

May 8, 1992.

K102 (organics)

Wastewater

Aug. 8, 1988.

K102 (metals)

Wastewater

Aug. 8, 1990.

K102 (organics)

Nonwastewater

Aug. 8, 1988.

K102 (metals)

Nonwastewater

May 8, 1992.

K103

All

Aug. 8, 1988.

K104

All

Aug. 8, 1988.

K105

All

Aug. 8, 1990.

K106

Wastewater

Aug. 8, 1990.

K106

Nonwastewater

May 8, 1992.

K107

Mixed with radioactive wastes

June 30, 1994.

K107

All others

Nov. 9, 1992.

K108

Mixed with radioactive wastes

June 30, 1994.

K108

All others

Nov. 9, 1992.

K109

Mixed with radioactive wastes

June 30, 1994.

K109

All others

Nov. 9, 1992.

K110

Mixed with radioactive wastes

June 30, 1994.

K110

All others

Nov. 9, 1992.

K111

Mixed with radioactive wastes

June 30, 1994.

K111

All others

Nov. 9, 1992.

K112

Mixed with radioactive wastes

June 30, 1994.

K112

All others

Nov. 9, 1992.

K113

All

June 8, 1989.

K114

All

June 8, 1989.

K115

All

June 8, 1989.

K116

All

June 8, 1989.

K117

Mixed with radioactive wastes

June 30, 1994.

K117

All others

Nov. 9, 1992.

K118

Mixed with radioactive wastes

June 30, 1994.

K118

All others

Nov. 9, 1992.

K123

Mixed with radioactive wastes

June 30, 1994.

K123

All others

Nov. 9, 1992.

K124

Mixed with radioactive wastes

June 30, 1994.

K124

All others

Nov. 9, 1992.

K125

Mixed with radioactive wastes

June 30, 1994.

K125

All others

Nov. 9, 1992.

K126

Mixed with radioactive wastes

June 30, 1994.

K126

All others

Nov. 9, 1992.

K131

Mixed with radioactive wastes

June 30, 1994.

K131

All others

Nov. 9, 1992.

K132

Mixed with radioactive wastes

June 30, 1994.

K132

All others

Nov. 9, 1992.

K136

Mixed with radioactive wastes

June 30, 1994.

K136

All others

Nov. 9, 1992.

K141

Mixed with radioactive wastes

Sep. 19, 1996.

K141

All others

Dec. 19, 1994.

K142

Mixed with radioactive wastes

Sep. 19, 1996.

K142

All others

Dec. 19, 1994.

K143

Mixed with radioactive wastes

Sep. 19, 1996.

K143

All others

Dec. 19, 1994.

K144

Mixed with radioactive wastes

Sep. 19, 1996.

K144

All others

Dec. 19, 1994.

K145

Mixed with radioactive wastes

Sep. 19, 1996.

K145

All others

Dec. 19, 1994.

K147

Mixed with radioactive wastes

Sep. 19, 1996.

K147

All others

Dec. 19, 1994.

K148

Mixed with radioactive wastes

Sep. 19, 1996.

K148

All others

Dec. 19, 1994.

K149

Mixed with radioactive wastes

Sep. 19, 1996.

K149

All others

Dec. 19, 1994.

K150

Mixed with radioactive wastes

Sep. 19, 1996.

K150

All others

Dec. 19, 1994.

K151

Mixed with radioactive wastes

Sep. 19, 1996.

K151

All others

Dec. 19, 1994.

K156

Mixed with radioactive wastes

Apr. 8, 1998.

K156

All others

July 8, 1996.

K157

Mixed with radioactive wastes

Apr. 8, 1998.

K157

All others

July 8, 1996.

K158

Mixed with radioactive wastes

Apr. 8, 1998.

K158

All others

July 8, 1996.

K159

Mixed with radioactive wastes

Apr. 8, 1998.

K159

All others

July 8, 1996.

K160

Mixed with radioactive wastes

Apr. 8, 1998.

K160

All others

July 8, 1996.

K161

Mixed with radioactive wastes

Apr. 8, 1998.

K161

All others

July 8, 1996.

P001

All

Aug. 8, 1990.

P002

All

Aug. 8, 1990.

P003

All

Aug. 8, 1990.

P004

All

Aug. 8, 1990.

P005

All

Aug. 8, 1990.

P006

All

Aug. 8, 1990.

P007

All

Aug. 8, 1990.

P008

All

Aug. 8, 1990.

P009

All

Aug. 8, 1990.

P010

Wastewater

Aug. 8, 1990.

P010

Nonwastewater

May 8, 1992.

P011

Wastewater

Aug. 8, 1990.

P011

Nonwastewater

May 8, 1992.

P012

Wastewater

Aug. 8, 1990.

P012

Nonwastewater

May 8, 1992.

P013 (barium)

Nonwastewater

Aug. 8, 1990.

P013

All others

June 8, 1989.

P014

All

Aug. 8, 1990.

P015

All

Aug. 8, 1990.

P016

All

Aug. 8, 1990.

P017

All

Aug. 8, 1990.

P018

All

Aug. 8, 1990.

P020

All

Aug. 8, 1990.

P021

All

June 8, 1989.

P022

All

Aug. 8, 1990.

P023

All

Aug. 8, 1990.

P024

All

Aug. 8, 1990.

P026

All

Aug. 8, 1990.

P027

All

Aug. 8, 1990.

P028

All

Aug. 8, 1990.

P029

All

June 8, 1989.

P030

All

June 8, 1989.

P031

All

Aug. 8, 1990.

P033

All

Aug. 8, 1990.

P034

All

Aug. 8, 1990.

P036

Wastewater

Aug. 8, 1990.

P036

Nonwastewater

May 8, 1992.

P037

All

Aug. 8, 1990.

P038

Wastewater

Aug. 8, 1990.

P038

Nonwastewater

May 8, 1992.

P039

All

June 8, 1989.

P040

All

June 8, 1989.

P041

All

June 8, 1989.

P042

All

Aug. 8, 1990.

P043

All

June 8, 1989.

P044

All

June 8, 1989.

P045

All

Aug. 8, 1990.

P046

All

Aug. 8, 1990.

P047

All

Aug. 8, 1990.

P048

All

Aug. 8, 1990.

P049

All

Aug. 8, 1990.

P050

All

Aug. 8, 1990.

P051

All

Aug. 8, 1990.

P054

All

Aug. 8, 1990.

P056

All

Aug. 8, 1990.

P057

All

Aug. 8, 1990.

P058

All

Aug. 8, 1990.

P059

All

Aug. 8, 1990.

P060

All

Aug. 8, 1990.

P062

All

June 8, 1989.

P063

All

June 8, 1989.

P064

All

Aug. 8, 1990.

P065

Wastewater

Aug. 8, 1990.

P065

Nonwastewater

May 8, 1992.

P066

All

Aug. 8, 1990.

P067

All

Aug. 8, 1990.

P068

All

Aug. 8, 1990.

P069

All

Aug. 8, 1990.

P070

All

Aug. 8, 1990.

P071

All

June 8, 1989.

P072

All

Aug. 8, 1990.

P073

All

Aug. 8, 1990.

P074

All

June 8, 1989.

P075

All

Aug. 8, 1990.

P076

All

Aug. 8, 1990.

P077

All

Aug. 8, 1990.

P078

All

Aug. 8, 1990.

P081

All

Aug. 8, 1990.

P082

All

Aug. 8, 1990.

P084

All

Aug. 8, 1990.

P085

All

June 8, 1989.

P087

All

May 8, 1992.

P088

All

Aug. 8, 1990.

P089

All

June 8, 1989.

P092

Wastewater

Aug. 8, 1990.

P092

Nonwastewater

May 8, 1992.

P093

All

Aug. 8, 1990.

P094

All

June 8, 1989.

P095

All

Aug. 8, 1990.

P096

All

Aug. 8, 1990.

P097

All

June 8, 1989.

P098

All

June 8, 1989.

P099 (silver)

Wastewater

Aug. 8, 1990.

P099

All others

June 8, 1989.

P101

All

Aug. 8, 1990.

P102

All

Aug. 8, 1990.

P103

All

Aug. 8, 1990.

P104 (silver)

Wastewater

Aug. 8, 1990.

P104

All others

June 8, 1989.

P105

All

Aug. 8, 1990.

P106

All

June 8, 1989.

P108

All

Aug. 8, 1990.

P109

All

June 8, 1989.

P110

All

Aug. 8, 1990.

P111

All

June 8, 1989.

P112

All

Aug. 8, 1990.

P113

All

Aug. 8, 1990.

P114

All

Aug. 8, 1990.

P115

All

Aug. 8, 1990.

P116

All

Aug. 8, 1990.

P118

All

Aug. 8, 1990.

P119

All

Aug. 8, 1990.

P120

All

Aug. 8, 1990.

P121

All

June 8, 1989.

P122

All

Aug. 8, 1990.

P123

All

Aug. 8, 1990.

P127

Mixed with radioactive wastes

Apr. 8, 1998.

P127

All others

July 8, 1996.

P128

Mixed with radioactive wastes

Apr. 8, 1998.

P128

All others

July 8, 1996.

P185

Mixed with radioactive wastes

Apr. 8, 1998.

P185

All others

July 8, 1996.

P188

Mixed with radioactive wastes

Apr. 8, 1998.

P188

All others

July 8, 1996.

P189

Mixed with radioactive wastes

Apr. 8, 1998.

P189

All others

July 8, 1996.

P190

Mixed with radioactive wastes

Apr. 8, 1998.

P190

All others

July 8, 1996.

P191

Mixed with radioactive wastes

Apr. 8, 1998.

P191

All others

July 8, 1996.

P192

Mixed with radioactive wastes

Apr. 8, 1998.

P192

All others

July 8, 1996.

P194

Mixed with radioactive wastes

Apr. 8, 1998.

P194

All others

July 8, 1996.

P196

Mixed with radioactive wastes

Apr. 8, 1998.

P196

All others

July 8, 1996.

P197

Mixed with radioactive wastes

Apr. 8, 1998.

P197

All others

July 8, 1996.

P198

Mixed with radioactive wastes

Apr. 8, 1998.

P198

All others

July 8, 1996.

P199

Mixed with radioactive wastes

Apr. 8, 1998.

P199

All others

July 8, 1996.

P201

Mixed with radioactive wastes

Apr. 8, 1998.

P201

All others

July 8, 1996.

P202

Mixed with radioactive wastes

Apr. 8, 1998.

P202

All others

July 8, 1996.

P203

Mixed with radioactive wastes

Apr. 8, 1998.

P203

All others

July 8, 1996.

P204

Mixed with radioactive wastes

Apr. 8, 1998.

P204

All others

July 8, 1996.

P205

Mixed with radioactive wastes

Apr. 8, 1998.

P205

All others

July 8, 1996.

U001

All

Aug. 8, 1990.

U002

All

Aug. 8, 1990.

U003

All

Aug. 8, 1990.

U004

All

Aug. 8, 1990.

U005

All

Aug. 8, 1990.

U006

All

Aug. 8, 1990.

U007

All

Aug. 8, 1990.

U008

All

Aug. 8, 1990.

U009

All

Aug. 8, 1990.

U010

All

Aug. 8, 1990.

U011

All

Aug. 8, 1990.

U012

All

Aug. 8, 1990.

U014

All

Aug. 8, 1990.

U015

All

Aug. 8, 1990.

U016

All

Aug. 8, 1990.

U017

All

Aug. 8, 1990.

U018

All

Aug. 8, 1990.

U019

All

Aug. 8, 1990.

U020

All

Aug. 8, 1990.

U021

All

Aug. 8, 1990.

U022

All

Aug. 8, 1990.

U023

All

Aug. 8, 1990.

U024

All

Aug. 8, 1990.

U025

All

Aug. 8, 1990.

U026

All

Aug. 8, 1990.

U027

All

Aug. 8, 1990.

U028

All

June 8, 1989.

U029

All

Aug. 8, 1990.

U030

All

Aug. 8, 1990.

U031

All

Aug. 8, 1990.

U032

All

Aug. 8, 1990.

U033

All

Aug. 8, 1990.

U034

All

Aug. 8, 1990.

U035

All

Aug. 8, 1990.

U036

All

Aug. 8, 1990.

U037

All

Aug. 8, 1990.

U038

All

Aug. 8, 1990.

U039

All

Aug. 8, 1990.

U041

All

Aug. 8, 1990.

U042

All

Aug. 8, 1990.

U043

All

Aug. 8, 1990.

U044

All

Aug. 8, 1990.

U045

All

Aug. 8, 1990.

U046

All

Aug. 8, 1990.

U047

All

Aug. 8, 1990.

U048

All

Aug. 8, 1990.

U049

All

Aug. 8, 1990.

U050

All

Aug. 8, 1990.

U051

All

Aug. 8, 1990.

U052

All

Aug. 8, 1990.

U053

All

Aug. 8, 1990.

U055

All

Aug. 8, 1990.

U056

All

Aug. 8, 1990.

U057

All

Aug. 8, 1990.

U058

All

June 8, 1989.

U059

All

Aug. 8, 1990.

U060

All

Aug. 8, 1990.

U061

All

Aug. 8, 1990.

U062

All

Aug. 8, 1990.

U063

All

Aug. 8, 1990.

U064

All

Aug. 8, 1990.

U066

All

Aug. 8, 1990.

U067

All

Aug. 8, 1990.

U068

All

Aug. 8, 1990.

U069

All

June 30, 1992.

U070

All

Aug. 8, 1990.

U071

All

Aug. 8, 1990.

U072

All

Aug. 8, 1990.

U073

All

Aug. 8, 1990.

U074

All

Aug. 8, 1990.

U075

All

Aug. 8, 1990.

U076

All

Aug. 8, 1990.

U077

All

Aug. 8, 1990.

U078

All

Aug. 8, 1990.

U079

All

Aug. 8, 1990.

U080

All

Aug. 8, 1990.

U081

All

Aug. 8, 1990.

U082

All

Aug. 8, 1990.

U083

All

Aug. 8, 1990.

U084

All

Aug. 8, 1990.

U085

All

Aug. 8, 1990.

U086

All

Aug. 8, 1990.

U087

All

June 8, 1989.

U088

All

June 8, 1989.

U089

All

Aug. 8, 1990.

U090

All

Aug. 8, 1990.

U091

All

Aug. 8, 1990.

U092

All

Aug. 8, 1990.

U093

All

Aug. 8, 1990.

U094

All

Aug. 8, 1990.

U095

All

Aug. 8, 1990.

U096

All

Aug. 8, 1990.

U097

All

Aug. 8, 1990.

U098

All

Aug. 8, 1990.

U099

All

Aug. 8, 1990.

U101

All

Aug. 8, 1990.

U102

All

June 8, 1989.

U103

All

Aug. 8, 1990.

U105

All

Aug. 8, 1990.

U106

All

Aug. 8, 1990.

U107

All

June 8, 1989.

U108

All

Aug. 8, 1990.

U109

All

Aug. 8, 1990.

U110

All

Aug. 8, 1990.

U111

All

Aug. 8, 1990.

U112

All

Aug. 8, 1990.

U113

All

Aug. 8, 1990.

U114

All

Aug. 8, 1990.

U115

All

Aug. 8, 1990.

U116

All

Aug. 8, 1990.

U117

All

Aug. 8, 1990.

U118

All

Aug. 8, 1990.

U119

All

Aug. 8, 1990.

U120

All

Aug. 8, 1990.

U121

All

Aug. 8, 1990.

U122

All

Aug. 8, 1990.

U123

All

Aug. 8, 1990.

U124

All

Aug. 8, 1990.

U125

All

Aug. 8, 1990.

U126

All

Aug. 8, 1990.

U127

All

Aug. 8, 1990.

U128

All

Aug. 8, 1990.

U129

All

Aug. 8, 1990.

U130

All

Aug. 8, 1990.

U131

All

Aug. 8, 1990.

U132

All

Aug. 8, 1990.

U133

All

Aug. 8, 1990.

U134

All

Aug. 8, 1990.

U135

All

Aug. 8, 1990.

U136

Wastewater

Aug. 8, 1990.

U136

Nonwastewater

May 8, 1992.

U137

All

Aug. 8, 1990.

U138

All

Aug. 8, 1990.

U140

All

Aug. 8, 1990.

U141

All

Aug. 8, 1990.

U142

All

Aug. 8, 1990.

U143

All

Aug. 8, 1990.

U144

All

Aug. 8, 1990.

U145

All

Aug. 8, 1990.

U146

All

Aug. 8, 1990.

U147

All

Aug. 8, 1990.

U148

All

Aug. 8, 1990.

U149

All

Aug. 8, 1990.

U150

All

Aug. 8, 1990.

U151

Wastewater

Aug. 8, 1990.

U151

Nonwastewater

May 8, 1992.

U152

All

Aug. 8, 1990.

U153

All

Aug. 8, 1990.

U154

All

Aug. 8, 1990.

U155

All

Aug. 8, 1990.

U156

All

Aug. 8, 1990.

U157

All

Aug. 8, 1990.

U158

All

Aug. 8, 1990.

U159

All

Aug. 8, 1990.

U160

All

Aug. 8, 1990.

U161

All

Aug. 8, 1990.

U162

All

Aug. 8, 1990.

U163

All

Aug. 8, 1990.

U164

All

Aug. 8, 1990.

U165

All

Aug. 8, 1990.

U166

All

Aug. 8, 1990.

U167

All

Aug. 8, 1990.

U168

All

Aug. 8, 1990.

U169

All

Aug. 8, 1990.

U170

All

Aug. 8, 1990.

U171

All

Aug. 8, 1990.

U172

All

Aug. 8, 1990.

U173

All

Aug. 8, 1990.

U174

All

Aug. 8, 1990.

U176

All

Aug. 8, 1990.

U177

All

Aug. 8, 1990.

U178

All

Aug. 8, 1990.

U179

All

Aug. 8, 1990.

U180

All

Aug. 8, 1990.

U181

All

Aug. 8, 1990.

U182

All

Aug. 8, 1990.

U183

All

Aug. 8, 1990.

U184

All

Aug. 8, 1990.

U185

All

Aug. 8, 1990.

U186

All

Aug. 8, 1990.

U187

All

Aug. 8, 1990.

U188

All

Aug. 8, 1990.

U189

All

Aug. 8, 1990.

U190

All

June 8, 1989.

U191

All

Aug. 8, 1990.

U192

All

Aug. 8, 1990.

U193

All

Aug. 8, 1990.

U194

All

June 8, 1989.

U196

All

Aug. 8, 1990.

U197

All

Aug. 8, 1990.

U200

All

Aug. 8, 1990.

U201

All

Aug. 8, 1990.

U203

All

Aug. 8, 1990.

U204

All

Aug. 8, 1990.

U205

All

Aug. 8, 1990.

U206

All

Aug. 8, 1990.

U207

All

Aug. 8, 1990.

U208

All

Aug. 8, 1990.

U209

All

Aug. 8, 1990.

U210

All

Aug. 8, 1990.

U211

All

Aug. 8, 1990.

U213

All

Aug. 8, 1990.

U214

All

Aug. 8, 1990.

U215

All

Aug. 8, 1990.

U216

All

Aug. 8, 1990.

U217

All

Aug. 8, 1990.

U218

All

Aug. 8, 1990.

U219

All

Aug. 8, 1990.

U220

All

Aug. 8, 1990.

U221

All

June 8, 1989.

U222

All

Aug. 8, 1990.

U223

All

June 8, 1989.

U225

All

Aug. 8, 1990.

U226

All

Aug. 8, 1990.

U227

All

Aug. 8, 1990.

U228

All

Aug. 8, 1990.

U234

All

Aug. 8, 1990.

U235

All

June 8, 1989.

U236

All

Aug. 8, 1990.

U237

All

Aug. 8, 1990.

U238

All

Aug. 8, 1990.

U239

All

Aug. 8, 1990.

U240

All

Aug. 8, 1990.

U243

All

Aug. 8, 1990.

U244

All

Aug. 8, 1990.

U246

All

Aug. 8, 1990.

U247

All

Aug. 8, 1990.

U248

All

Aug. 8, 1990.

U249

All

Aug. 8, 1990.

U271

Mixed with radioactive wastes

Apr. 8, 1998.

U271

All others

July 8, 1996.

U277

Mixed with radioactive wastes

Apr. 8, 1998.

U277

All others

July 8, 1996.

U278

Mixed with radioactive wastes

Apr. 8, 1998.

U278

All others

July 8, 1996.

U279

Mixed with radioactive wastes

Apr. 8, 1998.

U279

All others

July 8, 1996.

U280

Mixed with radioactive wastes

Apr. 8, 1998.

U280

All others

July 8, 1996.

U328

Mixed with radioactive wastes

June 30, 1994.

U328

All others

Nov. 9, 1992.

U353

Mixed with radioactive wastes

June 30, 1994.

U353

All others

Nov. 9, 1992.

U359

Mixed with radioactive wastes

June 30, 1994.

U359

All others

Nov. 9, 1992.

U364

Mixed with radioactive wastes

Apr. 8, 1998.

U364

All others

July 8, 1996.

U365

Mixed with radioactive wastes

Apr. 8, 1998.

U365

All others

July 8, 1996.

U366

Mixed with radioactive wastes

Apr. 8, 1998.

U366

All others

July 8, 1996.

U367

Mixed with radioactive wastes

Apr. 8, 1998.

U367

All others

July 8, 1996.

U372

Mixed with radioactive wastes

Apr. 8, 1998.

U372

All others

July 8, 1996.

U373

Mixed with radioactive wastes

Apr. 8, 1998.

U373

All others

July 8, 1996.

U375

Mixed with radioactive wastes

Apr. 8, 1998.

U375

All others

July 8, 1996.

U376

Mixed with radioactive wastes

Apr. 8, 1998.

U376

All others

July 8, 1996.

U377

Mixed with radioactive wastes

Apr. 8, 1998.

U377

All others

July 8, 1996.

U378

Mixed with radioactive wastes

Apr. 8, 1998.

U378

All others

July 8, 1996.

U379

Mixed with radioactive wastes

Apr. 8, 1998.

U379

All others

July 8, 1996.

U381

Mixed with radioactive wastes

Apr. 8, 1998.

U381

All others

July 8, 1996.

U382

Mixed with radioactive wastes

Apr. 8, 1998.

U382

All others

July 8, 1996.

U383

Mixed with radioactive wastes

Apr. 8, 1998.

U383

All others

July 8, 1996.

U384

Mixed with radioactive wastes

Apr. 8, 1998.

U384

All others

July 8, 1996.

U385

Mixed with radioactive wastes

Apr. 8, 1998.

U385

All others

July 8, 1996.

U386

Mixed with radioactive wastes

Apr. 8, 1998.

U386

All others

July 8, 1996.

U387

Mixed with radioactive wastes

Apr. 8, 1998.

U387

All others

July 8, 1996.

U389

Mixed with radioactive wastes

Apr. 8, 1998.

U389

All others

July 8, 1996.

U390

Mixed with radioactive wastes

Apr. 8, 1998.

U390

All others

July 8, 1996.

U391

Mixed with radioactive wastes

Apr. 8, 1998.

U391

All others

July 8, 1996.

U392

Mixed with radioactive wastes

Apr. 8, 1998.

U392

All others

July 8, 1996.

U393

Mixed with radioactive wastes

Apr. 8, 1998.

U393

All others

July 8, 1996.

U394

Mixed with radioactive wastes

Apr. 8, 1998.

U394

All others

July 8, 1996.

U395

Mixed with radioactive wastes

Apr. 8, 1998.

U395

All others

July 8, 1996.

U396

Mixed with radioactive wastes

Apr. 8, 1998.

U396

All others

July 8, 1996.

U400

Mixed with radioactive wastes

Apr. 8, 1998.

U400

All others

July 8, 1996.

U401

Mixed with radioactive wastes

Apr. 8, 1998.

U401

All others

July 8, 1996.

U402

Mixed with radioactive wastes

Apr. 8, 1998.

U402

All others

July 8, 1996.

U403

Mixed with radioactive wastes

Apr. 8, 1998.

U403

All others

July 8, 1996.

U404

Mixed with radioactive wastes

Apr. 8, 1998.

U404

All others

July 8, 1996.

U407

Mixed with radioactive wastes

Apr. 8, 1998.

U407

All others

July 8, 1996.

U409

Mixed with radioactive wastes

Apr. 8, 1998.

U409

All others

July 8, 1996.

U410

Mixed with radioactive wastes

Apr. 8, 1998.

U410

All others

July 8, 1996.

U411

Mixed with radioactive wastes

Apr. 8, 1998.

U411

All others

July 8, 1996.

a This table does not include mixed radioactive wastes (from the First, Second, and Third Third rules) which received national capacity variance until May 8, 1992. This table also does not include contaminated soil and debris wastes.

b The standard was revised in the Third Third Final Rule (55 FR 22520, June 1, 1990).

c The standard was revised in the Third Third Emergency Rule (58 FR 29860, May 24, 1993); the original effective date was August 8, 1990.

d The standard was revised in the Phase II Final Rule (59 FR 47982, Sept. 19, 1994); the original effective date was August 8, 1990.

e The standards for selected reactive wastes was revised in the Phase III Final Rule (61 FR 15566, Apr. 8, 1996); the original effective date was August 8, 1990.

Table 2—Summary of Effective Dates of Land Disposal Restrictions for Contaminated Soil and Debris (CSD)

Restricted hazardous waste in CSD

Effective date

1. Solvent-(F001-F005) and dioxin-(F020-F023 and F026-F028) containing soil and debris from CERCLA response or RCRA corrective actions

Nov. 8, 1990.

2. Soil and debris not from CERCLA response or RCRA corrective actions contaminated with less than 1% total solvents (F001-F005) or dioxins (F020-F023 and F026-F028)

Nov. 8, 1988.

3 All soil and debris contaminated with First Third wastes for which treatment standards are based on incineration

Aug. 8, 1990.

4. All soil and debris contaminated with Second Third wastes for which treatment standards are based on incineration

June 8, 1991.

5. All soil and debris contaminated with Third Third wastes or, First or Second Third “soft hammer” wastes which had treatment standards promulgated in the Third Third rule, for which treatment standards are based on incineration, vitrification, or mercury retorting, acid leaching followed by chemical precipitation, or thermal recovery of metals; as well as all inorganic solids debris contaminated with D004-D011 wastes, and all soil and debris contaminated with mixed RCRA/radioactive wastes

May 8, 1992.

6. Soil and debris contaminated with D012-D043, K141-K145, and K147-151 wastes

Dec. 19, 1994.

7. Debris (only) contaminated with F037, F038, K107-K112, K117, K118, K123-K126, K131, K132, K136, U328, U353, U359

Dec. 19, 1994

8. Soil and debris contaminated with K156-K161, P127, P128, P188-P192, P194, P196-P199, P201-P205, U271, U277-U280, U364-U367, U372, U373, U375-U379, U381-U387, U389-U396, U400-U404, U407, and U409-U411 wastes

July 8, 1996.

9. Soil and debris contaminated with K088 wastes

Oct. 8, 1997.

10. Soil and debris contaminated with radioactive wastes mixed with K088, K156-K161, P127, P128, P188-P192, P194, P196-P199, P201-P205, U271, U277-U280, U364-U367, U372, U373, U375-U379, U381-U387, U389-U396, U400-U404, U407, and U409-U411 wastes

April 8, 1998.

11. Soil and debris contaminated with F032, F034, and F035

May 12, 1997.

12. Soil and debris contaminated with newly identified D004-D011 toxicity characteristic wastes and mineral processing wastes.

Aug. 24, 1998.

13. Soil and debris contaminated with mixed radioactive newly identified D004-D011 characteristic wastes and mineral processing wastes.

May 26, 2000.

Note: Appendix VII is provided for the convenience of the reader.

Appendix VIII Appendix VIII to Part 268—LDR Effective Dates of Injected Prohibited Hazardous Wastes

National Capacity LDR Variances for UIC Wastes a

Waste code

Waste category

Effective date

F001-F005

All spent F001-F005 solvent containing less than 1 percent total F001-F005 solvent constituents

Aug. 8, 1990.

D001 (except High TOC Ignitable Liquids Subcategory) c

All

Feb. 10, 1994.

D001 (High TOC Ignitable Characteristic Liquids Subcategory)

Nonwastewater

Sept. 19, 1995.

D002 b

All

May 8, 1992.

D002 c

All

Feb. 10, 1994.

D003 (cyanides)

All

May 8, 1992.

D003 (sulfides)

All

May 8, 1992.

D003 (explosives, reactives)

All

May 8, 1992.

D007

All

May 8, 1992.

D009

Nonwastewater

May 8, 1992.

D012

All

Sept. 19, 1995.

D013

All

Sept. 19, 1995.

D014

All

Sept. 19, 1995.

D015

All

Sept. 19, 1995.

D016

All

Sept. 19, 1995.

D017

All

Sept. 19, 1995.

D018

All, including mixed with radioactive wastes

Apr. 8, 1998.

D019

All, including mixed with radioactive wastes

Apr. 8, 1998.

D020

All, including mixed with radioactive wastes

Apr. 8, 1998.

D021

All, including mixed with radioactive wastes

Apr. 8, 1998.

D022

All, including mixed with radioactive wastes

Apr. 8, 1998.

D023

All, including mixed radioactive wastes

Apr. 8, 1998.

D024

All, including mixed radioactive wastes

Apr. 8, 1998.

D025

All, including mixed radioactive wastes

Apr. 8, 1998.

D026

All, including mixed radioactive wastes

Apr. 8, 1998.

D027

All, including mixed radioactive wastes

Apr. 8, 1998.

D028

All, including mixed radioactive wastes

Apr. 8, 1998.

D029

All, including mixed radioactive wastes

Apr. 8, 1998.

D030

All, including mixed radioactive wastes

Apr. 8, 1998.

D031

All, including mixed radioactive wastes

Apr. 8, 1998.

D032

All, including mixed radioactive wastes

Apr. 8, 1998.

D033

All, including mixed radioactive wastes

Apr. 8, 1998.

D034

All, including mixed radioactive wastes

Apr. 8, 1998.

D035

All, including mixed radioactive wastes

Apr. 8, 1998.

D036

All, including mixed radioactive wastes

Apr. 8, 1998.

D037

All, including mixed radioactive wastes

Apr. 8, 1998.

D038

All, including mixed radioactive wastes

Apr. 8, 1998.

D039

All, including mixed radioactive wastes

Apr. 8, 1998.

D040

All, including mixed radioactive wastes

Apr. 8, 1998.

D041

All, including mixed radioactive wastes

Apr. 8, 1998.

D042

All, including mixed radioactive wastes

Apr. 8, 1998.

D043

All, including mixed radioactive wastes

Apr. 8, 1998.

F007

All

June 8, 1991.

F032

All, including mixed radioactive wastes

May 12, 1999.

F034

All, including mixed radioactive wastes

May 12, 1999.

F035

All, including mixed radioactive wastes

May 12, 1999.

F037

All

Nov. 8, 1992.

F038

All

Nov. 8, 1992.

F039

Wastewater

May 8, 1992.

K009

Wastewater

June 8, 1991.

K011

Nonwastewater

June 8, 1991.

K011

Wastewater

May 8, 1992.

K013

Nonwastewater

June 8, 1991.

K013

Wastewater

May 8, 1992.

K014

All

May 8, 1992.

K016 (dilute)

All

June 8, 1991.

K049

All

Aug. 8, 1990.

K050

All

Aug. 8, 1990.

K051

All

Aug. 8, 1990.

K052

All

Aug. 8, 1990.

K062

All

Aug. 8, 1990.

K071

All

Aug. 8, 1990.

K088

All

Jan. 8, 1997.

K104

All

Aug. 8, 1990.

K107

All

Nov. 8, 1992.

K108

All

Nov. 9, 1992.

K109

All

Nov. 9, 1992.

K110

All

Nov. 9, 1992.

K111

All

Nov. 9, 1992.

K112

All

Nov. 9, 1992.

K117

All

June 30, 1995.

K118

All

June 30, 1995.

K123

All

Nov. 9, 1992.

K124

All

Nov. 9, 1992.

K125

All

Nov. 9, 1992.

K126

All

Nov. 9, 1992.

K131

All

June 30, 1995.

K132

All

June 30, 1995.

K136

All

Nov. 9, 1992.

K141

All

Dec. 19, 1994.

K142

All

Dec. 19, 1994.

K143

All

Dec. 19, 1994.

K144

All

Dec. 19, 1994.

K145

All

Dec. 19, 1994.

K147

All

Dec. 19, 1994.

K148

All

Dec. 19, 1994.

K149

All

Dec. 19, 1994.

K150

All

Dec. 19, 1994.

K151

All

Dec. 19, 1994.

K156

All

July 8, 1996.

K157

All

July 8, 1996.

K158

All

July 8, 1996.

K159

All

July 8, 1996.

K160

All

July 8, 1996.

K161

All

July 8, 1996.

NA

Newly identified mineral processing wastes from titanium dioxide production and mixed radioactive/newly identified D004-D011 characteristic wastes and mineral processing wastes.

May 26, 2000.

P127

All

July 8, 1996.

P128

All

July 8, 1996.

P185

All

July 8, 1996.

P188

All

July 8, 1996.

P189

All

July 8, 1996.

P190

All

July 8, 1996.

P191

All

July 8, 1996.

P192

All

July 8, 1996.

P194

All

July 8, 1996.

P196

All

July 8, 1996.

P197

All

July 8, 1996.

P198

All

July 8, 1996.

P199

All

July 8, 1996.

P201

All

July 8, 1996.

P202

All

July 8, 1996.

P203

All

July 8, 1996.

P204

All

July 8, 1996.

P205

All

July 8, 1996.

U271

All

July 8, 1996.

U277

All

July 8, 1996.

U278

All

July 8, 1996.

U279

All

July 8, 1996.

U280

All

July 8, 1996.

U328

All

Nov. 9, 1992.

U353

All

Nov. 9, 1992.

U359

All

Nov. 9, 1992.

U364

All

July 8, 1996.

U365

All

July 8, 1996.

U366

All

July 8, 1996.

U367

All

July 8, 1996.

U372

All

July 8, 1996.

U373

All

July 8, 1996.

U375

All

July 8, 1996.

U376

All

July 8, 1996.

U377

All

July 8, 1996.

U378

All

July 8, 1996.

U379

All

July 8, 1996.

U381

All

July 8, 1996.

U382

All

July 8, 1996.

U383

All

July 8, 1996.

U384

All

July 8, 1996.

U385

All

July 8, 1996.

U386

All

July 8, 1996.

U387

All

July 8, 1996.

U389

All

July 8, 1996.

U390

All

July 8, 1996.

U391

All

July 8, 1996.

U392

All

July 8, 1996.

U395

All

July 8, 1996.

U396

All

July 8, 1996.

U400

All

July 8, 1996.

U401

All

July 8, 1996.

U402

All

July 8, 1996.

U403

All

July 8, 1996.

U404

All

July 8, 1996.

U407

All

July 8, 1996.

U409

All

July 8, 1996.

U410

All

July 8, 1996.

U411

All

July 8, 1996.

a Wastes that are deep well disposed on-site receive a six-month variance, with restrictions effective in November 1990.

b Deepwell injected D002 liquids with a pH less than 2 must meet the California List treatment standards on August 8, 1990.

c Managed in systems defined in 40 CFR 144.6(e) and 14.6(e) as Class V injection wells, that do not engage in CWA-equivalent treatment before injection.

Note: This table is provided for the convenience of the reader.

Appendix IX Appendix IX to Part 268—Extraction Procedure (EP) Toxicity Test Method and Structural Integrity Test (Method 1310B)

Note:

The EP (Method 1310B) is published in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” EPA Publication SW-846, as incorporated by reference in § 260.11 of this chapter.

Appendix XI Appendix XI to Part 268—Metal Bearing Wastes Prohibited From Dilution in a Combustion Unit According to 40 CFR 268.3( c )

Metal Bearing Wastes Prohibited From Dilution in a Combustion Unit According to 40 CFR 268.3( c ) 1

Waste code

Waste description

D004

Toxicity Characteristic for Arsenic.

D005

Toxicity Characteristic for Barium.

D006

Toxicity Characteristic for Cadmium.

D007

Toxicity Characteristic for Chromium.

D008

Toxicity Characteristic for Lead.

D009

Toxicity Characteristic for Mercury.

D010

Toxicity Characteristic for Selenium.

D011

Toxicity Characteristic for Silver.

F006

Wastewater treatment sludges from electroplating operations except from the following processes: (1) sulfuric acid anodizing of aluminum; (2) tin plating carbon steel; (3) zinc plating (segregated basis) on carbon steel; (4) aluminum or zinc-plating on carbon steel; (5) cleaning/stripping associated with tin, zinc and aluminum plating on carbon steel; and (6) chemical etching and milling of aluminum.

F007

Spent cyanide plating bath solutions from electroplating operations.

F008

Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process.

F009

Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process.

F010

Quenching bath residues from oil baths from metal treating operations where cyanides are used in the process.

F011

Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations.

F012

Quenching waste water treatment sludges from metal heat treating operations where cyanides are used in the process.

F019

Wastewater treatment sludges from the chemical conversion coating of aluminum except from zirconium phosphating in aluminum car washing when such phosphating is an exclusive conversion coating process.

K002

Wastewater treatment sludge from the production of chrome yellow and orange pigments.

K003

Wastewater treatment sludge from the production of molybdate orange pigments.

K004

Wastewater treatment sludge from the production of zinc yellow pigments.

K005

Wastewater treatment sludge from the production of chrome green pigments.

K006

Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous and hydrated).

K007

Wastewater treatment sludge from the production of iron blue pigments.

K008

Oven residue from the production of chrome oxide green pigments.

K061

Emission control dust/sludge from the primary production of steel in electric furnaces.

K069

Emission control dust/sludge from secondary lead smelting.

K071

Brine purification muds from the mercury cell processes in chlorine production, where separately prepurified brine is not used.

K100

Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting.

K106

Sludges from the mercury cell processes for making chlorine.

P010

Arsenic acid H 3 AsO 4

P011

Arsenic oxide As 2 O 5

P012

Arsenic trioxide

P013

Barium cyanide

P015

Beryllium

P029

Copper cyanide Cu(CN)

P074

Nickel cyanide Ni(CN) 2

P087

Osmium tetroxide

P099

Potassium silver cyanide

P104

Silver cyanide

P113

Thallic oxide

P114

Thallium (l) selenite

P115

Thallium (l) sulfate

P119

Ammonium vanadate

P120

Vanadium oxide V 2 O 5

P121

Zinc cyanide.

U032

Calcium chromate.

U145

Lead phosphate.

U151

Mercury.

U204

Selenious acid.

U205

Selenium disulfide.

U216

Thallium (I) chloride.

U217

Thallium (I) nitrate.

1 A combustion unit is defined as any thermal technology subject to 40 CFR part 264, subpart O; Part 265, subpart O; and/or 266, subpart H.