S.C. Code Ann. Regs. 61-79.268
SUBPART A
General
268.1. Purpose, scope and applicability.
(c) Restricted wastes may continue to be land disposed as follows:
(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:
(ii) The wastes are treated for purposes of the pretreatment requirements of section R.61-9 and R.61-68; 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
(e) The following hazardous wastes are not subject to any provision of part 268:
(f) Universal waste handlers and universal waste transporters (as defined in 260.10) are exempt from 268.7 and 268.50 for the hazardous wastes listed below. These handlers are subject to regulation under part 273.
(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: (amended 11/90)
(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. (11/99)
268.3. Dilution prohibited as a substitute for treatment.
(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):
(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: (amended 11/90)
(2) The following conditions are met: (amended 11/90)
(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. 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.
(3) The impoundment meets the design requirements of 264.221(c) or 265.221(a), regardless that the unit may not be new, expanded, or a replacement, and be in compliance with applicable groundwater monitoring requirements of subpart F of Part 264 or 265 unless: (amended 11/90)
(ii) Upon application by the owner or operator, the Department, after notice and an opportunity to comment, has grated a waiver of the requirements on the basis that the surface impoundment:
(C) Is in compliance with generally applicable groundwater monitoring requirements for facilities with permits; or,
(iii) Upon application by the owner or operator, the Department, 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 groundwater or surface water at any future time.
(4) The owner or operator submits to the Department a written certification that the requirements of 268.4(a)(3) have been met and submits a copy of the waste analysis plan required under 268.4(a)(2). The following certification is required: (amended 11/90)
I certify under penalty of law that the requirements of 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. (amended 11/90)
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 Department and the EPA for an extension to the effective date of any applicable restriction established under subpart C of this part. The applicant must demonstrate the following:
(b) An authorized representative signing an application described under paragraph (a) shall make the following certification:
I certify under penalty of law that I have personally examined and that I 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.
(h) Whenever the Department and EPA establishes an extension to an effective date under this section, during the period for which such extension is in effect: (amended 11/90)
(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:
(ii) The landfill, if permitted, is in compliance with the requirements of subpart F of R.61-79.264 and R.61-79.264.301 (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 R.61-79.265, R.61-79.265.221 (a), (c), and (d) of this chapter, and RCRA section 3005(j)(1); (revised 12/92) or
(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 Department and the EPA 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:
(b) The demonstration referred to in paragraph (a) must meet the following criteria:
(c) Each petition referred to in paragraph (a) 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:
(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;
(vi) The implementation schedule for the monitoring program;
(vii) The equipment used at the monitoring stations;
(viii) The sampling and analytical techniques employed; and
(5) The monitoring program specified under paragraph (c)(1) of this section meets the following criteria:
(ii) All estimation and monitoring techniques must be approved by the Department and EPA.
(iii) A quality assurance and quality control plan addressing all aspects of the monitoring program must be provided to and approved by the Department and EPA.
(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: (amended 11/90)
(f) If the owner or operator determines that there is migration of hazardous constituent(s) from the unit, the owner or operator must:
(g) Each petition must include the following statement signed by the petitioner or an authorized representative: (moved 11/90)
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.
(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. (amended 11/90)
268.7. Testing, tracking, and recordkeeping requirements for generators, reverse distributors, treaters, and disposal facilities.
(a) Requirements for generators and reverse distributors:
(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.
(i) For contaminated soil, the following certification statement should be included, signed by an authorized representative:
I certify under penalty of law that I personally have examined this contaminated soil and it [does/does not] contain listed hazardous waste and [does/does not] exhibit a characteristic of hazardous waste and requires treatment to meet the soil treatment standards as provided by 268.49(c).
(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 onetime 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 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. (11/90, 12/92; 5/96, 9/98)
| 268.7(a)(4) table | |||||
| Required information | 268.7(a)(2) | 268.7(a)(3) | 268.7(a)(4) | 268.7(a)(9) | |
| 1. | EPA Hazardous Waste and Manifest numbers and Manifest Number of first shipment | x | x | x | x |
| 2. | Statement: this waste is not prohibited from land disposal | x | |||
| 3. | The waste is subject to the 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) | x | x | ||
| 5. | Waste analysis data (when available) | x | x | x | |
| 6. | Date the waste is subject to the prohibition | x | |||
| 7. | For hazardous debris, when treating with the 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 | x | x | ||
| 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 | x | x | ||
| 9. | A certification is needed (see applicable section for exact wording) | x | x |
(5) If a generator is managing and treating prohibited waste or contaminated soil in tanks, containers, or containment buildings regulated under R.61-79.262.15, 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, 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:
(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 section 268.7(a)(3).
(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):
(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.
(b) Treatment facilities must test their wastes according to the frequency specified in their waste analysis plans as required by 264.13 (for permitted TSDs) or 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. (9/98)
(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. (9/98)
TREATMENT FACILITY PAPERWORK REQUIREMENTS TABLE 268.7 (9/98, 11/99)
| Required Information | 268.7(b) | |
| 1. | EPA Hazardous Waste and Manifest numbers and Manifest Number of first shipment | x |
| 2. | The waste is subject to the LDRs. The constituents of concern for F001-F005 and F039 and underlying constituents in characteristic wastes, unless the wastes will be treated and monitored for all constituents. If all constituents will be treated and monitored, there is no need to put them all on the LDR notice | x |
| 3. | The notice must include the applicable wastewater/nonwastewater category (see 268.2(d) and (f) and subdivisions made within a waste code based on waste-specific criteria (such as D003 reactive cyanide) | x |
| 4. | Waste analysis data (when available) | x |
| 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)” | x |
| 6. | A certification is needed (see applicable section for exact wording) | x |
(4) The treatment facility must submit a one-time certification signed by an authorized representative with the initial shipment of waste or treatment residue of a restricted waste to the land disposal facility. A certification is also necessary for contaminated soil and it must state:
(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: (new 12/92)
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 goodfaith 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: (11/99)
“I certify under penalty of law that the waste has been treated in accordance with the requirements of 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 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.”
“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 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 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 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. (12/93, (9/98)”
(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 266.20(b), the owner or operator of any land disposal facility disposing any waste subject to restrictions under this part must:
(d) Generators or treaters who first claim that hazardous debris is excluded from the definition of hazardous waste under 261.3 (f) (i.e., debris treated by an extraction or destruction technology provided by Table 1, 268.45, and debris that the Department has determined does not contain hazardous waste) are subject to the following notification and certification requirements:
(1) A onetime notification, including the following information, must be submitted to the Department to implement part 268 requirements:
(ii) A description of the hazardous debris as initially generated, including the applicable EPA Hazardous Waste Number(s); and
(iii) For debris excluded under Sections 261.3(f)(1) of this chapter, the technology from Table 1, Sections 268.45, used to treat the debris.
(3) For debris excluded under Sections 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:
(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 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:
(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.
(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:
(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. (revised 12/93; 5/96)
(iii) [Reserved. (5/96)]
(2) The certification must be signed by an authorized representative and must state the language found in 268.7(b)(4). (12/93)
(ii) [Reserved 5/96]
SUBPART B
Schedule for Land Disposal Prohibition and Establishment of Treatment Standards
268.13. Schedule for wastes identified or listed after November 8, 1984.
In the case of any hazardous waste identified or listed under SCHWMA 44-56-30 or RCRA section 3001 after November 8, 1984, the Department shall make a land disposal prohibition determination within 6 months after the date of identification or listing.
268.14. Surface impoundment exemptions.
(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, not withstanding 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.
(b) The requirements of paragraph (a) of this section do not apply if:
(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 268 are applicable, except as otherwise specified.
SUBPART C
Prohibitions on Land Disposal
268.30. Waste specific prohibitions—wood preserving wastes.
(d) The requirements of paragraphs (a) and (b) of this section do not apply if: (amended 11/90)
(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 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:
(d) The requirements of paragraphs (a) and (b) do not apply if:
(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. Soils exhibiting the toxicity characteristic for metals and containing PCBs.
(b) The requirements of paragraph (a) of this section do not apply if:
(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
(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.
(1)(i) The wastes contain halogenated organic compounds in total concentration less than 1,000 mg/kg; and
(b) The requirements of paragraph (a) of this section do not apply if:
(d) Disposal of K175 wastes that have complied with all applicable 268.40 treatment standards must also be macroencapsulated in accordance with 268.45 Table 1 unless the waste is placed in:
(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.
(e) The requirements of paragraphs (a) and (b) of this section do not apply if:
(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 concentrations 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.
(b) The requirements of paragraph (a) of this section do not apply if:
(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.
(b) The requirements of (a) of this section do not apply if:
(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 part 268 are applicable, except as otherwise specified.
268.37. Waste specific prohibitions-ignitable and corrosive characteristic wastes whose treatment standards were vacated.
(b) Effective February 10, 1994, the wastes specified in 261.21 as D001 (and is not in the High TOC Ignitable Liquids Subcategory), and specified in Sections 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.
(d) The requirements of paragraphs (a), (b), and (c) of this section do not apply if:
(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.
(f) The requirements of paragraphs (a), (b), (c), and (d) of this section do not apply if:
(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.
SUBPART D
Treatment Standards
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:
(d) Notwithstanding the prohibitions specified in paragraph (a) of this section, treatment and disposal facilities may demonstrate (and certify pursuant to 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:
(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.
Table 268.40—Treatment Standards for Hazardous Wastes
Note: The treatment standards that heretofore appeared in tables in 268.41, 268.42, and 268.43 of this part have been consolidated into the table “Treatment Standards for Hazardous Wastes” in this section.
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Footnotes to Treatment Standard Table 268.40
1 The waste descriptions provided in this table do not replace waste descriptions in 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/1 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 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 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 268.40(d). All concentration standards for nonwastewaters are based on analysis of grab samples.
6 Where an alternate treatment standard or set of alternate standards has been indicated, a facility may comply with this alternate standard, but only for the Treatment/Regulatory Subcategory or physical form (i.e., wastewater and/or nonwastewater) specified for that alternate standard.
7 Both Cyanides (Total) and Cyanides (Amenable) for nonwastewaters are to be analyzed using Method 9010C or 9012B, found in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods, EPA Publication SW-846, as incorporated by reference in 260.11, with a sample size of 10 grams and a distillation time of one hour and 15 minutes. (2/07)
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(c)(3) and (4)), (See R.61-87.11.D.2).
9 [Reserved 8/00]
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. (8/00)
11 For these wastes, the definition of CMBST is limited to: (1) combustion units operating under 266, (2) combustion units permitted under Part 264, Subpart O, or (3) combustion units operating under 265, Subpart O, which have obtained a determination of equivalent treatment under 268.42(b).[Note: NA means not applicable]
12 Disposal of K175 wastes that have complied with all applicable 268.40 treatment standards must also be microencapsulated in accordance with 268.45 Table 1 unless the waste is placed in:
(2) A dedicated Subtitle C landfill cell in which all other wastes being co-disposed are at pH 6.0.
Note: The treatment standards that heretofore appeared in tables in 268.41, 268.42, and 268.43 of this part have been consolidated into the table “Treatment Standards for Hazardous Wastes.”
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. (major revision 5/96)
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 Descriptions of Technology-Based Standards” in this section. (revised 12/92; 5/96)
| 268.42(a) Table 1—Technology Codes and Description of Technology-Based Standards | |
| Technology code | Description of technology-based standards (9/98) |
| 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 part 264, Subpart O, or part 265, subpart O, or 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. (5/96, 9/98) |
| 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 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 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 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. (9/98) |
| 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 flocculating, 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 crystallization; (6) ultrafiltration and/or (7) simple precipitation (i.e., crystallization) - Note: This does not preclude the use of other physical phase separation or concentration techniques such as decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies. |
| RORGS: | Recovery of organics utilizing one or more of the following technologies: (1) Distillation; (2) thin film evaporation; (3) steam stripping; (4) carbon adsorption; (5) critical fluid extraction; (6) liquid-liquid extraction; (7) precipitation/crystallization (including freeze crystallization); or (8) chemical phase separation techniques (i.e., addition of acids, bases, demulsifiers, or similar chemicals); - Note: this does not preclude the use of other physical phase separation techniques such as 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 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. |
| 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: 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 effective 5/96). 268.42 Table 3. Technology-Based Standards for Specific Radioactive Hazardous Mixed Waste removed 5/96] |
(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:
(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. (revised 12/93; 5/96)
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:
(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 th this is the case, the petitioner must either demonstrate that:
(c) Each petition must include the following statement signed by the petitioner or an authorized representative: (amended 11/90)
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. (amended 11/90)
(h) Based on a petition filed by a generator or treater of hazardous waste, the Department may approve a site-specific variance from an applicable treatment standard if:
(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:
(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:
(o) The following facilities are excluded from the treatment standards under 268.40,and are subject to the following constituent concentrations: (revised 12/92).
TABLE—WASTES EXCLUDED FROM THE TREATMENT STANDARDS UNDER 268.40
| FOOTNOTE: (1)-A facility may certify compliance with these treatment standards according to provisions in 268.7. |
| FOOTNOTE: (2)-Cyanide Wastewater Standards for F006 are based on analysis of composite samples. |
| FOOTNOTE: (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 268.7.a.4 for appropriate monitoring frequency consistent with the facilities’ waste analysis plan. |
| FOOTNOTE: (4)-Cyanide nonwastewaters are analyzed using SW-846 Method 9010 or 9012, sample size 10 grams, distillation time, 1 hour and 15 minutes. |
| Note: NA means Not Applicable. |
(p) [Removed]
268.45. Treatment standards for hazardous debris.
(a) Treatment standards. Hazardous debris must be treated prior to land disposal as follows unless the Department 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: (revised 5/96)
(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:
(d) Treatment residuals-
(1) General requirements. Except as provided by paragraphs (d)(2) and (d)(4) of this section:
(5) Residue from spalling. Layers of debris removed by spalling are hazardous debris that remain subject to the treatment standards of this section.
| Appendix A-10: 268.45(d)(5)—Table 1.—Alternative Treatment Standards For Hazardous Debris1 | ||
| Table 1.—Alternative Treatment Standards For Hazardous Debris1 | ||
| Technology description | Performance and/or design and operating standard | Contaminant restrictions2 |
| A. Extraction Technologies: | ||
| 1. Physical Extraction | ||
| a. Abrasive Blasting: Removal of contaminated debris surface layers using water and/or air pressure to propel a | Glass, Metal, Plastic, Rubber: Treatment to a clean debris surface.3 | All Debris: None. |
| solid media (e.g., steel shot, aluminum oxide grit, plastic beads). | 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 | |
| b. Scarification, Grinding, and Planing: Process utilizing striking piston heads, saws, or rotating grinding wheels such that contaminated debris surface layers are removed. | Same as above | Same as above |
| c. Spalling: Drilling or chipping holes at appropriate locations and depth in the contaminated debris surface and applying a tool which exerts a force on the sides of those holes such that the surface layer is removed. The surface layer removed remains hazardous debris subject to the debris treatment standards. | Same as above | Same as above |
| d. Vibratory Finishing: Process utilizing scrubbing media, flushing fluid, and oscillating energy such that hazardous contaminants or contaminated debris surface layers are removed.4 | Same as above | Same as above |
| e. High Pressure Steam and Water Sprays: Application of water or steam sprays of sufficient temperature, pressure, residence time, agitation, surfactants, and detergents to remove hazardous contaminants from debris surfaces or to remove contaminated debris surface layers | Same as above | Same as above |
| 2. Chemical Extraction | ||
| a. Water Washing and Spraying: Application of water sprays or water baths of sufficient temperature, pressure, residence time, agitation, surfactants, acids, bases, and detergents to remove hazardous contaminants from debris surfaces and surface pores or to remove contaminated debris surface layers. | All Debris: Treatment to a clean debris surface3; Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (1/2 inch) in one dimension (i.e., thickness limit,5 except that this thickness limit may be waived under an “Equivalent Technology” approval under 268.42(b);5 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:6 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. | All Debris: Metals other than mercury. |
| 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. | ||
| 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. | All Debris: Metal contaminants. |
| 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. | ||
| 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,3 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. |
| FOOTNOTE: 1Hazardous debris must be treated by either these standards or the waste-specific treatment standards for the waste contaminating the debris. The treatment standards must be met for each type of debris contained in a mixture of debris types, unless the debris is converted into treatment residue as a result of the treatment process. Debris treatment residuals are subject to the waste-specific treatment standards for the waste contaminating the debris. | ||
| FOOTNOTE: 2Contaminant restriction means that the technology is not BDAT for that contaminant. If debris containing a restricted contaminant is treated by the technology, the contaminant must be subsequently treated by a technology for which it is not restricted in order to be land disposed (and excluded from Subtitle C regulation). | ||
| FOOTNOTE: 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. | ||
| FOOTNOTE: 4Acids, solvents, and chemical reagents may react with some debris and contaminants to form hazardous compounds. For example, acid washing of cyanide-contaminated debris could result in the formation of hydrogen cyanide. Some acids may also react violently with some debris and contaminants, depending on the concentration of the acid and the type of debris and contaminants. Debris treaters should refer to the safety precautions specified in Material Safety Data Sheets for various acids to avoid applying an incompatible acid to a particular debris/contaminant combination. For example, concentrated sulfuric acid may react violently with certain organic compounds, such as acrylonitrile. | ||
| FOOTNOTE: 5If reducing the particle size of debris to meet the treatment standards results in material that no longer meets the 60 mm minimum particle size limit for debris, such material is subject to the waste-specific treatment standards for the waste contaminating the material, unless the debris has been cleaned and separated from contaminated soil and waste prior to size reduction. At a minimum, simple physical or mechanical means must be used to provide such cleaning and separation of nondebris materials to ensure that the debris surface is free of caked soil, waste, or other nondebris material. | ||
| FOOTNOTE: 6Dioxin-listed wastes are EPA Hazardous Waste numbers FO20, FO21, FO22, FO23, FO26, and FO27. | ||
| FOOTNOTE: 7Thermal desorption is distinguished from Thermal Destruction in that the primary purpose of Thermal Desorption is to volatilize contaminants and to remove them from the treatment chamber for subsequent destruction or other treatment. | ||
| FOOTNOTE: 8The 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. | ||
| FOOTNOTE: 9Any soil, waste, and other nondebris material that remains on the debris surface (or remains mixed with the debris) after treatment is considered a treatment residual that must be separated from the debris using, at a minimum, simple physical or mechanical means. Examples of simple physical or mechanical means are vibratory or trommel screening or water washing. The debris surface need not be cleaned to a “clean debris surface” as defined in note 3 when separating treated debris from residue; rather, the surface must be free of caked soil, waste, or other nondebris material. Treatment residuals are subject to the waste-specific treatment standards for the waste contaminating the debris.” |
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 (added 5/96).
(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.
| 268.48 - UNIVERSAL TREATMENT STANDARDS NOTE: NA means not applicable (8/00, 2/07) | |||
| REGULATED CONSTITUENT Common Name | CAS1 Number | Wastewater Standard | Nonwastewater Standard |
| Concentration2 in mg/l | Concentration3 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-Chlorophenol | 95-57-8 | 0.044 | 5.7 |
| 3-Chloropropylene | 107-05-1 | 0.036 | 30 |
| Chrysene | 218-01-9 | 0.059 | 3.4 |
| p-Cresidine | 120-71-8 | 0.010 | 0.66 |
| o-Cresol | 95-48-7 | 0.11 | 5.6 |
| m-Cresol (difficult to distinguish from p-cresol) | 108-39-4 | 0.77 | 5.6 |
| p-Cresol (difficult to distinguish from m-cresol) | 106-44-5 | 0.77 | 5.6 |
| Cyclohexanone | 108-94-1 | 0.36 | 0.75 mg/l TCLP |
| o,p’-DDD | 53-19-0 | 0.023 | 0.087 |
| p,p’-DDD | 72-54-8 | 0.023 | 0.087 |
| o,p’-DDE | 3424-82-6 | 0.031 | 0.087 |
| p,p’-DDE | 72-55-9 | 0.031 | 0.087 |
| o,p’-DDT | 789-02-6 | 0.0039 | 0.087 |
| p,p’-DDT | 50-29-3 | 0.0039 | 0.087 |
| Dibenz(a,h)anthracene | 53-70-3 | 0.055 | 8.2 |
| Dibenz(a,e)pyrene | 192-65-4 | 0.061 | NA |
| 1,2-Dibromo-3-chloropropane | 96-12-8 | 0.11 | 15 |
| 1,2-Dibromoethane/Ethylene dibromide | 106-93-4 | 0.028 | 15 |
| Dibromomethane | 74-95-3 | 0.11 | 15 |
| m-Dichlorobenzene | 541-73-1 | 0.036 | 6.0 |
| o-Dichlorobenzene | 95-50-1 | 0.088 | 6.0 |
| p-Dichlorobenzene | 106-46-7 | 0.090 | 6.0 |
| Dichlorodifluoromethane | 75-71-8 | 0.23 | 7.2 |
| 1,1-Dichloroethane | 75-34-3 | 0.059 | 6.0 |
| 1,2-Dichloroethane | 107-06-2 | 0.21 | 6.0 |
| 1,1-Dichloroethylene | 75-35-4 | 0.025 | 6.0 |
| trans-1,2-Dichloroethylene | 156-60-5 | 0.054 | 30 |
| 2,4-Dichlorophenol | 120-83-2 | 0.044 | 14 |
| 2,6-Dichlorophenol | 87-65-0 | 0.044 | 14 |
| 2,4-Dichlorophenoxyacetic acid/2,4-D | 94-75-7 | 0.72 | 10 |
| 1,2-Dichloropropane | 78-87-5 | 0.85 | 18 |
| cis-1,3-Dichloropropylene | 10061-01-5 | 0.036 | 18 |
| trans-1,3-Dichloropropylene | 10061-02-6 | 0.036 | 18 |
| Dieldrin | 60-57-1 | 0.017 | 0.13 |
| Diethyl phthalate | 84-66-2 | 0.20 | 28 |
| p-Dimethylaminoazobenzene | 60-11-7 | 0.13 | NA |
| 2,4-Dimethylaniline (2,4-xylidine) | 95-68-1 | 0.010 | 0.66 |
| 2-4-Dimethyl phenol | 105-67-9 | 0.036 | 14 |
| Dimethyl phthalate | 131-11-3 | 0.047 | 28 |
| Dimetilan | 644-64-4 | 0.056 | 1.4 |
| Di-n-butyl phthalate | 84-74-2 | 0.057 | 28 |
| 1,4-Dinitrobenzene | 100-25-4 | 0.32 | 2.3 |
| 4,6-Dinitro-o-cresol | 534-52-1 | 0.28 | 160 |
| 2,4-Dinitrophenol | 51-28-5 | 0.12 | 160 |
| 2,4-Dinitrotoluene | 121-14-2 | 0.32 | 140 |
| 2,6-Dinitrotoluene | 606-20-2 | 0.55 | 28 |
| Di-n-octyl phthalate | 117-84-0 | 0.017 | 28 |
| Di-n-propylnitrosamine | 621-64-7 | 0.40 | 14 |
| 1,4-Dioxane | 123-91-1 | 12.0 | 170 |
| Diphenylamine (difficult to distinguish from diphenylnitrosamine) | 122-39-4 | 0.92 | 13 |
| Diphenylnitrosamine (difficult to distinguish from diphenylamine) | 86-30-6 | 0.92 | 13 |
| 1,2-Diphenylhydrazine | 122-66-7 | 0.087 | NA |
| Disulfoton | 298-04-4 | 0.017 | 6.2 |
| Endosulfan I | 959-98-8 | 0.023 | 0.066 |
| Endosulfan II | 33213-65-9 | 0.029 | 0.13 |
| Endosulfan sulfate | 1031-07-8 | 0.029 | 0.13 |
| Endrin | 72-20-8 | 0.0028 | 0.13 |
| Endrin aldehyde | 7421-93-4 | 0.025 | 0.13 |
| Ethyl acetate | 141-78-6 | 0.34 | 33 |
| Ethyl benzene | 100-41-4 | 0.057 | 10 |
| Ethyl cyanide/Propanenitrile | 107-12-0 | 0.24 | 360 |
| Ethyl ether | 60-29-7 | 0.12 | 160 |
| bis(2-Ethylhexyl) phthalate | 117-81-7 | 0.28 | 28 |
| Ethyl methacrylate | 97-63-2 | 0.14 | 160 |
| Ethylene oxide | 75-21-8 | 0.12 | NA |
| Famphur | 52-85-7 | 0.017 | 15 |
| Fluoranthene | 206-44-0 | 0.068 | 3.4 |
| Fluorene | 86-73-7 | 0.059 | 3.4 |
| Heptachlor | 76-44-8 | 0.0012 | 0.066 |
| Heptachlor epoxide | 1024-57-3 | 0.016 | 0.066 |
| 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin(1,2,3,4,6,7,8-HpCDD) (6/02) | 35822-46-9 | 0.000035 | 0.0025 |
| 1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF) (6/02) | 67562-39-4 | 0.000035 | 0.0025 |
| 1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF) (6/02) | 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 |
| 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 methansulfonate | 66-27-3 | 0.018 | NA |
| Methyl parathion | 298-00-0 | 0.014 | 4.6 |
| Naphthalene | 91-20-3 | 0.059 | 5.6 |
| 2-Naphthylamine | 91-59-8 | 0.52 | NA |
| o-Nitroaniline | 88-74-4 | 0.27 | 14 |
| p-Nitroaniline | 100-01-6 | 0.028 | 28 |
| Nitrobenzene | 98-95-3 | 0.068 | 14 |
| 5-Nitro-o-toluidine | 99-55-8 | 0.32 | 28 |
| o-Nitrophenol | 88-75-5 | 0.028 | 13 |
| p-Nitrophenol | 100-02-7 | 0.12 | 29 |
| N-Nitrosodiethylamine | 55-18-5 | 0.40 | 28 |
| N-Nitrosodimethylamine | 62-75-9 | 0.40 | 2.3 |
| N-Nitroso-di-n-butylamine | 924-16-3 | 0.40 | 17 |
| N-Nitrosomethylethylamine | 10595-95-6 | 0.40 | 2.3 |
| N-Nitrosomorpholine | 59-89-2 | 0.40 | 2.3 |
| N-Nitrosopiperidine | 100-75-4 | 0.013 | 35 |
| N-Nitrosopyrrolidine | 930-55-2 | 0.013 | 35 |
| 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (OCDD) (6/02) | 3268-87-9 | 0.000063 | 0.005 |
| 1,2,3,4,6,7,8,9-Octachlorodibenzofuran (OCDF) (6/02) | 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 |
| o-Phenylenediamine | 95-54-5 | 0.056 | 5.6 |
| 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 |
| Trichloromonofluoromethane | 75-69-4 | 0.020 | 30 |
| 2,4,5-Trichlorophenol | 95-95-4 | 0.18 | 7.4 |
| 2,4,6-Trichlorophenol | 88-06-2 | 0.035 | 7.4 |
| 2,4,5-Trichlorophenoxyacetic acid/2,4,5-T | 93-76-5 | 0.72 | 7.9 |
| 1,2,3-Trichloropropane | 96-18-4 | 0.85 | 30 |
| 1,1,2-Trichloro-1,2,2-trifluoroethane | 76-13-1 | 0.057 | 30 |
| tris-(2,3-Dibromopropyl) phosphate | 126-72-7 | 0.11 | 0.10 |
| Vinyl chloride | 75-01-4 | 0.27 | 6.0 |
| Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) | 1330-20-7 | 0.32 | 30 |
| Inorganic Constituents | |||
| Antimony | 7440-36-0 | 1.9 | 1.15 mg/l TCLP |
| Arsenic | 7440-38-2 | 1.4 | 5.0 mg/l TCLP |
| Barium | 7440-39-3 | 1.2 | 21 mg/l TCLP |
| Beryllium | 7440-41-7 | 0.82 | 1.22 mg/l TCLP |
| Cadmium | 7440-43-9 | 0.69 | 0.11 mg/l TCLP |
| Chromium (Total) | 7440-47-3 | 2.77 | 0.60 mg/l TCLP |
| Cyanides (Total)4 | 57-12-5 | 1.2 | 590 |
| Cyanides (Amenable)4 | 57-12-5 | 0.86 | 30 |
| Fluoride5 | 16984-48-8 | 35 | NA |
| Lead | 7439-92-1 | 0.69 | 0.75 mg/l TCLP |
| Mercury - Nonwastewater from Retort | 7439-97-6 | NA | 0.20 mg/l TCLP |
| Mercury - All Others | 7439-97-6 | 0.15 | 0.025 mg/lTCLP |
| Nickel | 7440-02-0 | 3.98 | 11. mg/l TCLP |
| Selenium7 | 7782-49-2 | 0.82 | 5.7 mg/l TCLP |
| Silver | 7440-22-4 | 0.43 | 0.14 mg/l TCLP |
| Sulfide5 | 18496-25-8 | 14 | NA |
| Thallium | 7440-28-0 | 1.4 | 0.20 mg/l TCLP |
| Vanadium5 | 7440-62-2 | 4.3 | 1.6 mg/l TCLP |
| Zinc5 | 7440-66-6 | 2.61 | 4.3 mg/l TCLP |
| FOOTNOTES TO TABLE UTS - * Note: N/A means “not applicable.” | |||
| 1. CAS means Chemical Abstract Services. When the waste code and/or regulated constituents are described as a combination of a chemical with 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, in part, based upon incineration in units operated in accordance with the technical requirements of 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 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 9010 or 9012, found in Test Methods for Evaluating Solid Waste, Physical/Chemical Methods, EPA Publication SW-846, as incorporated by reference in 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 8/00] | |||
| 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 treated selenium waste would always be characteristically hazardous, unless it is treated to below its characteristic level. | |||
| 8. This standard is temporarily deferred for soil exhibiting a hazardous characteristic due to D004-D011 only. |
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 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 placed into any given land disposal unit or, in the case of an accidental spill, the date of the spill. |
(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 268.48.
(1) All soils. Prior to land disposal, all constituents subject to treatment must by treated as follows:
(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:
(e) Management of treatment residual. Treatment residuals from treating contaminated soil identified by paragraph (a) of this section as needing to comply with LDRs must be managed as follows:
(2) Non-soil residuals are subject to:
(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.
SUBPART E
Prohibitions on Storage
268.50. Prohibitions on storage of restricted wastes.
(a) Except as provided for in this section, the storage of hazardous wastes restricted from land disposal under subpart C of this part is prohibited, unless the following conditions are met:
(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: (amended 11/90, 12/92)
(i) Each container is clearly marked to identify its contents and with:
(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. 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). 268 Appendix III consists of the following compounds:
35. Vinyl Chloride
II. Semivolatiles
33. Tris(2,3-dibromopropyl)phosphate
III. Organochlorine Pesticides
20. Toxaphene
IV. Phenoxyacetic Acid Herbicides
8. PCBs not otherwise specified
VI. Dioxins and Furans
7. 2,3,7,8-Tetrachlorodibenzo-p-dioxin
Appendix IV. Wastes Excluded From Lab Packs Under the Alternative Treatment Standards of 268.42(c): (major revision 5/96)
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. 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 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 | Nonwaste- waters | Waste- waters | |
| 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 |
| FOOTNOTE: Note: “n.a.” stands for “not applicable”; “fb.” stands for “followed by”. |
Appendix VII . [Effective dates].
| Table 1.—Effective Dates of Surface Disposed Wastes (Non-Soil and Debris) Regulated in the LDRsa—Comprehensive List | ||
| D001c | All (except High TOC Ignitable Liquids) | Aug. 9, 1993. |
| D001 | High TOC Ignitable Liquids | Aug. 8, 1990. |
| D002c | All | Aug. 9, 1993. |
| D003e | All | July 8, 1996. |
| D004 | Nonwastewater | May 8, 1992. |
| D004 | Wastewater | Aug. 8, 1992. |
| D005 | All | Aug. 8, 1990. |
| D006 | All | Aug. 8, 1990. |
| D007 | All | Aug. 8, 1990. |
| D008 | Lead materials before secondary smelting | May 8, 1992. |
| D008 | All others | Aug. 8, 1990. |
| D009 | Nonwastewater | May 8, 1992. |
| D009 | All others | Aug. 8, 1990. |
| D010 | All | Aug. 8, 1990. |
| D011 | All | Aug. 8, 1990. |
| 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 | May 12, 1997 |
| F033 | Mixed with radioactive wastes | May 12, 1999 |
| F033 | All others | May 12, 1997 |
| F034 | Mixed with radioactive wastes | May 12, 1999 |
| F034 | All others | May 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 | Nonwastewate | 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 | 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 | Mixed with radioactive waste | Apr. 8, 1998. |
| K088 | All others | Jan. 8, 1997. |
| K093 | All | June 8, 1989. |
| K094 | All | June 8, 1989. |
| K095 | Wastewater | Aug. 8, 1990. |
| K095 | Nonwastewate | 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 other | Nov. 9, 1992. |
| K112 | Mixed with radioactive wastes | June 30, 1994. |
| K112 | All other | 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 | 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 waste | 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. |
| U202 | 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. |
| aThis 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. | ||
| bThe standard was revised in the Third Third Final Rule (55 FR 22520, June 1, 1990). | ||
| cThe standard was revised in the Third Third Emergency Rule (58 FR 29860, May 24, 1993); the original effective date was August 8, 1990. | ||
| dThe standard was revised in the Phase II Final Rule (59 FR 47982, Sept. 19, 1994); the original effective date was August 8, 1990. | ||
| eThe 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 Contamination Soil and Debris (CSD)
| Restricted hazardous waste in CSD | Effective date | |
| 1. | Solvent-(F001-F005) and dioxin-(F020-5023 and F026-F028) containing soil and debris from CERCLA response of 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. | Soil and debris contaminated with California list HOC’s from CERCLA response or RCRA corrective actions. | Nov. 8, 1990. |
| 4. | Soil and debris contaminated with California list HOC’s not from CERCLA response or RCRA corrective actions. | July 8, 1989. |
| 5. | All soil and debris contaminated with First Third wastes for which treatment standards are based on incineration. | Aug. 8, 1990. |
| 6. | All soil and debris contaminated with Second Third wastes for which treatment standards are based on incineration. | June 8, 1991. |
| 7. | 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. |
Note: 1. Appendix VII is provided for the convenience of the reader.
2. Contaminated Soil and Debris Rule will be promulgated in the future.
Appendix VIII. National Capacity LDR Variance for UIC Wastes
| National Capacity LDR Variances for UIC WastesA | ||
| 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). | All | Feb. 10, 1994. |
| D001 (High TOC Ignitable Characteristic Liquids Subcategory). | Nonwastewater | Sept. 19, 1995. |
| D002B | All | May 8, 1992. |
| D002B | 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. |
| 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. |
| AWastes that are deep well disposed on-site receive a six-month variance, with restrictions effective in November 1990. | ||
| BDeepwell injected D002 liquids with a pH less than 2 must meet the Carolina List treatment standards on August 8, 1990. |
Note: This table is provided for the convenience of the reader.
Appendix IX. Extraction Procedure (EP) Toxicity Test Method and Structural Integrity Test (SW-846, Method 1310A)
Note: Appendix IX - Removed upon promulgation of SW-846; remove from SC Text 12/92.
Note: The EP (Method 1310) is published in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” EPA Publication SW-846, as incorporated by reference in R. 61-79.260.11.
Appendix XI. Metal Bearing Wastes Prohibited From Dilution in a Combustion Unit According to 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 H3AsO4 |
| P011 | Arsenic oxide As2O5 |
| 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 (I) selenite |
| P115 | Thallium (I) sulfate |
| P119 | Ammonium vanadate |
| P120 | Vanadium oxide V2O5 |
| 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. |
1A combustion unit is defined as any thermal technology subject to part 264, subpart O; Part 265, subpart O; and/or 266, subpart H.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 16, Issue No. 12, eff December 25, 1992; State Register Volume 17, Issue No. 12, eff December 24, 1993; State Register Volume 20, Issue No. 5, eff May 24, 1996; State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998; State Register Volume 23, Issue No. 11, eff November 26, 1999; State Register Volume 24, Issue No. 8, eff August 25, 2000; State Register Volume 31, Issue No. 6, eff June 22, 2007; SCSR 43-5 Doc. No. 4841, eff May 24, 2019; SCSR 45-5 Doc. No. 4975, eff May 28, 2021.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 16, Issue No. 12, eff December 25, 1992; State Register Volume 17, Issue No. 12, eff December 24, 1993; State Register Volume 20, Issue No. 5, eff May 24, 1996; State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998; State Register Volume 23, Issue No. 11, eff November 26, 1999; State Register Volume 24, Issue No. 8, eff August 25, 2000.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 16, Issue No. 12, eff December 25, 1992; State Register Volume 17, Issue No. 12, eff December 24, 1993; State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998; State Register Volume 23, Issue No. 11, eff November 26, 1999.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998; State Register Volume 23, Issue No. 11, eff November 26, 1999.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 16, Issue No. 12, eff December 25, 1992; State Register Volume 17, Issue No. 12, eff December 24, 1993.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 16, Issue No. 12, eff December 25, 1992; State Register Volume 17, Issue No. 12, eff December 24, 1993.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 16, Issue No. 12, eff December 25, 1992; State Register Volume 17, Issue No. 12, eff December 24, 1993; State Register Volume 18, Issue No. 12, eff December 23, 1994; State Register Volume 20, Issue No. 5, eff May 24, 1996; State Register Volume 20, Issue No. 12, eff December 27, 1996; State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998; State Register Volume 23, Issue No. 11, eff November 26, 1999; State Register Volume 24, Issue No. 8, eff August 25, 2000; State Register Volume 25, Issue No. 10, eff October 26, 2001; State Register Volume 28, Issue No. 6, eff June 25, 2004; State Register Volume 32, Issue No. 6, eff June 27, 2008; State Register Volume 36, Issue No. 9, eff September 28, 2012; SCSR 43-5 Doc. No. 4841, eff May 24, 2019; SCSR 44-11 Doc. No. 4976, eff November 27, 2020; SCSR 46-5 Doc. No. 5058, eff May 27, 2022.
HISTORY: Added by State Register Volume 16, Issue No. 12, eff December 25, 1992. Amended by State Register Volume 17, Issue No. 12, eff December 24, 1993; State Register Volume 20, Issue No. 5, eff May 24, 1996; State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998; State Register Volume 24, Issue No. 8, eff August 25, 2000; State Register Volume 32, Issue No. 6, eff June 27, 2008; SCSR 46-5 Doc. No. 5058, eff May 27, 2022.
HISTORY: Amended by State Register Volume 16, Issue No. 12, eff December 25, 1992.
HISTORY: Added by State Register Volume 17, Issue No. 12, eff December 24, 1993.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 16, Issue No. 12, eff December 25, 1992, State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990.
HISTORY: Added by State Register Volume 26, Issue No. 6, Part 1, eff June 28, 2002.
HISTORY: Added by State Register Volume 26, Issue No. 6, Part 1, eff June 28, 2002.
HISTORY: Added by State Register Volume 23, Issue No. 11, eff November 26, 1999. Amended by State Register Volume 24, Issue No. 8, eff August 25, 2000.
HISTORY: Added by State Register Volume 24, Issue No. 8, eff August 25, 2000.
HISTORY: Added by State Register Volume 27, Issue No. 6, Part 1, eff June 27, 2003.
HISTORY: Added by State Register Volume 17, Issue No. 12, eff December 24, 1993.
HISTORY: Added by State Register Volume 20, Issue No. 5, eff May 24, 1996.
HISTORY: Added by State Register 22, Issue No. 9, Part 2, eff September 2, 1998. Amended by State Register Volume 24, Issue No. 8, eff August 25, 2000.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 16, Issue No. 12, eff December 25, 1992; State Register Volume 17, Issue No. 12, eff December 24, 1993; State Register Volume 20, Issue No. 5, eff May 24, 1996; State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998; State Register Volume 23, Issue No. 11, eff November 26, 1999; State Register Volume 24, Issue No. 8, eff August 25, 2000; State Register Volume 25, Issue No. 10, eff October 26, 2001; State Register Volume 26, Issue No. 6, Part 1, eff June 28, 2002; State Register Volume 27, Issue No. 6, Part 1, eff June 27, 2003; State Register Volume 28, Issue No. 6, eff June 25, 2004; State Register Volume 31, Issue No. 2, eff February 23, 2007; Amended by State Register Volume 36, Issue No. 9, eff September 28, 2012; State Register Volume 39, Issue No. 6, Doc. No. 4541, eff June 26, 2015; SCSR 46-5 Doc. No. 5058, eff May 27, 2022.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 16, Issue No. 12, eff December 25, 1992; State Register Volume 17, Issue No. 12, eff December 24, 1993; State Register Volume 20, Issue No. 5, eff May 24, 1996.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 16, Issue No. 12, eff December 25, 1992; State Register Volume 17, Issue No. 12, eff December 24, 1993; State Register Volume 18, Issue No. 12, eff December 23, 1994; State Register Volume 20, Issue No. 5, eff May 24, 1996; State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998; State Register Volume 23, Issue No. 11, eff November 26, 1999.
HISTORY: Added by State Register Volume 14, Issue No. 11, eff November 23, 1990; amended by State Register Volume 16, Issue No. 12, eff December 25, 1992; State Register Volume 17, Issue No. 12, eff December 24, 1993; State Register Volume 20, Issue No. 5, eff May 24, 1996.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 16, Issue No. 12, eff December 25, 1992; State Register Volume 17, Issue No. 12, eff December 24, 1993; State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998; State Register Volume 23, Issue No. 11, eff November 26, 1999.
HISTORY: Added by State Register Volume 17, Issue No. 12, eff December 24, 1993. Amended by State Register Volume 20, Issue No. 5, eff May 24, 1996; State Register Volume 23, Issue No. 11, eff November 26, 1999.
HISTORY: Added by State Register Volume 17, Issue No. 12, eff December 24, 1993; amended by State Register Volume 20, Issue No. 5, eff May 24, 1996.
HISTORY: Added by the State Register Volume 20, Issue No. 5, eff May 24, 1996. Amended by State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998; State Register Volume 23, Issue No. 11, eff November 26, 1999; State Register Volume 24, Issue No. 8, eff August 25, 2000; State Register Volume 25, Issue No. 10, eff October 26, 2001; State Register Volume 26, Issue No. 6, Part 1, eff June 28, 2002; State Register Volume 31, Issue No. 2, eff February 23, 2007; State Register Volume 36, Issue No. 9, eff September 28, 2012; State Register Volume 39, Issue No. 6, Doc. No. 4541, eff June 26, 2015.
HISTORY: Added by State Register Volume 23, Issue No. 11, eff November 26, 1999. Amended by State Register Volume 24, Issue No. 8, eff August 25, 2000; State Register Volume 25, Issue No. 10, eff October 26, 2001; State Register Volume 26, Issue No. 6, Part 1, eff June 28, 2002.
HISTORY: Amended by State Register Volume 14, Issue No. 11, eff November 23, 1990; State Register Volume 16, Issue No. 12, eff December 25, 1992; State Register Volume 17, Issue No. 12, eff December 24, 1993; State Register Volume 24, Issue No. 8, eff August 25, 2000; SCSR 43-5 Doc. No. 4841, eff May 24, 2019; SCSR 44-11 Doc. No. 4976, eff November 27, 2020; SCSR 46-5 Doc. No. 5058, eff May 27, 2022.
HISTORY: Added by State Register Volume 26, Issue No. 6, Part 1, eff June 28, 2002.
HISTORY: Added by State Register Volume 16, Issue No. 12, eff December 25, 1992; amended by State Register Volume 17, Issue No. 12, eff December 24, 1993; State Register Volume 20, Issue No. 5, eff May 24, 1996.
HISTORY: Added by State Register Volume 16, Issue No. 12, eff December 25, 1992; Amended by State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998.
HISTORY: Added by State Register Volume 16, Issue No. 12, eff December 25, 1992; Amended by State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998.
HISTORY: Added by State Register Volume 16, Issue No. 12, eff December 25, 1992; Amended by State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998.
HISTORY: Added by State Register Volume 22, Issue No. 9, Part 2, eff September 25, 1998.