|
ILLINOIS POLLUTION CONTROL BOARD
June 5, 2003
IN THE MATTER OF: | ) | |
) | R03-18 | |
RCRA SUBTITLE C UPDATE, USEPA | ) | (Identical-in-Substance |
AMENDMENTS (July 1, 2002 through | ) | Rulemaking - Land) |
December 31, 2002) | ) | |
Adopted Rule. Final Order.
ORDER OF THE BOARD (by M.E. Tristano):
This identical-in-substance rulemaking updates the Illinois hazardous waste regulations to incorporate revisions to the federal regulations. The United States Environmental Protection Agency (USEPA) made the federal amendments that prompted this action during the period of July 1, 2002 through December 31, 2002. This proceeding adopts amendments to 35 Ill. Adm. Code 703, 720, 721, 726, and 728. This adoption also makes a series of non-substantive corrections and stylistic revisions to segments of the text of 35 Ill. Adm. Code 720, 721, 726, and 728 that are not otherwise affected by the covered federal amendments.
Sections 7.2 and 22.4(a) of the Environmental Protection Act (Act) (415 ILCS 5/7.2 and 22.4(a) (2002)) require the Board to adopt regulations that are “identical in substance” to hazardous waste regulations adopted by the USEPA. These USEPA rules implement Subtitle C of the federal Resource Conservation and Recovery Act of 1976 (RCRA Subtitle C) (42 U.S.C. §§ 6921 et seq. (2000)).
Sections 7.2 and 22.4(a) provide for quick adoption of regulations that are identical in substance to federal regulations that USEPA adopts to implement Sections 3001 through 3005 of RCRA (42 U.S.C. §§ 6921-6925 (2000)). Section 22.4(a) also provides that Title VII of the Act and Section 5 of the Administrative Procedure Act (APA) (5 ILCS 100/5-35 and 5-40 (2002)) do not apply to the Board’s adoption of identical-in-substance regulations. The federal RCRA Subtitle C regulations are found at 40 C.F.R. 260 through 266, 268, 270, 271, 273, and 279.
This order is supported by an opinion that the Board also adopts today. The Board will cause the proposed amendments to be published in the Illinois Register and will hold the docket open to receive public comments for 45 days after the date of publication.
IT IS SO ORDERED.
I, Dorothy M. Gunn, Clerk of the Illinois Pollution Control Board, certify that the Board adopted the above order on June 5, 2003, by a vote of 6-0.
Dorothy M. Gunn, Clerk
Illinois Pollution Control Board
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER b: PERMITS
PART 703
RCRA PERMIT PROGRAM
SUBPART A: GENERAL PROVISIONS
Section
703.100 | Scope and Relation to Other Parts |
703.101 | Purpose |
703.110 | References |
SUBPART B: PROHIBITIONS
Section
703.120 | Prohibitions in General |
703.121 | RCRA Permits |
703.122 | Specific Inclusions in Permit Program |
703.123 | Specific Exclusions from Permit Program |
703.124 | Discharges of Hazardous Waste |
703.125 | Reapplications |
703.126 | Initial Applications |
703.127 | Federal Permits (Repealed) |
SUBPART C: AUTHORIZATION BY RULE AND INTERIM STATUS
Section
703.140 | Purpose and Scope |
703.141 | Permits by Rule |
703.150 | Application by Existing HWM Facilities and Interim Status Qualifications |
703.151 | Application by New HWM Facilities |
703.152 | Amended Part A Application |
703.153 | Qualifying for Interim Status |
703.154 | Prohibitions During Interim Status |
703.155 | Changes During Interim Status |
703.156 | Interim Status Standards |
703.157 | Grounds for Termination of Interim Status |
703.158 | Permits for Less Than an Entire Facility |
703.159 | Closure by Removal |
703.160 | Procedures for Closure Determination |
703.161 | Enforceable Document for Post-Closure Care |
SUBPART D: APPLICATIONS
Section
703.180 | Applications in General |
703.181 | Contents of Part A |
703.182 | Contents of Part B |
703.183 | General Information |
703.184 | Facility Location Information |
703.185 | Groundwater Protection Information |
703.186 | Exposure Information |
703.187 | Solid Waste Management Units |
703.188 | Other Information |
703.191 | Public Participation: Pre-Application Public Notice and Meeting |
703.192 | Public Participation: Public Notice of Application |
703.193 | Public Participation: Information Repository |
703.200 | Specific Part B Application Information |
703.201 | Containers |
703.202 | Tank Systems |
703.203 | Surface Impoundments |
703.204 | Waste Piles |
703.205 | Incinerators that Burn Hazardous Waste |
703.206 | Land Treatment |
703.207 | Landfills |
703.208 | Boilers and Industrial Furnaces Burning Hazardous Waste |
703.209 | Miscellaneous Units |
703.210 | Process Vents |
703.211 | Equipment |
703.212 | Drip Pads |
703.213 | Air Emission Controls for Tanks, Surface Impoundments, and Containers |
703.214 | Post-Closure Care Permits |
SUBPART E: SHORT TERM AND PHASED PERMITS
Section
703.220 | Emergency Permits |
703.221 | Alternative Compliance with the Federal NESHAPS |
703.222 | Incinerator Conditions Prior to Trial Burn |
703.223 | Incinerator Conditions During Trial Burn |
703.224 | Incinerator Conditions After Trial Burn |
703.225 | Trial Burns for Existing Incinerators |
703.230 | Land Treatment Demonstration |
703.231 | Research, Development and Demonstration Permits |
703.232 | Permits for Boilers and Industrial Furnaces Burning Hazardous Waste |
703.234 | Remedial Action Plans |
SUBPART F: PERMIT CONDITIONS OR DENIAL
Section
703.240 | Permit Denial |
703.241 | Establishing Permit Conditions |
703.242 | Noncompliance Pursuant to Emergency Permit |
703.243 | Monitoring |
703.244 | Notice of Planned Changes (Repealed) |
703.245 | Twenty-four Hour Reporting |
703.246 | Reporting Requirements |
703.247 | Anticipated Noncompliance |
703.248 | Information Repository |
SUBPART G: CHANGES TO PERMITS
Section
703.260 | Transfer |
703.270 | Modification |
703.271 | Causes for Modification |
703.272 | Causes for Modification or Reissuance |
703.273 | Facility Siting |
703.280 | Permit Modification at the Request of the Permittee |
703.281 | Class 1 Modifications |
703.282 | Class 2 Modifications |
703.283 | Class 3 Modifications |
SUBPART H: REMEDIAL ACTION PLANS
Section
703.300 | Special Regulatory Format |
703.301 | General Information |
703.302 | Applying for a RAP |
703.303 | Getting a RAP Approved |
703.304 | How a RAP May Be Modified, Revoked and Reissued, or Terminated |
703.305 | Operating Under A RAP |
703.306 | Obtaining a RAP for an Off-Site Location |
SUBPART I: INTEGRATION WITH MAXIMUM ACHIEVABLE CONTROL TECHNOLOGY (MACT) STANDARDS
Section |
703.320 | Options for Incinerators and Cement and Lightweight Aggregate Kilns to Minimize Emissions from Startup, Shutdown, and Malfunction Events |
Classification of Permit Modifications | |
AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].
SOURCE: Adopted in R82-19 at 7 Ill. Reg. 14289, effective October 12, 1983; amended in R83-24 at 8 Ill. Reg. 206, effective December 27, 1983; amended in R84-9 at 9 Ill. Reg. 11899, effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 1110, effective January 2, 1986; amended in R85-23 at 10 Ill. Reg. 13284, effective July 28, 1986; amended in R86-1 at 10 Ill. Reg. 14093, effective August 12, 1986; amended in R86-19 at 10 Ill. Reg. 20702, effective December 2, 1986; amended in R86-28 at 11 Ill. Reg. 6121, effective March 24, 1987; amended in R86-46 at 11 Ill. Reg. 13543, effective August 4, 1987; amended in R87-5 at 11 Ill. Reg. 19383, effective November 12, 1987; amended in R87-26 at 12 Ill. Reg. 2584, effective January 15, 1988; amended in R87-39 at 12 Ill. Reg. 13069, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 447, effective December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18477, effective November 13, 1989; amended in R89-9 at 14 Ill. Reg. 6278, effective April 16, 1990; amended in R90-2 at 14 Ill. Reg. 14492, effective August 22, 1990; amended in R90-11 at 15 Ill. Reg. 9616, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14554, effective September 30, 1991; amended in R91-13 at 16 Ill. Reg. 9767, effective June 9, 1992; amended in R92-10 at 17 Ill. Reg. 5774, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20794, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6898, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12392, effective July 29, 1994; amended in R94-5 at 18 Ill. Reg. 18316, effective December 20, 1994; amended in R95-6 at 19 Ill. Reg. 9920, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 11225, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 553, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7632, effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17930, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 2153, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9381, effective July 26, 1999; amended in R00-13 at 24 Ill. Reg. 9765, effective June 20, 2000; amended in R01-21/R01-23 at 25 Ill. Reg. 9313, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. 6539, effective April 22, 2002; amended in R03-7 at 27 Ill. Reg. 3496, effective February 14, 2003; amended in R03-18 at 27 Ill. Reg. ________, effective ______________________.
SUBPART D: APPLICATIONS
Section 703.205 | Incinerators that Burn Hazardous Waste |
For a facility that incinerates hazardous waste, except as 35 Ill. Adm. Code 724.440 and subsection (e) of this Section provide otherwise, the applicant must fulfill the requirements of subsection (a), (b), or (c) of this Section in completing the Part B application.
a) | When seeking exemption under 35 Ill. Adm. Code 724.440(b) or (c) (ignitable, corrosive, or reactive wastes only), the following requirements: |
1) | Documentation that the waste is listed as a hazardous waste in Subpart D of 35 Ill. Adm. Code 721 solely because it is ignitable (Hazard Code I), corrosive (Hazard Code C), or both; |
2) | Documentation that the waste is listed as a hazardous waste in Subpart D of 35 Ill. Adm. Code 721 solely because it is reactive (Hazard Code R) for characteristics other than those listed in 35 Ill. Adm. Code 721.123(a)(4) and (a)(5) and will not be burned when other hazardous wastes are present in the combustion zone; |
3) | Documentation that the waste is a hazardous waste solely because it possesses the characteristic of ignitability or corrosivity, or both, as determined by the tests for characteristics of hazardous wastes under Subpart C of 35 Ill. Adm. Code 721; or |
4) | Documentation that the waste is a hazardous waste solely because it possesses the reactivity characteristics listed in 35 Ill. Adm. Code 721.123(a)(1) through (a)(3) or (a)(6) through (a)(8), and that it will not be burned when other hazardous wastes are present in the combustion zone. |
b) | Submit a trial burn plan or the results of a trial burn, including all required determinations, in accordance with Section 703.222 et seq. |
c) | In lieu of a trial burn, the applicant may submit the following information: |
1) | An analysis of each waste or mixture of wastes to be burned including the following: |
A) | Heat value of the waste in the form and composition in which it will be burned; |
B) | Viscosity (if applicable) or description of physical form of the waste; |
C) | An identification of any hazardous organic constituents listed in Appendix H to 35 Ill. Adm. Code 721 that are present in the waste to be burned, except that the applicant need not analyze for constituents listed in Appendix H to 35 Ill. Adm. Code 721 that would reasonably not be expected to be found in the waste. The constituents excluded from analysis must be identified and the basis for their exclusion stated. The waste analysis must rely on analytical techniques specified in “Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods,” USEPA Publication SW-846, as incorporated by reference at 35 Ill. Adm. Code 720.111, or their equivalent; |
D) | An approximate quantification of the hazardous constituents identified in the waste, within the precision produced by the analytical methods specified in “Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods,” USEPA Publication SW-846, as incorporated by reference at 35 Ill. Adm. Code 720.111; and |
E) | A quantification of those hazardous constituents in the waste that may be designated as POHCs based on data submitted from other trial or operational burns that demonstrate compliance with the performance standard in 35 Ill. Adm. Code 724.443; |
2) | A detailed engineering description of the incinerator, including the following: |
A) | Manufacturer’s name and model number of incinerator; |
B) | Type of incinerator; |
C) | Linear dimension of incinerator unit including cross sectional area of combustion chamber; |
D) | Description of auxiliary fuel system (type/feed); |
E) | Capacity of prime mover; |
F) | Description of automatic waste feed cutoff systems; |
G) | Stack gas monitoring and pollution control monitoring system; |
H) | Nozzle and burner design; |
I) | Construction materials; and |
J) | Location and description of temperature, pressure and flow indicating devices and control devices; |
3) | A description and analysis of the waste to be burned compared with the waste for which data from operational or trial burns are provided to support the contention that a trial burn is not needed. The data should include those items listed in subsection (c)(1) of this Section. This analysis should specify the POHCs that the applicant has identified in the waste for which a permit is sought, and any differences from the POHCs in the waste for which burn data are provided; |
4) | The design and operating conditions of the incinerator unit to be used, compared with that for which comparative burn data are available; |
5) | A description of the results submitted from any previously conducted trial burns, including the following: |
A) | Sampling and analysis techniques used to calculate performance standards in 35 Ill. Adm. Code 724.443; |
B) | Methods and results of monitoring temperatures, waste feed rates, carbon monoxide, and an appropriate indicator of combustion gas velocity (including a statement concerning the precision and accuracy of this measurement); and |
C) | The certification and results required by subsection (b) of this Section; |
6) | The expected incinerator operation information to demonstrate compliance with 35 Ill. Adm. Code 724.443 and 724.445, including the following: |
A) | Expected carbon monoxide (CO) level in the stack exhaust gas; |
B) | Waste feed rate; |
C) | Combustion zone temperature; |
D) | Indication of combustion gas velocity; |
E) | Expected stack gas volume, flow rate, and temperature; |
F) | Computed residence time for waste in the combustion zone; |
G) | Expected hydrochloric acid removal efficiency; |
H) | Expected fugitive emissions and their control procedures; and |
I) | Proposed waste feed cut-off limits based on the identified significant operating parameters; |
7) | The Agency may, pursuant to 35 Ill. Adm. Code 705.122, request such additional information as may be necessary for the Agency to determine whether the incinerator meets the requirements of Subpart O of 35 Ill. Adm. Code 724 and what conditions are required by that Subpart and Section 39(d) of the Environmental Protection Act [415 ILCS 5/39(d)]; and |
8) | Waste analysis data, including that submitted in subsection (c)(1) of this Section, sufficient to allow the Agency to specify as permit Principal Organic Hazardous Constituents (permit POHCs) those constituents for which destruction and removal efficiencies will be required. |
d) | The Agency must approve a permit application without a trial burn if it finds the following: |
1) | The wastes are sufficiently similar; and |
2) | The incinerator units are sufficiently similar, and the data from other trial burns are adequate to specify (under 35 Ill. Adm. Code 724.445) operating conditions that will ensure that the performance standards in 35 Ill. Adm. Code 724.443 will be met by the incinerator. |
e) | When an owner or operator demonstrates compliance with the air emission standards and limitations of the federal National Emission Standards for Hazardous Air Pollutants (NESHAPs) in 40 CFR 63, subpart EEE, incorporated by reference in 35 Ill. Adm. Code 720.111 (i.e., by conducting a comprehensive performance test and submitting a Notification of Compliance under 40 CFR 63.1207(j) and 63.1210(b) documenting compliance with all applicable requirements of 40 CFR 63, subpart EEE), the requirements of this Section do not apply, except those provisions that the Agency determines are necessary to ensure compliance with 35 Ill. Adm. Code 724.445(a) and (c) if the owner or operator elects to comply with Section 703.320(a)(1)(A) to minimize emissions of toxic compounds from startup, shutdown, and malfunction events. Nevertheless, the Agency may apply the provisions of this Section, on a case-by-case basis, for purposes of information collection in accordance with Sections 703.188 and 703.241( |
BOARD NOTE: Operating conditions used to determine effective treatment of hazardous waste remain effective after the owner or operator demonstrates compliance with the standards of 40 CFR 63, subpart EEE.
BOARD NOTE: Derived from 40 CFR 270.19 (2002), as amended at 67 Fed. Reg. 77687 (December 19, 2002).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 703.208 | Boilers and Industrial Furnaces Burning Hazardous Waste |
When the owner or operator of a cement or lightweight aggregate kiln demonstrates compliance with the air emission standards and limitations of the federal National Emission Standards for Hazardous Air Pollutants (NESHAPs) in 40 CFR 63, subpart EEE, incorporated by reference in 35 Ill. Adm. Code 720.111 (i.e., by conducting a comprehensive performance test and submitting a Notification of Compliance under 40 CFR 63.1207(j) and 63.1210(b) documenting compliance with all applicable requirements of 40 CFR 63, subpart EEE), the requirements of this Section do not apply, except those provisions that the Agency determines are necessary to ensure compliance with 35 Ill. Adm. Code 726.202(e)(1) and (e)(2)(C) if the owner or operator elects to comply with Section 703.310(a)(1)(A) to minimize emissions of toxic compounds from startup, shutdown, and malfunction events. Nevertheless, the Agency may apply the provisions of this Section, on a case-by-case basis, for purposes of information collection in accordance with Sections 703.188 and 703.241(a)(2).
a) | Trial burns. |
1) | General. Except as provided below, an owner or operator that is subject to the standards to control organic emissions provided by 35 Ill. Adm. Code 726.204, standards to control particulate matter provided by 35 Ill. Adm. Code 726.205, standards to control metals emissions provided by 35 Ill. Adm. Code 726.206, or standards to control hydrogen chloride (HCl) or chlorine gas emissions provided by 35 Ill. Adm. Code 726.207 must conduct a trial burn to demonstrate conformance with those standards and must submit a trial burn plan or the results of a trial burn, including all required determinations, in accordance with Section 703.232. |
A) | Under subsections (a)(2) through (a)(5) of this Section and 35 Ill. Adm. Code 726.204 through 726.207, the Agency may waive a trial burn to demonstrate conformance with a particular emission standard; and |
B) | The owner or operator may submit data in lieu of a trial burn, as prescribed in subsection (a)(6) of this Section. |
2) | Waiver of trial burn of DRE (destruction removal efficiency). |
A) | Boilers operated under special operating requirements. When seeking to be permitted under 35 Ill. Adm. Code 726.204(a)(4) and 726.210, which automatically waive the DRE trial burn, the owner or operator of a boiler must submit documentation that the boiler operates under the special operating requirements provided by 35 Ill. Adm. Code 726.210. |
B) | Boilers and industrial furnaces burning low risk waste. When seeking to be permitted under the provisions for low risk waste provided by 35 Ill. Adm. Code 726.204(a)(5) and 726.209(a), which waive the DRE trial burn, the owner or operator must submit the following: |
i) | Documentation that the device is operated in conformance with the requirements of 35 Ill. Adm. Code 726.209(a)(1). |
ii) | Results of analyses of each waste to be burned, documenting the concentrations of nonmetal compounds listed in Appendix H to 35 Ill. Adm. Code 721, except for those constituents that would reasonably not be expected to be in the waste. The constituents excluded from analysis must be identified and the basis for their exclusion explained. The analysis must rely on analytical techniques specified in Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods, incorporated by reference in 35 Ill. Adm. Code 720.111. |
iii) | Documentation of hazardous waste firing rates and calculations of reasonable, worst-case emission rates of each constituent identified in subsection (a)(2)(B)(ii) of this Section using procedures provided by 35 Ill. Adm. Code 726.209(a)(2)(B). |
iv) | Results of emissions dispersion modeling for emissions identified in subsection (a)(2)(B)(iii) of this Section using modeling procedures prescribed by 35 Ill. Adm. Code 726.206(h). The Agency must review the emission modeling conducted by the applicant to determine conformance with these procedures. The Agency must either approve the modeling or determine that alternate or supplementary modeling is appropriate. |
v) | Documentation that the maximum annual average ground level concentration of each constituent identified in subsection (a)(2)(B)(ii) of this Section quantified in conformance with subsection (a)(2)(B)(iv) of this Section does not exceed the allowable ambient level established in Appendix D or E to 35 Ill. Adm. Code 726. The acceptable ambient concentration for emitted constituents for which a specific reference air concentration has not been established in Appendix D to 35 Ill. Adm. Code 726 or risk-specific doses has not been established in Appendix E to 35 Ill. Adm. Code 726 is 0.1 micrograms per cubic meter, as noted in the footnote to Appendix D to 35 Ill. Adm. Code 726. |
3) | Waiver of trial burn for metals. When seeking to be permitted under the Tier I (or adjusted Tier I) metals feed rate screening limits provided by 35 Ill. Adm. Code 726.206(b) and (e) that control metals emissions without requiring a trial burn, the owner or operator must submit the following: |
A) | Documentation of the feed rate of hazardous waste, other fuels, and industrial furnace feed stocks; |
B) | Documentation of the concentration of each metal controlled by 35 Ill. Adm. Code 726.206(b) or (c) in the hazardous waste, other fuels and industrial furnace feedstocks, and calculations of the total feed rate of each metal; |
C) | Documentation of how the applicant will ensure that the Tier I feed rate screening limits provided by 35 Ill. Adm. Code 726.206(b) or (e) will not be exceeded during the averaging period provided by that subsection; |
D) | Documentation to support the determination of the TESH (terrain-adjusted effective stack height), good engineering practice stack height, terrain type, and land use, as provided by 35 Ill. Adm. Code 726.206(b)(3) through (5); |
E) | Documentation of compliance with the provisions of 35 Ill. Adm. Code 726.206(b)(6), if applicable, for facilities with multiple stacks; |
F) | Documentation that the facility does not fail the criteria provided by 35 Ill. Adm. Code 726.206(b)(7) for eligibility to comply with the screening limits; and |
G) | Proposed sampling and metals analysis plan for the hazardous waste, other fuels, and industrial furnace feed stocks. |
4) | Waiver of trial burn for PM (particulate matter). When seeking to be permitted under the low risk waste provisions of 35 Ill. Adm. Code 726.209(b), which waives the particulate standard (and trial burn to demonstrate conformance with the particulate standard), applicants must submit documentation supporting conformance with subsections (a)(2)(B) and (a)(3) of this Section. |
5) | Waiver of trial burn for HCl and chlorine gas. When seeking to be permitted under the Tier I (or adjusted Tier I) feed rate screening limits for total chlorine and chloride provided by 35 Ill. Adm. Code 726.207(b)(1) and (e) that control emissions of HCl and chlorine gas without requiring a trial burn, the owner or operator must submit the following: |
A) | Documentation of the feed rate of hazardous waste, other fuels, and industrial furnace feed stocks; |
B) | Documentation of the levels of total chlorine and chloride in the hazardous waste, other fuels and industrial furnace feedstocks, and calculations of the total feed rate of total chlorine and chloride; |
C) | Documentation of how the applicant will ensure that the Tier I (or adjusted Tier I) feed rate screening limits provided by 35 Ill. Adm. Code 726.207(b)(1) or (e) will not be exceeded during the averaging period provided by that subsection; |
D) | Documentation to support the determination of the TESH, good engineering practice stack height, terrain type and land use as provided by 35 Ill. Adm. Code 726.207(b)(3); |
E) | Documentation of compliance with the provisions of 35 Ill. Adm. Code 726.207(b)(4), if applicable, for facilities with multiple stacks; |
F) | Documentation that the facility does not fail the criteria provided by 35 Ill. Adm. Code 726.207(b)(3) for eligibility to comply with the screening limits; and |
G) | Proposed sampling and analysis plan for total chlorine and chloride for the hazardous waste, other fuels, and industrial furnace feedstocks. |
6) | Data in lieu of trial burn. The owner or operator may seek an exemption from the trial burn requirements to demonstrate conformance with Section 703.232 and 35 Ill. Adm. Code 726.204 through 726.207 by providing the information required by Section 703.232 from previous compliance testing of the device in conformance with 35 Ill. Adm. Code 726.203 or from compliance testing or trial or operational burns of similar boilers or industrial furnaces burning similar hazardous wastes under similar conditions. If data from a similar device is used to support a trial burn waiver, the design and operating information required by Section 703.232 must be provided for both the similar device and the device to which the data is to be applied, and a comparison of the design and operating information must be provided. The Agency must approve a permit application without a trial burn if the Agency finds that the hazardous wastes are sufficiently similar, the devices are sufficiently similar, the operating conditions are sufficiently similar, and the data from other compliance tests, trial burns, or operational burns are adequate to specify (under 35 Ill. Adm. Code 726.102) operating conditions that will ensure conformance with 35 Ill. Adm. Code 726.102(c). In addition, the following information must be submitted: |
A) | For a waiver from any trial burn, the following: |
i) | A description and analysis of the hazardous waste to be burned compared with the hazardous waste for which data from compliance testing or operational or trial burns are provided to support the contention that a trial burn is not needed; |
ii) | The design and operating conditions of the boiler or industrial furnace to be used, compared with that for which comparative burn data are available; and |
iii) | Such supplemental information as the Agency finds necessary to achieve the purposes of this subsection (a). |
B) | For a waiver of the DRE trial burn, the basis for selection of POHCs (principal organic hazardous constituents) used in the other trial or operational burns that demonstrate compliance with the DRE performance standard in 35 Ill. Adm. Code 726.204(a). This analysis should specify the constituents in Appendix H to 35 Ill. Adm. Code 721 that the applicant has identified in the hazardous waste for which a permit is sought and any differences from the POHCs in the hazardous waste for which burn data are provided. |
b) | Alternative HC limit for industrial furnaces with organic matter in raw materials. An owner or operator of industrial furnaces requesting an alternative HC limit under 35 Ill. Adm. Code 726.204(f) must submit the following information at a minimum: |
1) | Documentation that the furnace is designed and operated to minimize HC emissions from fuels and raw materials; |
2) | Documentation of the proposed baseline flue gas HC (and CO) concentration, including data on HC (and CO) levels during tests when the facility produced normal products under normal operating conditions from normal raw materials while burning normal fuels and when not burning hazardous waste; |
3) | Test burn protocol to confirm the baseline HC (and CO) level including information on the type and flow rate of all feedstreams, point of introduction of all feedstreams, total organic carbon content (or other appropriate measure of organic content) of all nonfuel feedstreams, and operating conditions that affect combustion of fuels and destruction of hydrocarbon emissions from nonfuel sources; |
4) | Trial burn plan to do the following: |
A) | |
B) | |
5) | Implementation plan to monitor over time changes in the operation of the facility that could reduce the baseline HC level and procedures to periodically confirm the baseline HC level; and |
6) | Such other information as the Agency finds necessary to achieve the purposes of this subsection (b). |
c) | Alternative metals implementation approach. When seeking to be permitted under an alternative metals implementation approach under 35 Ill. Adm. Code 726.206(f), the owner or operator must submit documentation specifying how the approach ensures compliance with the metals emissions standards of 35 Ill. Adm. Code 726.106(c) or (d) and how the approach can be effectively implemented and monitored. Further, the owner or operator must provide such other information that the Agency finds necessary to achieve the purposes of this subsection (c). |
d) | Automatic waste feed cutoff system. An owner or operator must submit information describing the automatic waste feed cutoff system, including any pre-alarm systems that may be used. |
e) | Direct transfer. An owner or operator that uses direct transfer operations to feed hazardous waste from transport vehicles (containers, as defined in 35 Ill. Adm. Code 726.211) directly to the boiler or industrial furnace must submit information supporting conformance with the standards for direct transfer provided by 35 Ill. Adm. Code 726.211. |
f) | Residues. An owner or operator that claims that its residues are excluded from regulation under the provisions of 35 Ill. Adm. Code 726.212 must submit information adequate to demonstrate conformance with those provisions. |
BOARD NOTE: Derived from 40 CFR 270.22 (2002), as amended at 67 Fed. Reg. 77687 (December 19, 2002).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART E: SHORT TERM AND PHASED PERMITS
Section 703.221 | Alternative Compliance with the Federal NESHAPS |
When an owner or operator demonstrates compliance with the air emission standards and limitations of the federal National Emission Standards for Hazardous Air Pollutants (NESHAPs) in 40 CFR 63, subpart EEE, incorporated by reference in 35 Ill. Adm. Code 720.111 (i.e., by conducting a comprehensive performance test and submitting a Notification of Compliance under 40 CFR 63.1207(j) and 63.1210(b) documenting compliance with all applicable requirements of 40 CFR 63, subpart EEE), the requirements of Sections 703.221 through 703.225 do not apply, except those provisions that the Agency determines are necessary to ensure compliance with 35 Ill. Adm. Code 724.445(a) and (c) if the owner or operator elects to comply with Section 703.310(a)(1)(A) to minimize emissions of toxic compounds from startup, shutdown, and malfunction events. Nevertheless, the Agency may apply the provisions of Sections 703.221 through 703.225, on a case-by-case basis, for purposes of information collection in accordance with Sections 703.188 and 703.241(a)(2).
BOARD NOTE: Derived from 40 CFR 270.62 preamble (2002), as amended at 67 Fed. Reg. 77687 (December 19, 2002).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 703.232 | Permits for Boilers and Industrial Furnaces Burning Hazardous Waste |
When the owner or operator of a cement or lightweight aggregate kiln demonstrates compliance with the air emission standards and limitations of the federal National Emission Standards for Hazardous Air Pollutants (NESHAPs) in 40 CFR 63, subpart EEE, incorporated by reference in 35 Ill. Adm. Code 720.111 (i.e., by conducting a comprehensive performance test and submitting a Notification of Compliance under 40 CFR 63.1207(j) and 63.1210(b) documenting compliance with all applicable requirements of 40 CFR 63, subpart EEE), the requirements of this Section do not apply, except those provisions that the Agency determines are necessary to ensure compliance with 35 Ill. Adm. Code 726.202(e)(1) and (e)(2)(C) if the owner or operator elects to comply with Section 703.310(a)(1)(A) to minimize emissions of toxic compounds from startup, shutdown, and malfunction events. Nevertheless, the Agency may apply the provisions of this Section, on a case-by-case basis, for purposes of information collection in accordance with Sections 703.188 and 703.241(a)(2).
a) | General. The owner or operator of a new boiler or industrial furnace (one not operating under the interim status standards of 35 Ill. Adm. Code 726.203) is subject to subsections (b) through (f) of this Section. A boiler or industrial furnace operating under the interim status standards of 35 Ill. Adm. Code 726.203 is subject to subsection (g) of this Section. |
b) | Permit operating periods for a new boiler or industrial furnace. A permit for a new boiler or industrial furnace must specify appropriate conditions for the following operating periods: |
1) | Pretrial burn period. For the period beginning with initial introduction of hazardous waste and ending with initiation of the trial burn, and only for the minimum time required to bring the boiler or industrial furnace to a point of operation readiness to conduct a trial burn, not to exceed 720 hours operating time when burning hazardous waste, the Agency must establish permit conditions in the pretrial burn period, including but not limited to allowable hazardous waste feed rates and operating conditions. The Agency must extend the duration of this operational period once, for up to 720 additional hours, at the request of the applicant when good cause is shown. The permit must be modified to reflect the extension according to Sections 703.280 through 703.283. |
A) | Applicants must submit a statement, with Part B of the permit application, that suggests the conditions necessary to operate in compliance with the standards of 35 Ill. Adm. Code 726.204 through 726.207 during this period. This statement should include, at a minimum, restrictions on the applicable operating requirements identified in 35 Ill. Adm. Code 726.202 (e). |
B) | The Agency must review this statement and any other relevant information submitted with Part B of the permit application and specify requirements for this period sufficient to meet the performance standards of 35 Ill. Adm. Code 726.204 through 726.207 based on the Agency’s engineering judgment. |
2) | Trial burn period. For the duration of the trial burn, the Agency must establish conditions in the permit for the purposes of determining feasibility of compliance with the performance standards of 35 Ill. Adm. Code 726.204 through 726.207 and determining adequate operating conditions under 35 Ill. Adm. Code 726.202(e). Applicants must propose a trial burn plan, prepared under subsection (c) of this Section, to be submitted with Part B of the permit application. |
3) | Post-trial burn period. |
A) | For the period immediately following completion of the trial burn, and only for the minimum period sufficient to allow sample analysis, data computation and submission of the trial burn results by the applicant, and review of the trial burn results and modification of the facility permit by the Agency to reflect the trial burn results, the Agency must establish the operating requirements most likely to ensure compliance with the performance standards of 35 Ill. Adm. Code 726.204 through 726.207 based on the Agency’s engineering judgment. |
B) | Applicants must submit a statement, with Part B of the application, that identifies the conditions necessary to operate during this period in compliance with the performance standards of 35 Ill. Adm. Code 726.204 through 726.207. This statement should include, at a minimum, restrictions on the operating requirements provided by 35 Ill. Adm. Code 726.202 (e). |
C) | The Agency must review this statement and any other relevant information submitted with Part B of the permit application and specify requirements of this period sufficient to meet the performance standards of 35 Ill. Adm. Code 726.204 through 726.207 based on the Agency’s engineering judgment. |
4) | Final permit period. For the final period of operation the Agency must develop operating requirements in conformance with 35 Ill. Adm. Code 726.202(e) that reflect conditions in the trial burn plan and are likely to ensure compliance with the performance standards of 35 Ill. Adm. Code 726.204 through 726.207. Based on the trial burn results, the Agency must make any necessary modifications to the operating requirements to ensure compliance with the performance standards. The permit modification must proceed according to Sections 703.280 through 703.283. |
c) | Requirements for trial burn plans. The trial burn plan must include the following information. The Agency, in reviewing the trial burn plan, must evaluate the sufficiency of the information provided and may require the applicant to supplement this information, if necessary, to achieve the purposes of this subsection (c). |
1) | An analysis of each feed stream, including hazardous waste, other fuels, and industrial furnace feed stocks, as fired, that includes the following: |
A) | Heating value, levels of antimony, arsenic, barium, beryllium, cadmium, chromium, lead, mercury, silver, thallium, total chlorine and chloride, and ash; and |
B) | Viscosity or description of the physical form of the feed stream. |
2) | An analysis of each hazardous waste, as fired, including the following: |
A) | An identification of any hazardous organic constituents listed in Appendix H to 35 Ill. Adm. Code 721 that are present in the feed stream, except that the applicant need not analyze for constituents listed in Appendix H that would reasonably not be expected to be found in the hazardous waste. The constituents excluded from analysis must be identified and the basis for this exclusion explained. The analysis must be conducted in accordance with analytical techniques specified in “Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods,” USEPA Publication SW-846, as incorporated by reference at 35 Ill. Adm. Code 720.111 and Section 703.110, or their equivalent; |
B) | An approximate quantification of the hazardous constituents identified in the hazardous waste, within the precision produced by the analytical methods specified in “Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods,” USEPA Publication SW-846, as incorporated by reference at 35 Ill. Adm. Code 720.111 and Section 703.110, or other equivalent; and |
C) | A description of blending procedures, if applicable, prior to firing the hazardous waste, including a detailed analysis of the hazardous waste prior to blending, an analysis of the material with which the hazardous waste is blended, and blending ratios. |
3) | A detailed engineering description of the boiler or industrial furnace, including the following: |
A) | Manufacturer’s name and model number of the boiler or industrial furnace; |
B) | Type of boiler or industrial furnace; |
C) | Maximum design capacity in appropriate units; |
D) | Description of the feed system for the hazardous waste and, as appropriate, other fuels and industrial furnace feedstocks; |
E) | Capacity of hazardous waste feed system; |
F) | Description of automatic hazardous waste feed cutoff systems; |
G) | Description of any pollution control system; and |
H) | Description of stack gas monitoring and any pollution control monitoring systems. |
4) | A detailed description of sampling and monitoring procedures, including sampling and monitoring locations in the system, the equipment to be used, sampling and monitoring frequency, and sample analysis. |
5) | A detailed test schedule for each hazardous waste for which the trial burn is planned, including dates, duration, quantity of hazardous waste to be burned, and other factors relevant to the Agency’s decision under subsection (b)(2) of this Section. |
6) | A detailed test protocol, including, for each hazardous waste identified, the ranges of hazardous waste feed rate, and, as appropriate, the feed rates of other fuels and industrial furnace feedstocks, and any other relevant parameters that may affect the ability of the boiler or industrial furnace to meet the performance standards in 35 Ill. Adm. Code 726.204 through 726.207. |
7) | A description of and planned operating conditions for any emission control equipment that will be used. |
8) | Procedures for rapidly stopping the hazardous waste feed and controlling emissions in the event of an equipment malfunction. |
9) | Such other information as the Agency finds necessary to determine whether to approve the trial burn plan in light of the purposes of this subsection (c) and the criteria in subsection (b)(2) of this Section. |
d) | Trial burn procedures. |
1) | A trial burn must be conducted to demonstrate conformance with the standards of 35 Ill. Adm. Code 726.104 through 726.107. |
2) | The Agency must approve a trial burn plan if the Agency finds as follows: |
A) | That the trial burn is likely to determine whether the boiler or industrial furnace can meet the performance standards of 35 Ill. Adm. Code 726.104 through 726.107; |
B) | That the trial burn itself will not present an imminent hazard to human health and the environment; |
C) | That the trial burn will help the Agency to determine operating requirements to be specified under 35 Ill. Adm. Code 726.102(e); and |
D) | That the information sought in the trial burn cannot reasonably be developed through other means. |
3) | The Agency must send a notice to all persons on the facility mailing list, as set forth in 35 Ill. Adm. Code 705.161(a), and to the appropriate units of State and local government, as set forth in 35 Ill. Adm. Code 705.163(a)(5), announcing the scheduled commencement and completion dates for the trial burn. The applicant may not commence the trial burn until after the Agency has issued such notice. |
A) | This notice must be mailed within a reasonable time period before the trial burn. An additional notice is not required if the trial burn is delayed due to circumstances beyond the control of the facility or the Agency. |
B) | This notice must contain the following: |
i) | The name and telephone number of applicant’s contact person; |
ii) | The name and telephone number of the Agency regional office appropriate for the facility; |
iii) | The location where the approved trial burn plan and any supporting documents can be reviewed and copied; and |
iv) | An expected time period for commencement and completion of the trial burn. |
4) | The applicant must submit to the Agency a certification that the trial burn has been carried out in accordance with the approved trial burn plan, and submit the results of all the determinations required in subsection (c) of this Section. The Agency must, in the trial burn plan, require that the submission be made within 90 days after completion of the trial burn, or later if the Agency determines that a later date is acceptable. |
5) | All data collected during any trial burn must be submitted to the Agency following completion of the trial burn. |
6) | All submissions required by this subsection (d) must be certified on behalf of the applicant by the signature of a person authorized to sign a permit application or a report under 35 Ill. Adm. Code 702.126. |
e) | Special procedures for DRE trial burns. When a DRE trial burn is required under 35 Ill. Adm. Code 726.104, the Agency must specify (based on the hazardous waste analysis data and other information in the trial burn plan) as trial Principal Organic Hazardous Constituents (POHCs) those compounds for which destruction and removal efficiencies must be calculated during the trial burn. These trial POHCs will be specified by the Agency based on information including the Agency’s estimate of the difficulty of destroying the constituents identified in the hazardous waste analysis, their concentrations or mass in the hazardous waste feed, and, for hazardous waste containing or derived from wastes listed in Subpart D of 35 Ill. Adm. Code 721, the hazardous waste organic constituents identified in Appendix G to 35 Ill. Adm. Code 721 as the basis for listing. |
f) | Determinations based on trial burn. During each approved trial burn (or as soon after the burn as is practicable), the applicant must make the following determinations: |
1) | A quantitative analysis of the levels of antimony, arsenic, barium, beryllium, cadmium, chromium, lead, mercury, thallium, silver, and chlorine/chloride in the feed streams (hazardous waste, other fuels, and industrial furnace feedstocks); |
2) | When a DRE trial burn is required under 35 Ill. Adm. Code 726.204(a), the following determinations: |
A) | A quantitative analysis of the trial POHCs in the hazardous waste feed; |
B) | A quantitative analysis of the stack gas for the concentration and mass emissions of the trial POHCs; and |
C) | A computation of destruction and removal efficiency (DRE), in accordance with the DRE formula specified in 35 Ill. Adm. Code 726.204(a); |
3) | When a trial burn for chlorinated dioxins and furans is required under 35 Ill. Adm. Code 726.204(e), a quantitative analysis of the stack gas for the concentration and mass emission rate of the 2,3,7,8-chlorinated tetra- through octa-congeners of chlorinated dibenzo-p-dioxins and furans, and a computation showing conformance with the emission standard; |
4) | When a trial burn for PM, metals, or HCl and chlorine gas is required under 35 Ill. Adm. Code 726.205, 726.206(c) or (d), or 726.207(b)(2) or (c), a quantitative analysis of the stack gas for the concentrations and mass emissions of PM, metals, or HCl and chlorine gas, and computations showing conformance with the applicable emission performance standards; |
5) | When a trial burn for DRE, metals, and HCl and chlorine gas is required under 35 Ill. Adm. Code 726.204(a), 726.206(c) or (d), or 726.207(b)(2) or (c), a quantitative analysis of the scrubber water (if any), ash residues, other residues, and products for the purpose of estimating the fate of the trial POHCs, metals, and chlorine and chloride; |
6) | An identification of sources of fugitive emissions and their means of control; |
7) | A continuous measurement of carbon monoxide (CO), oxygen, and, where required, hydrocarbons (HC) in the stack gas; and |
8) | Such other information as the Agency specifies as necessary to ensure that the trial burn will determine compliance with the performance standards 35 Ill. Adm. Code 726.204 through 726.207 and to establish the operating conditions required by 35 Ill. Adm. Code 726.204 through 726.207 and of determining adequate operating conditions under 35 Ill. Adm. Code 726.203, and to establish the operating conditions required by 35 Ill. Adm. Code 726.202(e) as necessary to meet those performance standards. |
g) | Interim status boilers and industrial furnaces. For the purpose of determining feasibility of compliance with the performance standards of 35 Ill. Adm. Code 726.204 through 726.207 and of determining adequate operating conditions under 35 Ill. Adm. Code 726.203, an applicant that owns or operates an existing boiler or industrial furnace which is operated under the interim status standards of 35 Ill. Adm. Code 726.203 must either prepare and submit a trial burn plan and perform a trial burn in accordance with the requirements of this Section or submit other information as specified in Section 703.208(a)(6). The Agency must announce its intention to approve of the trial burn plan in accordance with the timing and distribution requirements of subsection (d)(3) of this Section. The contents of the notice must include all of the following information: the name and telephone number of a contact person at the facility; the name and telephone number of the Agency regional office appropriate for the facility; the location where the trial burn plan and any supporting documents can be reviewed and copied; and a schedule of the activities that are required prior to permit issuance, including the anticipated time schedule for Agency approval of the plan, and the time periods during which the trial burn would be conducted. Applicants that submit a trial burn plan and receive approval before submission of the Part B permit application must complete the trial burn and submit the results specified in subsection (f) of this Section with the Part B permit application. If completion of this process conflicts with the date set for submission of the Part B application, the applicant must contact the Agency to establish a later date for submission of the Part B application or the trial burn results. If the applicant submits a trial burn plan with Part B of the permit application, the trial burn must be conducted and the results submitted within a time period prior to permit issuance to be specified by the Agency. |
BOARD NOTE: Derived from 40 CFR 270.66 (2002), as amended at 67 Fed. Reg. 77687 (December 19, 2002).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 720
HAZARDOUS WASTE MANAGEMENT SYSTEM: GENERAL
SUBPART A: GENERAL PROVISIONS
Section
720.101 | Purpose, Scope, and Applicability |
720.102 | Availability of Information; Confidentiality of Information |
720.103 | Use of Number and Gender |
SUBPART B: DEFINITIONS AND REFERENCES
Section
720.110 | Definitions |
720.111 | References |
SUBPART C: RULEMAKING PETITIONS AND OTHER PROCEDURES
Section
720.120 | Rulemaking |
720.121 | Alternative Equivalent Testing Methods |
720.122 | Waste Delisting |
720.123 | Petitions for Regulation as Universal Waste |
720.130 | Procedures for Solid Waste Determinations |
720.131 | Solid Waste Determinations |
720.132 | Boiler Determinations |
720.133 | Procedures for Determinations |
720.140 | Additional |
720.141 | Procedures for |
Overview of 40 CFR, Subtitle C Regulations | |
AUTHORITY: Implementing Sections 7.2, 13, and 22.4 and authorized by Section 27 of the Environmental Protection Act [415 ILCS 5/7.2, 13, 22.4, and 27].
SOURCE: Adopted in R81-22 at 5 Ill. Reg. 9781, effective May 17, 1982; amended and codified in R81-22 at 6 Ill. Reg. 4828, effective May 17, 1982; amended in R82-19 at 7 Ill. Reg. 14015, effective October 12, 1983; amended in R84-9 at 9 Ill. Reg. 11819, effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 968, effective January 2, 1986; amended in R86-1 at 10 Ill. Reg. 13998, effective August 12, 1986; amended in R86-19 at 10 Ill. Reg. 20630, effective December 2, 1986; amended in R86-28 at 11 Ill. Reg. 6017, effective March 24, 1987; amended in R86-46 at 11 Ill. Reg. 13435, effective August 4, 1987; amended in R87-5 at 11 Ill. Reg. 19280, effective November 12, 1987; amended in R87-26 at 12 Ill. Reg. 2450, effective January 15, 1988; amended in R87-39 at 12 Ill. Reg. 12999, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 362, effective December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18278, effective November 13, 1989; amended in R89-2 at 14 Ill. Reg. 3075, effective February 20, 1990; amended in R89-9 at 14 Ill. Reg. 6225, effective April 16, 1990; amended in R90-10 at 14 Ill. Reg. 16450, effective September 25, 1990; amended in R90-17 at 15 Ill. Reg. 7934, effective May 9, 1991; amended in R90-11 at 15 Ill. Reg. 9323, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14446, effective September 30, 1991; amended in R91-13 at 16 Ill. Reg. 9489, effective June 9, 1992; amended in R92-1 at 16 Ill. Reg. 17636, effective November 6, 1992; amended in R92-10 at 17 Ill. Reg. 5625, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20545, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6720, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12160, effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17480, effective November 23, 1994; amended in R95-6 at 19 Ill. Reg. 9508, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 10929, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 256, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7590, effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17496, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1704, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9094, effective July 26, 1999; amended in R00-5 at 24 Ill. Reg. 1063, effective January 6, 2000; amended in R00-13 at 24 Ill. Reg. 9443, effective June 20, 2000; amended in R01-3 at 25 Ill. Reg. 1266, effective January 11, 2001; amended in R01-21/R01-23 at 25 Ill. Reg. 9168, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. 6550, effective April 22, 2002; amended in R03-7 at 27 Ill. Reg. 3712, effective February 14, 2003; amended in R03-18 at 27 Ill. Reg. ________, effective ______________________.
SUBPART A: GENERAL PROVISIONS
Section 720.101 | Purpose, Scope, and Applicability |
a) | This Part provides definitions of terms, general standards, and overview information applicable to 35 Ill. Adm. Code 720 through |
b) | In this Part: |
1) | Section 720.102 sets forth the rules that the Board and the Agency will use in making information it receives available to the public and sets forth the requirements that a generator, transporter, or owner or operator of a treatment, storage, or disposal facility must follow to assert claims of business confidentiality with respect to information that is submitted to the Board or the Agency under 35 Ill. Adm. Code 720 through 725 and 728. |
2) | Section 720.103 establishes rules of grammatical construction for 35 Ill. Adm. Code 720 through |
3) | Section 720.110 defines terms |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 720.103 | Use of Number and Gender |
As used in 35 Ill. Adm. Code 720 through 725 726, and 728, 733, and 739:
a) | Words in the masculine gender also include the feminine and neuter genders; |
b) | Words in the singular include the plural; and |
c) | Words in the plural include the singular. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART B: DEFINITIONS AND REFERENCES
Section 720.110 | Definitions |
When used in 35 Ill. Adm. Code 720 through 726, and 728, 733, and 739 only, the following terms have the meanings given below:
“Aboveground tank” means a device meeting the definition of tank that is situated in such a way that the entire surface area of the tank is completely above the plane of the adjacent surrounding surface and the entire surface area of the tank (including the tank bottom) is able to be visually inspected.
“Act” or “RCRA” means the Solid Waste Disposal Act, as amended by the Resource Conservation and Recovery Act of 1976, as amended (42 USC 6901 et seq.)
“Active life” of a facility means the period from the initial receipt of hazardous waste at the facility until the Agency receives certification of final closure.
“Active portion” means that portion of a facility where treatment, storage, or disposal operations are being or have been conducted after May 19, 1980, and which is not a closed portion. (See also “closed portion” and “inactive portion.”.)
“Administrator” means the Administrator of the United States Environmental Protection Agency or the Administrator’s designee.
“Agency” means the Illinois Environmental Protection Agency.
“Ancillary equipment” means any device, including, but not limited to, such devices as piping, fittings, flanges, valves, and pumps, that is used to distribute, meter, or control the flow of hazardous waste from its point of generation to storage or treatment tanks, between hazardous waste storage and treatment tanks to a point of disposal onsite, or to a point of shipment for disposal off-site.
“Aquifer” means a geologic formation, group of formations, or part of a formation capable of yielding a significant amount of groundwater to wells or springs.
“Authorized representative” means the person responsible for the overall operation of a facility or an operational unit (i.e., part of a facility), e.g., the plant manager, superintendent, or person of equivalent responsibility.
“Battery” means a device consisting that consists of one or more electrically connected electrochemical cells that which is designed to receive, store, and deliver electric energy. An electrochemical cell is a system consisting of an anode, cathode, and an electrolyte, plus such connections (electrical and mechanical) as may be needed to allow the cell to deliver or receive electrical energy. The term battery also includes an intact, unbroken battery from which the electrolyte has been removed.
“Board” means the Illinois Pollution Control Board.
“Boiler” means an enclosed device using controlled flame combustion and having the following characteristics:
Boiler physical characteristics.
The unit must have physical provisions for recovering and exporting thermal energy in the form of steam, heated fluids, or heated gases; and the unit’s combustion chamber and primary energy recovery sections must be of integral design. To be of integral design, the combustion chamber and the primary energy recovery sections (such as waterwalls and superheaters) must be physically formed into one manufactured or assembled unit. A unit in which the combustion chamber and the primary energy recovery sections are joined only by ducts or connections carrying flue gas is not integrally designed; however, secondary energy recovery equipment (such as economizers or air preheaters) need not be physically formed into the same unit as the combustion chamber and the primary energy recovery section. The following units are not precluded from being boilers solely because they are not of integral design: process heaters (units that transfer energy directly to a process stream) and fluidized bed combustion units; and
While in operation, the unit must maintain a thermal energy recovery efficiency of at least 60 percent, calculated in terms of the recovered energy compared with the thermal value of the fuel; and
The unit must export and utilize at least 75 percent of the recovered energy, calculated on an annual basis. In this calculation, no credit may be given for recovered heat used internally in the same unit. (Examples of internal use are the preheating of fuel or combustion air, and the driving of induced or forced draft fans or feedwater pumps.); or
Boiler by designation. The unit is one which that the Board has determined, on a case-by-case basis, to be a boiler, after considering the standards in Section 720.132.
“Carbon regeneration unit” means any enclosed thermal treatment device used to regenerate spent activated carbon.
“Certification” means a statement of professional opinion based upon knowledge and belief.
“Closed portion” means that portion of a facility that an owner or operator has closed in accordance with the approved facility closure plan and all applicable closure requirements. (See also “active portion” and “inactive portion.”.)
“Component” means either the tank or ancillary equipment of a tank system.
“Confined aquifer” means an aquifer bounded above and below by impermeable beds or by beds of distinctly lower permeability than that of the aquifer itself; an aquifer containing confined groundwater.
“Container” means any portable device in which a material is stored, transported, treated, disposed of, or otherwise handled.
“Containment building” means a hazardous waste management unit that is used to store or treat hazardous waste under the provisions of Subpart DD of 35 Ill. Adm. Code 724.Subpart DD and Subpart DD of 35 Ill. Adm. Code 725.Subpart DD.
“Contingency plan” means a document setting out an organized, planned and coordinated course of action to be followed in case of a fire, explosion, or release of hazardous waste or hazardous waste constituents that could threaten human health or the environment.
“Corrosion expert” means a person who, by reason of knowledge of the physical sciences and the principles of engineering and mathematics, acquired by a professional education and related practical experience, is qualified to engage in the practice of corrosion control on buried or submerged metal piping systems and metal tanks. Such a person must be certified as being qualified by the National Association of Corrosion Engineers (NACE) or be a registered professional engineer who has certification or licensing that includes education and experience in corrosion control on buried or submerged metal piping systems and metal tanks.
“Designated facility” means a hazardous waste treatment, storage, or disposal facility,
Of which any of the following is true:
The facility has received a RCRA permit (or interim status) pursuant to 35 Ill. Adm. Code 702, 703, and 705;
The facility has received a RCRA permit from USEPA pursuant to 40 CFR 124 and 270 (1999) (2002);
The facility has received a RCRA permit from a state authorized by USEPA pursuant to 40 CFR 271 (1999) (2002); or
The facility is regulated under 35 Ill. Adm. Code 721.106(c)(2) or Subpart F of 35 Ill. Adm. Code 266.Subpart F; and
The facility has been designated on the manifest by the generator pursuant to 35 Ill. Adm. Code 722.120.
If a waste is destined to a facility in a state other than Illinois that has been authorized by USEPA pursuant to 40 CFR 271, but which has not yet obtained authorization to regulate that waste as hazardous, then the designated facility must be a facility allowed by the receiving state to accept such waste.
“Destination facility” means a facility that treats, disposes of, or recycles a particular category of universal waste, except those management activities described in 35 Ill. Adm. Code 733.113(a) and (c) and 733.133(a) and (c). A facility at which a particular category of universal waste is only accumulated is not a destination facility for the purposes of managing that category of universal waste.
“Dike” means an embankment or ridge of either natural or manmade materials used to prevent the movement of liquids, sludges, solids, or other materials.
“Dioxins and furans” or “D/F” means tetra, penta penta-, hexa hexa-, hepta hepta-, and octa-chlorinated dibenzo dioxins and furans.
“Director” means the Director of the Illinois Environmental Protection Agency.
“Discharge” or “hazardous waste discharge” means the accidental or intentional spilling, leaking, pumping, pouring, emitting, emptying, or dumping of hazardous waste into or on any land or water.
“Disposal” means the discharge, deposit, injection, dumping, spilling, leaking, or placing of any solid waste or hazardous waste into or on any land or water so that such solid waste or hazardous waste or any constituent thereof may enter the environment or be emitted into the air or discharged into any waters, including groundwaters.
“Disposal facility” means a facility or part of a facility at which hazardous waste is intentionally placed into or on any land or water and at which waste will remain after closure. The term disposal facility does not include a corrective action management unit (CAMU) into which remediation wastes are placed.
“Drip pad” means an engineered structure consisting of a curbed, free-draining base, constructed of non-earthen materials and designed to convey preservative kick-back or drippage from treated wood, precipitation and surface water runon to an associated collection system at wood preserving plants.
“Elementary neutralization unit” means a device of which the following is true:
Is It is used for neutralizing wastes which that are hazardous only because they exhibit the corrosivity characteristic defined in 35 Ill. Adm. Code 721.122 or which are listed in Subpart D of 35 Ill. Adm. Code 721.Subpart D only for this reason; and
Meets It meets the definition of tank, tank system, container, transport vehicle, or vessel in this Section.
“EPA hazardous waste number” or “USEPA hazardous waste number” means the number assigned by USEPA to each hazardous waste listed in Subpart D of 35 Ill. Adm. Code 721.Subpart D and to each characteristic identified in Subpart C of 35 Ill. Adm. Code 721.Subpart C.
“EPA identification number” or “USEPA identification number” means the number assigned by USEPA pursuant to 35 Ill. Adm. Code 722 through 725 to each generator; transporter; and treatment, storage, or disposal facility.
“EPA region” or “USEPA region” means the states and territories found in any one of the following ten regions:
Region I: Maine, Vermont, New Hampshire, Massachusetts, Connecticut, and Rhode Island
Region II: New York, New Jersey, Commonwealth of Puerto Rico, and the U.S. Virgin Islands
Region III: Pennsylvania, Delaware, Maryland, West Virginia, Virginia, and the District of Columbia
Region IV: Kentucky, Tennessee, North Carolina, Mississippi, Alabama, Georgia, South Carolina, and Florida
Region V: Minnesota, Wisconsin, Illinois, Michigan, Indiana, and Ohio
Region VI: New Mexico, Oklahoma, Arkansas, Louisiana, and Texas
Region VII: Nebraska, Kansas, Missouri, and Iowa
Region VIII: Montana, Wyoming, North Dakota, South Dakota, Utah, and Colorado
Region IX: California, Nevada, Arizona, Hawaii, Guam, American Samoa, and Commonwealth of the Northern Mariana Islands
Region X: Washington, Oregon, Idaho, and Alaska
“Equivalent method” means any testing or analytical method approved by the Board pursuant to Section 720.120.
“Existing hazardous waste management (HWM) facility” or “existing facility” means a facility that was in operation or for which construction commenced on or before November 19, 1980. A facility had commenced construction if the owner or operator had obtained the federal, State, and local approvals or permits necessary to begin physical construction and either of the following had occurred:
A continuous on-site, physical construction program had begun; or
The owner or operator had entered into contractual obligations that could not be canceled or modified without substantial loss for physical construction of the facility to be completed within a reasonable time.
“Existing portion” means that land surface area of an existing waste management unit, included in the original Part A permit application, on which wastes have been placed prior to the issuance of a permit.
“Existing tank system” or “existing component” means a tank system or component that is used for the storage or treatment of hazardous waste and which was in operation, or for which installation was commenced, on or prior to July 14, 1986. Installation will be considered to have commenced if the owner or operator has obtained all federal, State, and local approvals or permits necessary to begin physical construction of the site or installation of the tank system and if either of the following is true:
A continuous on-site physical construction or installation program has begun; or
The owner or operator has entered into contractual obligations that cannot be canceled or modified without substantial loss for physical construction of the site or installation of the tank system to be completed within a reasonable time.
“Explosives or munitions emergency” means a situation involving the suspected or detected presence of unexploded ordnance (UXO), damaged or deteriorated explosives or munitions, an improvised explosive device (IED), other potentially explosive material or device, or other potentially harmful military chemical munitions or device, that creates an actual or potential imminent threat to human health, including safety, or the environment, including property, as determined by an explosives or munitions emergency response specialist. Such situations may require immediate and expeditious action by an explosives or munitions emergency response specialist to control, mitigate, or eliminate the threat.
“Explosives or munitions emergency response” means all immediate response activities by an explosives and munitions emergency response specialist to control, mitigate, or eliminate the actual or potential threat encountered during an explosives or munitions emergency. An explosives or munitions emergency response may include in-place render-safe procedures, treatment, or destruction of the explosives or munitions or transporting those items to another location to be rendered safe, treated, or destroyed. Any reasonable delay in the completion of an explosives or munitions emergency response caused by a necessary, unforeseen, or uncontrollable circumstance will not terminate the explosives or munitions emergency. Explosives and munitions emergency responses can occur on either public or private lands and are not limited to responses at RCRA facilities.
“Explosives or munitions emergency response specialist” means an individual trained in chemical or conventional munitions or explosives handling, transportation, render-safe procedures, or destruction techniques. Explosives or munitions emergency response specialists include United States Department of Defense (USDOD) emergency explosive ordnance disposal (EOD), technical escort unit (TEU), and USDOD-certified civilian or contractor personnel and other federal, State, or local government or civilian personnel who are similarly trained in explosives or munitions emergency responses.
“Facility” means the following:
All contiguous land and structures, other appurtenances, and improvements on the land used for treating, storing, or disposing of hazardous waste. A facility may consist of several treatment, storage, or disposal operational units (e.g., one or more landfills, surface impoundments, or combinations of them).
For the purpose of implementing corrective action under 35 Ill. Adm. Code 724.201, all contiguous property under the control of the owner or operator seeking a permit under Subtitle C of RCRA. This definition also applies to facilities implementing corrective action under RCRA section 3008(h).
Notwithstanding the immediately-preceding paragraph of this definition, a remediation waste management site is not a facility that is subject to 35 Ill. Adm. Code 724.201, but a facility that is subject to corrective action requirements if the site is located within such a facility.
“Federal agency” means any department, agency, or other instrumentality of the federal government, any independent agency or establishment of the federal government, including any government corporation and the Government Printing Office.
“Federal, State, and local approvals or permits necessary to begin physical construction” means permits and approvals required under federal, State, or local hazardous waste control statutes, regulations, or ordinances.
“Final closure” means the closure of all hazardous waste management units at the facility in accordance with all applicable closure requirements so that hazardous waste management activities under 35 Ill. Adm. Code 724 and 725 are no longer conducted at the facility unless subject to the provisions of 35 Ill. Adm. Code 722.134.
“Food-chain crops” means tobacco, crops grown for human consumption, and crops grown for feed for animals whose products are consumed by humans.
“Freeboard” means the vertical distance between the top of a tank or surface impoundment dike and the surface of the waste contained therein.
“Free liquids” means liquids which that readily separate from the solid portion of a waste under ambient temperature and pressure.
“Generator” means any person, by site, whose act or process produces hazardous waste identified or listed in 35 Ill. Adm. Code 721 or whose act first causes a hazardous waste to become subject to regulation.
“Groundwater” means water below the land surface in a zone of saturation.
“Hazardous waste” means a hazardous waste as defined in 35 Ill. Adm. Code 721.103.
“Hazardous waste constituent” means a constituent that caused the hazardous waste to be listed in Subpart D of 35 Ill. Adm. Code 721.Subpart D, or a constituent listed in 35 Ill. Adm. Code 721.124.
“Hazardous waste management unit” is a contiguous area of land on or in which hazardous waste is placed, or the largest area in which there is significant likelihood of mixing hazardous waste constituents in the same area. Examples of hazardous waste management units include a surface impoundment, a waste pile, a land treatment area, a landfill cell, an incinerator, a tank and its associated piping and underlying containment system, and a container storage area. A container alone does not constitute a unit; the unit includes containers, and the land or pad upon which they are placed.
“Inactive portion” means that portion of a facility which that is not operated after November 19, 1980. (See also “active portion” and “closed portion.”.)
“Incinerator” means any enclosed device of which the following is true:
The facility uses controlled flame combustion, and it neither both of the following are true of the facility:
Meets The facility does not meet the criteria for classification as a boiler, sludge dryer, or carbon regeneration unit, nor
Is The facility is not listed as an industrial furnace; or
The facility meets the definition of infrared incinerator or plasma arc incinerator.
“Incompatible waste” means a hazardous waste that is unsuitable for the following:
Placement in a particular device or facility because it may cause corrosion or decay of containment materials (e.g., container inner liners or tank walls); or
Commingling with another waste or material under uncontrolled conditions because the commingling might produce heat or pressure, fire, or explosion, violent reaction, toxic dusts, mists, fumes or gases, or flammable fumes or gases.
(See Appendix E to 35 Ill. Adm. Code 725.Appendix E for examples.)
“Industrial furnace” means any of the following enclosed devices that are integral components of manufacturing processes and that use thermal treatment to accomplish recovery of materials or energy:
Cement kilns;
Lime kilns;
Aggregate kilns;
Phosphate kilns;
Coke ovens;
Blast furnaces;
Smelting, melting and refining furnaces (including pyrometallurgical devices such as cupolas, reverberator furnaces, sintering machines, roasters, and foundry furnaces);
Titanium dioxide chloride process oxidation reactors;
Methane reforming furnaces;
Pulping liquor recovery furnaces;
Combustion devices used in the recovery of sulfur values from spent sulfuric acid;
Halogen acid furnaces (HAFs) for the production of acid from halogenated hazardous waste generated by chemical production facilities where the furnace is located on the site of a chemical production facility, the acid product has a halogen acid content of at least three percent, the acid product is used in a manufacturing process, and, except for hazardous waste burned as fuel, hazardous waste fed to the furnace has a minimum halogen content of 20 percent, as generated; and
Any other such device as the Agency determines to be an industrial furnace on the basis of one or more of the following factors:
The design and use of the device primarily to accomplish recovery of material products;
The use of the device to burn or reduce raw materials to make a material product;
The use of the device to burn or reduce secondary materials as effective substitutes for raw materials, in processes using raw materials as principal feedstocks;
The use of the device to burn or reduce secondary materials as ingredients in an industrial process to make a material product;
The use of the device in common industrial practice to produce a material product; and
Other relevant factors.
“Individual generation site” means the contiguous site at or on which one or more hazardous wastes are generated. An individual generation site, such as a large manufacturing plant, may have one or more sources of hazardous waste but is considered a single or individual generation site if the site or property is contiguous.
“Infrared incinerator” means any enclosed device that uses electric powered resistance heaters as a source of radiant heat followed by an afterburner using controlled flame combustion and which is not listed as an industrial furnace.
“Inground tank” means a device meeting the definition of tank whereby a portion of the tank wall is situated to any degree within the ground, thereby preventing visual inspection of that external surface area of the tank that is in the ground.
“In operation” refers to a facility that is treating, storing, or disposing of hazardous waste.
“Injection well” means a well into which fluids are being injected. (See also “underground injection.”.)
“Inner liner” means a continuous layer of material placed inside a tank or container that protects the construction materials of the tank or container from the contained waste or reagents used to treat the waste.
“Installation inspector” means a person who, by reason of knowledge of the physical sciences and the principles of engineering, acquired by a professional education and related practical experience, is qualified to supervise the installation of tank systems.
“International shipment” means the transportation of hazardous waste into or out of the jurisdiction of the United States.
“Lamp” or “universal waste lamp” means the bulb or tube portion of an electric lighting device. A lamp is specifically designed to produce radiant energy, most often in the ultraviolet, visible, or infra-red infrared regions of the electromagnetic spectrum. Examples of common universal waste lamps include, but are not limited to, fluorescent, high intensity discharge, neon, mercury vapor, high pressure high-pressure sodium, and metal halide lamps.
“Land treatment facility” means a facility or part of a facility at which hazardous waste is applied onto or incorporated into the soil surface; such facilities are disposal facilities if the waste will remain after closure.
“Landfill” means a disposal facility or part of a facility where hazardous waste is placed in or on land and which is not a pile, a land treatment facility, a surface impoundment, an underground injection well, a salt dome formation, a salt bed formation, an underground mine, a cave, or a corrective action management unit (CAMU).
“Landfill cell” means a discrete volume of a hazardous waste landfill that uses a liner to provide isolation of wastes from adjacent cells or wastes. Examples of landfill cells are trenches and pits.
“LDS” means leak detection system.
“Leachate” means any liquid, including any suspended components in the liquid, that has percolated through or drained from hazardous waste.
“Liner” means a continuous layer of natural or manmade materials beneath or on the sides of a surface impoundment, landfill, or landfill cell that restricts the downward or lateral escape of hazardous waste, hazardous waste constituents, or leachate.
“Leak-detection system” means a system capable of detecting the failure of either the primary or secondary containment structure or the presence of a release of hazardous waste or accumulated liquid in the secondary containment structure. Such a system must employ operational controls (e.g., daily visual inspections for releases into the secondary containment system of aboveground tanks) or consist of an interstitial monitoring device designed to detect continuously and automatically the failure of the primary or secondary containment structure or the presence of a release of hazardous waste into the secondary containment structure.
“Management” or “hazardous waste management” means the systematic control of the collection, source separation, storage, transportation, processing, treatment, recovery, and disposal of hazardous waste.
“Manifest” means the shipping document originated and signed by the generator that contains the information required by Subpart B of 35 Ill. Adm. Code 722.Subpart B.
“Manifest document number” means the USEPA twelve digit identification number assigned to the generator plus a unique five digit five-digit document number assigned to the manifest by the generator for recording and reporting purposes.
“Military munitions” means all ammunition products and components produced or used by or for the United States Department of Defense or the United States Armed Services for national defense and security, including military munitions under the control of the United States Department of Defense (USDOD), the United States Coast Guard, the United States Department of Energy (USDOE), and National Guard personnel. The term military munitions includes: confined gaseous, liquid, and solid propellants, explosives, pyrotechnics, chemical and riot control agents, smokes, and incendiaries used by USDOD components, including bulk explosives and chemical warfare agents, chemical munitions, rockets, guided and ballistic missiles, bombs, warheads, mortar rounds, artillery ammunition, small arms ammunition, grenades, mines, torpedoes, depth charges, cluster munitions and dispensers, demolition charges, and devices and components of these items and devices. Military munitions do not include wholly inert items, improvised explosive devices, and nuclear weapons, nuclear devices, and nuclear components of these items and devices. However, the term does include non-nuclear components of nuclear devices, managed under USDOE’s nuclear weapons program after all sanitization operations required under the Atomic Energy Act of 1954 (42 USC 2014 et seq.), as amended, have been completed.
“Mining overburden returned to the mine site” means any material overlying an economic mineral deposit which that is removed to gain access to that deposit and is then used for reclamation of a surface mine.
“Miscellaneous unit” means a hazardous waste management unit where hazardous waste is treated, stored, or disposed of and that is not a container; tank; surface impoundment; pile; land treatment unit; landfill; incinerator; boiler; industrial furnace; underground injection well with appropriate technical standards under 35 Ill. Adm. Code 730; containment building; corrective action management unit (CAMU); unit eligible for a research, development, and demonstration permit under 35 Ill. Adm. Code 703.231; or staging pile.
“Movement” means hazardous waste that is transported to a facility in an individual vehicle.
“New hazardous waste management facility” or “new facility” means a facility that began operation, or for which construction commenced after November 19, 1980. (See also “Existing hazardous waste management facility.”.)
“New tank system” or “new tank component” means a tank system or component that will be used for the storage or treatment of hazardous waste and for which installation commenced after July 14, 1986; except, however, for purposes of 35 Ill. Adm. Code 724.293(g)(2) and 725.293(g)(2), a new tank system is one for which construction commenced after July 14, 1986. (See also “existing tank system.”.)
“Onground tank” means a device meeting the definition of tank that is situated in such a way that the bottom of the tank is on the same level as the adjacent surrounding surfaces so that the external tank bottom cannot be visually inspected.
“On-site” means the same or geographically contiguous property which that may be divided by public or private right-of-way, provided the entrance and exit between the properties is at a crossroads intersection and access is by crossing as opposed to going along the right-of-way. Noncontiguous properties owned by the same person but connected by a right-of-way which he that the owner controls and to which the public does not have access is also considered on-site property.
“Open burning” means the combustion of any material without the following characteristics:
Control of combustion air to maintain adequate temperature for efficient combustion;
Containment of the combustion reaction in an enclosed device to provide sufficient residence time and mixing for complete combustion; and
Control of emission of the gaseous combustion products.
(See also “incineration” and “thermal treatment.”.)
“Operator” means the person responsible for the overall operation of a facility.
“Owner” means the person that owns a facility or part of a facility.
“Partial closure” means the closure of a hazardous waste management unit in accordance with the applicable closure requirements of 35 Ill. Adm. Code 724 or 725 at a facility that contains other active hazardous waste management units. For example, partial closure may include the closure of a tank (including its associated piping and underlying containment systems), landfill cell, surface impoundment, waste pile, or other hazardous waste management unit, while other units of the same facility continue to operate.
“Person” means an individual, trust, firm, joint stock company, federal agency, corporation (including a government corporation), partnership, association, state, municipality, commission, political subdivision of a state, or any interstate body.
“Personnel” or “facility personnel” means all persons who work at or oversee the operations of a hazardous waste facility and whose actions or failure to act may result in noncompliance with the requirements of 35 Ill. Adm. Code 724 or 725.
“Pesticide” means any substance or mixture of substances intended for preventing, destroying, repelling, or mitigating any pest or intended for use as a plant regulator, defoliant, or desiccant, other than any article that fulfills one of the following descriptions:
It is a new animal drug under section 201(v) of the Federal Food, Drug and Cosmetic Act (FFDCA; 21 USC 321(v)), incorporated by reference in Section 720.111;
It is an animal drug that has been determined by regulation of the federal Secretary of Health and Human Services pursuant to FFDCA section 512 (21 USC 360b), incorporated by reference in Section 720.111, to be an exempted new animal drug; or
It is an animal feed under FFDCA section 201(w) (21 USC 321(w)), incorporated by reference in Section 720.111, that bears or contains any substances described in either of the two preceding paragraphs of this definition.
BOARD NOTE: The second exception of corresponding 40 CFR 260.10 reads as follows: “Is an animal drug that has been determined by regulation of the Secretary of Health and Human Services not to be a new animal drug.”. This is very similar to the language of section 2(u) of the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA; 7 USC 136(u)). The three exceptions, taken together, appear intended not to include as pesticide any material within the scope of federal Food and Drug Administration regulation. The Board codified this provision with the intent of retaining the same meaning as its federal counterpart while adding the definiteness required under Illinois law.
“Pile” means any noncontainerized accumulation of solid, non-flowing hazardous waste that is used for treatment or storage, and that is not a containment building.
“Plasma arc incinerator” means any enclosed device that uses a high intensity electrical discharge or arc as a source of heat followed by an afterburner using controlled flame combustion and which is not listed as an industrial furnace.
“Point source” means any discernible, confined, and discrete conveyance, including, but not limited to, any pipe, ditch, channel, tunnel, conduit, well, discrete fissure, container, rolling stock, concentrated animal feeding operation, or vessel or other floating craft from which pollutants are or may be discharged. This term does not include return flows from irrigated agriculture.
“Publicly owned treatment works” or “POTW” is as defined in 35 Ill. Adm. Code 310.110.
“Qualified groundwater scientist” means a scientist or engineer who has received a baccalaureate or postgraduate degree in the natural sciences or engineering, and has sufficient training and experience in groundwater hydrology and related fields, as demonstrated by state registration, professional certifications, or completion of accredited university courses that enable the individual to make sound professional judgments regarding groundwater monitoring and contaminant rate and transport.
BOARD NOTE: State registration includes, but is not limited to, registration as a professional engineer with the Department of Professional Regulation, pursuant to 225 ILCS 325 and 68 Ill. Adm. Code 1380. Professional certification includes, but is not limited to, certification under the certified groundwater professional program of the National Ground Water Association.
“RCRA” means the Solid Waste Disposal Act, as amended by the Resource Conservation and Recovery Act of 1976, as amended (42 USC 6901 et seq.).
“Regional Administrator” means the Regional Administrator for the USEPA Region in which the facility is located or the Regional Administrator’s designee.
“Remediation waste” means all solid and hazardous wastes, and all media (including groundwater, surface water, soils, and sediments) and debris that are managed for implementing cleanup.
“Remediation waste management site” means a facility where an owner or operator is or will be treating, storing, or disposing of hazardous remediation wastes. A remediation waste management site is not a facility that is subject to corrective action under 35 Ill. Adm. Code 724.201, but a remediation waste management site is subject to corrective action requirements if the site is located in such a facility.
“Replacement unit” means a landfill, surface impoundment, or waste pile unit from which all or substantially all of the waste is removed, and which is subsequently reused to treat, store, or dispose of hazardous waste. Replacement unit does not include a unit from which waste is removed during closure, if the subsequent reuse solely involves the disposal of waste from that unit and other closing units or corrective action areas at the facility, in accordance with a closure or corrective action plan approved by USEPA or the Agency.
“Representative sample” means a sample of a universe or whole (e.g., waste pile, lagoon, groundwater) that can be expected to exhibit the average properties of the universe or whole.
“Runoff” means any rainwater, leachate, or other liquid that drains over land from any part of a facility.
“Runon” means any rainwater, leachate, or other liquid that drains over land onto any part of a facility.
“Saturated zone” or “zone of saturation” means that part of the earth’s crust in which all voids are filled with water.
“SIC Code” means Standard Industrial Classification Code as defined in Standard Industrial Classification Manual, incorporated by reference in Section 720.111.
“Sludge” means any solid, semi-solid, or liquid waste generated from a municipal, commercial, or industrial wastewater treatment plant, water supply treatment plant, or air pollution control facility, exclusive of the treated effluent from a wastewater treatment plant.
“Sludge dryer” means any enclosed thermal treatment device that is used to dehydrate sludge and which has a total thermal input, excluding the heating value of the sludge itself, of 2500 Btu/lb or less of sludge treated on a wet weight wet-weight basis.
“Small quantity generator” means a generator that generates less than 1000 kg of hazardous waste in a calendar month.
“Solid waste” means a solid waste as defined in 35 Ill. Adm. Code 721.102.
“Sorbent” means a material that is used to soak up free liquids by either adsorption or absorption, or both. “Sorb” means to either adsorb or absorb, or both.
“Staging pile” means an accumulation of solid, non-flowing “remediation waste” (as defined in this Section) that is not a containment building and that is used only during remedial operations for temporary storage at a facility. Staging piles must be designated by the Agency according to the requirements of 35 Ill. Adm. Code 724.654.
“State” means any of the several states, the District of Columbia, the Commonwealth of Puerto Rico, the Virgin Islands, Guam, American Samoa, and the Commonwealth of the Northern Mariana Islands.
“Storage” means the holding of hazardous waste for a temporary period, at the end of which the hazardous waste is treated, disposed of, or stored elsewhere.
“Sump” means any pit or reservoir that meets the definition of tank and those troughs or trenches connected to it that serve to collect hazardous waste for transport to hazardous waste storage, treatment, or disposal facilities; except that, as used in the landfill, surface impoundment, and waste pile rules, sump means any lined pit or reservoir that serves to collect liquids drained from a leachate collection and removal system or leak detection system for subsequent removal from the system.
“Surface impoundment” or “impoundment” means a facility or part of a facility that is a natural topographic depression, manmade excavation, or diked area formed primarily of earthen materials (although it may be lined with manmade materials) which that is designed to hold an accumulation of liquid wastes or wastes containing free liquids and which is not an injection well. Examples of surface impoundments are holding, storage, settling, and aeration pits, ponds, and lagoons.
“Tank” means a stationary device, designed to contain an accumulation of hazardous waste that is constructed primarily of nonearthen materials (e.g., wood, concrete, steel, plastic) which that provide structural support.
“Tank system” means a hazardous waste storage or treatment tank and its associated ancillary equipment and containment system.
“TEQ” means toxicity equivalence, the international method of relating the toxicity of various dioxin and furan congeners to the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin.
“Thermal treatment” means the treatment of hazardous waste in a device that uses elevated temperatures as the primary means to change the chemical, physical, or biological character or composition of the hazardous waste. Examples of thermal treatment processes are incineration, molten salt, pyrolysis, calcination, wet air oxidation, and microwave discharge. (See also “incinerator” and “open burning.”.)
“Thermostat” means a temperature control device that contains metallic mercury in an ampule attached to a bimetal sensing element and mercury-containing ampules that have been removed from such a temperature control device in compliance with the requirements of 35 Ill. Adm. Code 733.113(c)(2) or 733.133(c)(2).
“Totally enclosed treatment facility” means a facility for the treatment of hazardous waste that is directly connected to an industrial production process and which is constructed and operated in a manner which that prevents the release of any hazardous waste or any constituent thereof into the environment during treatment. An example is a pipe in which waste acid is neutralized.
“Transfer facility” means any transportation related facility, including loading docks, parking areas, storage areas, and other similar areas where shipments of hazardous waste are held during the normal course of transportation.
“Transport vehicle” means a motor vehicle or rail car used for the transportation of cargo by any mode. Each cargo-carrying body (trailer, railroad freight car, etc.) is a separate transport vehicle.
“Transportation” means the movement of hazardous waste by air, rail, highway, or water.
“Transporter” means a person engaged in the off-site transportation of hazardous waste by air, rail, highway, or water.
“Treatability study” means the following:
A study in which a hazardous waste is subjected to a treatment process to determine the following:
Whether the waste is amenable to the treatment process;
What pretreatment (if any) is required;
The optimal process conditions needed to achieve the desired treatment;
The efficiency of a treatment process for a specific waste or wastes; and
The characteristics and volumes of residuals from a particular treatment process;
Also included in this definition for the purpose of 35 Ill. Adm. Code 721.104(e) and (f) exemptions are liner compatibility, corrosion and other material compatibility studies, and toxicological and health effects studies. A treatability study is not a means to commercially treat or dispose of hazardous waste.
“Treatment” means any method, technique, or process, including neutralization, designed to change the physical, chemical, or biological character or composition of any hazardous waste so as to neutralize the waste, recover energy or material resources from the waste, or render the waste non-hazardous or less hazardous; safer to transport, store, or dispose of; or amenable for recovery, amenable for storage, or reduced in volume.
“Treatment zone” means a soil area of the unsaturated zone of a land treatment unit within which hazardous constituents are degraded, transformed, or immobilized.
“Underground injection” means the subsurface emplacement of fluids through a bored, drilled, or driven well or through a dug well, where the depth of the dug well is greater than the largest surface dimension. (See also “injection well.”.)
“Underground tank” means a device meeting the definition of tank whose entire surface area is totally below the surface of and covered by the ground.
“Unfit-for-use tank system” means a tank system that has been determined, through an integrity assessment or other inspection, to be no longer capable of storing or treating hazardous waste without posing a threat of release of hazardous waste to the environment.
“United States” means the 50 states, the District of Columbia, the Commonwealth of Puerto Rico, the U.S. Virgin Islands, Guam, American Samoa, and the Commonwealth of the Northern Mariana Islands.
“Universal waste” means any of the following hazardous wastes that are managed under the universal waste requirements of 35 Ill. Adm. Code 733:
Batteries, as described in 35 Ill. Adm. Code 733.102;
Pesticides, as described in 35 Ill. Adm. Code 733.103;
Thermostats, as described in 35 Ill. Adm. Code 733.104; and
Lamps, as described in 35 Ill. Adm. Code 733.105.
“Universal waste handler” means either of the following:
A generator (as defined in this Section) of universal waste; or
The owner or operator of a facility, including all contiguous property, that receives universal waste from other universal waste handlers, accumulates the universal waste, and sends that universal waste to another universal waste handler, to a destination facility, or to a foreign destination.
“Universal waste handler” does not mean either of the following:
A person that treats (except under the provisions of Section 733.113(a) or (c) or 733.133(a) or (c)), disposes of, or recycles universal waste; or
A person engaged in the off-site transportation of universal waste by air, rail, highway, or water, including a universal waste transfer facility.
“Universal waste transporter” means a person engaged in the off-site transportation of universal waste by air, rail, highway, or water.
“Unsaturated zone” or “zone of aeration” means the zone between the land surface and the water table.
“Uppermost aquifer” means the geologic formation nearest the natural ground surface that is an aquifer, as well as lower aquifers that are hydraulically interconnected with this aquifer within the facility’s property boundary.
“USDOT” or “Department of Transportation” means the United States Department of Transportation.
“Used oil” means any oil that has been refined from crude oil, or any synthetic oil, that has been used and as a result of such use is contaminated by physical or chemical impurities.
“USEPA” or “EPA” or “U.S. EPA” means the United States Environmental Protection Agency.
“Vessel” includes every description of watercraft used or capable of being used as a means of transportation on the water.
“Wastewater treatment unit” means a device of which the following is true:
It is part of a wastewater treatment facility that has an NPDES permit pursuant to 35 Ill. Adm. Code 309 or a pretreatment permit or authorization to discharge pursuant to 35 Ill. Adm. Code 310; and
It receives and treats or stores an influent wastewater that is a hazardous waste as defined in 35 Ill. Adm. Code 721.103, or generates and accumulates a wastewater treatment sludge which that is a hazardous waste as defined in 35 Ill. Adm. Code 721.103, or treats or stores a wastewater treatment sludge which that is a hazardous waste as defined in 35 Ill. Adm. Code 721.103; and
It meets the definition of tank or tank system in this Section.
“Water (bulk shipment)” means the bulk transportation of hazardous waste that is loaded or carried on board a vessel without containers or labels.
“Well” means any shaft or pit dug or bored into the earth, generally of a cylindrical form, and often walled with bricks or tubing to prevent the earth from caving in.
“Well injection” (See “underground injection.”.)
“Zone of engineering control” means an area under the control of the owner or operator that, upon detection of a hazardous waste release, can be readily cleaned up prior to the release of hazardous waste or hazardous constituents to groundwater or surface water.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 720.111 | References |
The following documents are incorporated by reference for the purposes of this Part and 35 Ill. Adm. Code 703 through 705, 721 through 726, 728, 730, 733, 738, and 739:
a) | Non-Regulatory Government Publications and Publications of Recognized Organizations and Associations: |
ACI. Available from the American Concrete Institute, Box 19150, Redford Station, Detroit, Michigan 48219:
ACI 318-83: “Building Code Requirements for Reinforced Concrete,” adopted September 1983.
ANSI. Available from the American National Standards Institute, 1430 Broadway, New York, New York 10018, 212-354-3300:
ANSI B31.3 and B31.4. See ASME/ANSI B31.3 and B31.4.
API. Available from the American Petroleum Institute, 1220 L Street, N.W., Washington, D.C. 20005, 202-682-8000:
“Cathodic Protection of Underground Petroleum Storage Tanks and Piping Systems,” API Recommended Practice 1632, Second Edition, December 1987.
“Evaporative Loss from External Floating-Roof Tanks,” API Publication 2517, Third Edition, February 1989.
“Guide for Inspection of Refinery Equipment, Chapter XIII, Atmospheric and Low Pressure Storage Tanks,” 4th Edition, 1981, reaffirmed December 1987.
“Installation of Underground Petroleum Storage Systems,” API Recommended Practice 1615, Fourth Edition, November 1987.
ASME. Available from the American Society of Mechanical Engineers, 345 East 47th Street, New York, NY 10017, 212-705-7722:
“Chemical Plant and Petroleum Refinery Piping,” ASME/ANSI B31.3-1987, as supplemented by B31.3a-1988 and B31.3b-1988. Also available from ANSI.
“Liquid Transportation Systems for Hydrocarbons, Liquid Petroleum Gas, Anhydrous Ammonia, and Alcohols,” ASME/ANSI B31.4-1986, as supplemented by B31.4a-1987. Also available from ANSI.
ASTM. Available from American Society for Testing and Materials, 100 Barr Harbor Drive, West Conshohocken, PA 19428-2959, 610-832-9585:
ASTM C 94-90, Standard Specification for Ready-Mixed Concrete, approved March 30, 1990.
ASTM D 88-87, Standard Test Method for Saybolt Viscosity, April 24, 1981, reapproved January 1987.
ASTM D 93-85, Standard Test Methods for Flash Point by Pensky-Martens Closed Tester, approved October 25, 1985.
ASTM D 140–70, Standard Practice for Sampling Bituminous Materials, approved 1970.
ASTM D 346–75, Standard Practice for Collection and Preparation of Coke Samples for Laboratory Analysis, approved 1975.
ASTM D 420–69, Guide to Site Characterization for Engineering, Design, and Construction Purposes, approved 1969.
ASTM D 1452–65, Standard Practice for Soil Investigation and Sampling by Auger Borings, approved 1965.
ASTM D 1946-90, Standard Practice for Analysis of Reformed Gas by Gas Chromatography, approved March 30, 1990.
ASTM D 2161-87, Standard Practice for Conversion of Kinematic Viscosity to Saybolt Universal or to Saybolt Furol Viscosity, March 27, 1987.
ASTM D 2234–76, Standard Practice for Collection of a Gross Sample of Coal, approved 1976.
ASTM D 2267-88, Standard Test Method for Aromatics in Light Naphthas and Aviation Gasolines by Gas Chromatography, approved November 17, 1988.
ASTM D 2382-88, Standard Test Method for Heat of Combustion of Hydrocarbon Fuels by Bomb Calorimeter (High Precision Method), approved October 31, 1988.
ASTM D 2879-92, Standard Test Method for Vapor Pressure-Temperature Relationship and Initial Decomposition Temperature of Liquids by Isoteniscope, approved 1992.
ASTM D 3828-87, Standard Test Methods for Flash Point of Liquids by Setaflash Closed Tester, approved December 14, 1988.
ASTM E 168-88, Standard Practices for General Techniques of Infrared Quantitative Analysis, approved May 27, 1988.
ASTM E 169-87, Standard Practices for General Techniques of Ultraviolet-Visible Quantitative Analysis, approved February 1, 1987.
ASTM E 260-85, Standard Practice for Packed Column Gas Chromatography, approved June 28, 1985.
ASTM Method G 21-70 (1984a), Standard Practice for Determining Resistance of Synthetic Polymer Materials to Fungi.
ASTM Method G 22-76 (1984b), Standard Practice for Determining Resistance of Plastics to Bacteria.
MICE. Methods Information Communication Exchange Service, 703-821-4690:
“Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA publication number SW-846, Update IIIA (April 1998).
GPO. Available from the Superintendent of Documents, U.S. Government Printing Office, Washington, D.C. 20402,202-512-1800:
Standard Industrial Classification Manual (1972), and 1977 Supplement, republished in 1983.
“Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA Publication number SW-846 (Third Edition, November 1986), as amended by Updates I (July 1992), II (September 1994), IIA (August, 1993), IIB (January 1995), and III (December 1996) (document number 955-001-00000-1).
NACE. Available from the National Association of Corrosion Engineers, 1400 South Creek Dr., Houston, TX 77084, 713-492-0535:
“Control of External Corrosion on Metallic Buried, Partially Buried, or Submerged Liquid Storage Systems,” NACE Recommended Practice RP-02-85, approved March 1985.
NFPA. Available from the National Fire Protection Association, Batterymarch Park, Boston, MA 02269, 617-770-3000 or 800-344-3555:
“Flammable and Combustible Liquids Code,” NFPA 30, issued July 17, 1987. Also available from ANSI.
NTIS. Available from the U.S. Department of Commerce, National Technical Information Service, 5285 Port Royal Road, Springfield, VA 22161, 703-605-6000 or 800-553-6847:
APTI Course 415: Control of Gaseous Emissions, PB80-208895, December 1981.
“Generic Quality Assurance Project Plan for Land Disposal Restrictions Program,” EPA/530-SW-87-011, March 15, 1987 (document number PB88-170766).
“Guideline on Air Quality Models,” Revised 1986 (document number PB86-245-248 (Guideline) and PB88-150-958 (Supplement), also set forth at 40 CFR 51, Appendix W).
“Method 164, Revision A, n-Hexane Extractable Material (HEM; Oil and Grease) and Silica Gel Treated n-Hexane Extractable Material (SGT-HEM; Non-polar Material) by Extraction and Gravimetry” (document number PB99-121949).
“Methods for Chemical Analysis of Water and Wastes,” Third Edition, March 1983 (document number PB84-128677).
“Methods Manual for Compliance with BIF Regulations,” December 1990 (document number PB91-120-006).
“Petitions to Delist Hazardous Wastes — A Guidance Manual, Second Edition,” EPA/530-R-93-007, March 1993 (document number PB93-169 365).
“Screening Procedures for Estimating the Air Quality Impact of Stationary Sources,” October 1992, publication number EPA-450/R-92-019.
“Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” USEPA Publication number SW-846 (Third Edition, November 1986), as amended by Updates I (July 1992), II (September 1994), IIA (August 1993), IIB (January 1995), III (December 1996), and IIIA (April 1998) (document number 955-001-00000-1).
OECD. Organisation for Economic Co-operation and Development, Environment Directorate, 2 rue Andre Pascal, 75775 Paris Cedex 16, France:
OECD Guideline for Testing of Chemicals, Method 301B: “CO2 Evolution (Modified Sturm Test),” adopted 17 July 1992.
Table 2.B of the Annex of OECD Council Decision C(88)90(Final) of 27 May 1988.
STI. Available from the Steel Tank Institute, 728 Anthony Trail, Northbrook, IL 60062, 708-498-1980:
“Standard for Dual Wall Underground Steel Storage Tanks” (1986).
USDOD. Available from the United States Department of Defense:
“DOD Ammunition and Explosives Safety Standards” (DOD 6055.9-STD), as in effect in July 1999.
The Motor Vehicle Inspection Report (DD Form 626), as in effect on November 8, 1995.
Requisition Tracking Form (DD Form 1348), as in effect on November 8, 1995.
The Signature and Tally Record (DD Form 1907), as in effect on November 8, 1995.
Special Instructions for Motor Vehicle Drivers (DD Form 836), as in effect on November 8, 1995.
USEPA. Available from United States Environmental Protection Agency, Office of Drinking Water, State Programs Division, WH 550 E, Washington, D.C. 20460:
“Technical Assistance Document: Corrosion, Its Detection and Control in Injection Wells,” EPA 570/9-87-002, August 1987.
USEPA. Available from Receptor Analysis Branch, USEPA (MD-14), Research Triangle Park, NC 27711:
“Samplers and Sampling Procedures for Hazardous Waste Streams,” EPA 600/2–80–018, January 1980.
“Screening Procedures for Estimating the Air Quality Impact of Stationary Sources, Revised,” October 1992, publication number EPA-450/R-92-019.
USEPA. Available from RCRA Docket Information Center (RIC), 1235 Jefferson Davis Highway, first floor, Arlington, VA 22202, 401 M Street, SW, Washington, D.C. 20460 (phone: 202-566-0270) (Docket # F-94-IEHF-FFFFF):
OECD Amber List of Wastes, Appendix 4 to the OECD Council Decision C(92)39/FINAL (Concerning the Control of Transfrontier Movements of Wastes Destined for Recovery Operations) (May 1993).
OECD Green List of Wastes, Appendix 3 to the OECD Council Decision C(92)39/FINAL (Concerning the Control of Transfrontier Movements of Wastes Destined for Recovery Operations) (May 1994).
OECD Red List of Wastes, Appendix 5 to the OECD Council Decision C(92)39/FINAL (Concerning the Control of Transfrontier Movements of Wastes Destined for Recovery Operations) (May 1993).
Table 2.B of the Annex of OECD Council Decision C(88)90(Final) (May 27, 1988).
USEPA Region 6. Available from United States Environmental Protection Agency, Region 6, Multimedia Permitting and Planning Division, 1445 Ross Avenue, Dallas, TX 75202 (phone: 214-665-7430):
“EPA RCRA Delisting Program--Guidance Manual for the Petitioner,” March 23, 2000.
USGSA. Available from the United States Government Services Administration:
Government Bill of Lading (GBL) (GSA Standard Form 1109), as in effect on November 8, 1995.
b) | Code of Federal Regulations. Available from the Superintendent of Documents, U.S. Government Printing Office, Washington, D.C. 20401, 202-783-3238: |
10 CFR 20.2006 (2002)
10 CFR 20, Appendix B (2002)
10 CFR 71 (2002)
40 CFR 51.100(ii) (2002)
40 CFR 51, Appendix W (2002)
40 CFR 52.741, Appendix B (2002)
40 CFR 60 (2002)
40 CFR 61, Subpart V (2002)
40 CFR 63 (2002), as amended at 67 Fed. Reg. 77687 (December 19, 2002)
40 CFR 136 (2002), as amended at 67 Fed. Reg. 65220 (October 23, 2002) and 67 Fed. Reg. 65876 (October 29, 2002)
40 CFR 142 (2002)
40 CFR 220 (2002)
40 CFR 232.2 (2002)
40 CFR 260.20 (2002)
40 CFR 264 (2002)
40 CFR 268.41 (1990)
40 CFR 268, Appendix IX (2002)
40 CFR 270.5 (2002)
40 CFR 302.4, 302.5, and 302.6 (2002)
40 CFR 423, appendix A (2002)
40 CFR 761 (2002)
49 CFR 107 (2001) (2002)
49 CFR 171 (2001) (2002)
49 CFR 172 (2001) (2002)
49 CFR 173 (2001) (2002)
49 CFR 178 (2001) (2002)
49 CFR 179 (2001) (2002)
c) | Federal Statutes |
Sections 201(v), 201(w), and 360b(j) of the Federal Food, Drug, and Cosmetic Act (FFDCA; 21 USC 321(v), 321(w), and 512(j)), as amended through October 25, 1994.
Section 1412 of the Department of Defense Authorization Act of 1986, Pub. L. 99-145, 50 USC 1521(j)(1) (1997).
d) | This Section incorporates no later editions or amendments. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART C: RULEMAKING PETITIONS AND OTHER PROCEDURES
Section 720.120 | Rulemaking |
a) | Any person may petition the Board to adopt as State regulations rules that are identical in substance with newly-adopted federal amendments or regulations. The petition |
b) | Any person may petition the Board to adopt amendments or additional regulations not identical in substance with federal regulations. Such proposal |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 720.121 | Alternative Equivalent Testing Methods |
a) | The Agency has no authority to alter the universe of regulated wastes. Modification of testing methods that are stated in 35 Ill. Adm. Code 721 requires rulemaking pursuant to Section 720.120. However, deviation from these methods is allowed under 35 Ill. Adm. Code 721, as observed, for example, |
b) | The Agency may approve alternative equivalent testing methods for a particular person’s use to determine whether specified waste streams are subject to these regulations. This |
c) | The testing methods specified in 35 Ill. Adm. Code 721 or alternative equivalent testing methods approved by the Agency need not be applied to identify or distinguish waste streams that are known, admitted, or assumed to be subject to these regulations. In this case, any method may be used, subject to the Agency’s authority |
d) | Any petition to the Board or request to the Agency concerning alternative equivalent testing methods must include the information required by 40 CFR Section 260.21(b). |
e) | Alternative equivalent testing methods will not be approved if the result of the approval would make the Illinois RCRA Subtitle C program less than substantially equivalent to the federal. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 720.122 | Waste Delisting |
a) | Any person seeking to exclude a waste from a particular generating facility from the lists in Subpart D of 35 Ill. Adm. Code 721 |
1) | The petitioner demonstrates that the waste produced by a particular generating facility does not meet any of the criteria under which the waste was listed as a hazardous or acute hazardous waste; and |
2) | If the Board determines that there is a reasonable basis to believe that factors (including additional constituents) other than those for which the waste was listed could cause the waste to be a hazardous waste, that such factors do not warrant retaining the waste as a hazardous waste. A Board determination under the preceding sentence must be made by reliance on, and in a manner consistent with, |
b) | Listed wastes and mixtures. A person may also petition the Board to exclude from 35 Ill. Adm. Code 721.103(a)(2)(B) or (a)(2)(C), a waste that is described in these Sections and is either a waste listed in Subpart D of 35 Ill. Adm. Code 721 |
c) | Ignitable, corrosive, reactive and toxicity characteristic wastes. If the waste is listed in codes “I,” |
1) | The petitioner |
2) | Based on a complete petition, the Board will determine, if it has a reasonable basis to believe that factors (including additional constituents) other than those for which the waste was listed could cause the waste to be hazardous waste, that such factors do not warrant retaining the waste as a hazardous waste. A Board determination under the preceding sentence must be made by reliance on, and in a manner consistent with, |
d) | Toxic waste. If the waste is listed in code “T” in Subpart D of 35 Ill. Adm. Code 721 |
1) | The petitioner |
A) | |
B) | Although containing one or more of the hazardous constituents (as defined in Appendix G of 35 Ill. Adm. Code 721 |
2) | Based on a complete petition, the Board will determine, if it has a reasonable basis to believe that factors (including additional constituents) other than those for which the waste was listed could cause the waste to be hazardous waste, that such factors do not warrant retaining the waste as a hazardous waste. |
3) | The petitioner |
4) | A waste that is so excluded, however, may still be a hazardous waste by operation of Subpart C of 35 Ill. Adm. Code 721 |
e) | Acute hazardous waste. If the waste is listed with the code “H” in Subpart D of 35 Ill. Adm. Code 721 |
1) | The petitioner |
2) | Based on a complete petition, the Board will determine, if it has a reasonable basis to believe that factors (including additional constituents) other than those for which the waste was listed could cause the waste to be hazardous waste, that such factors do not warrant retaining the waste as a hazardous waste. A Board determination under the preceding sentence must be made by reliance on, and in a manner consistent with, |
3) | The petitioner |
4) | A waste that is so excluded, however, may still be a hazardous waste by operation of Subpart C of 35 Ill. Adm. Code 721 |
h) | Demonstration samples must consist of enough representative samples, but in no case less than four samples, taken over a period of time sufficient to represent the variability or the uniformity of the waste. |
i) | Each petition must include, in addition to the information required by subsection (n) |
1) | The name and address of the laboratory facility performing the sampling or tests of the waste; |
2) | The names and qualifications of the persons sampling and testing the waste; |
3) | The dates of sampling and testing; |
4) | The location of the generating facility; |
5) | A description of the manufacturing processes or other operations and feed materials producing the waste and an assessment of whether such processes, operations, or feed materials can or might produce a waste that is not covered by the demonstration; |
6) | A description of the waste and an estimate of the average and maximum monthly and annual quantities of waste covered by the demonstration; |
7) | Pertinent data on and discussion of the factors delineated in the respective criterion for listing a hazardous waste, where the demonstration is based on the factors in 35 Ill. Adm. Code 721.111(a)(3); |
8) | A description of the methodologies and equipment used to obtain the representative samples; |
9) | A description of the sample handling and preparation techniques, including techniques used for extraction, containerization, and preservation of the samples; |
10) | A description of the tests performed (including results); |
11) | The names and model numbers of the instruments used in performing the tests; and |
12) | The following statement signed by the generator or the generator’s authorized representative: |
I certify under penalty of law that I have personally examined and am familiar with the information submitted in this demonstration 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.
j) | After receiving a petition, the Board may request any additional information that the Board needs to evaluate the petition. |
k) | An exclusion will only apply to the waste generated at the individual facility covered by the demonstration and will not apply to waste from any other facility. |
l) | The Board will exclude only part of the waste for which the demonstration is submitted if the Board determines that variability of the waste justifies a partial exclusion. |
BOARD NOTE: See “Petitions to Delist--A Guidance Manual”, “EPA RCRA Delisting Program--Guidance Manual for the Petitioner,” incorporated by reference in Section 720.111.
m) | Delisting of specific wastes from specific sources that have been adopted by |
n) | Delistings that have not been adopted by |
1) | In accordance with 35 Ill. Adm. Code |
U.S. EPAUSEPA
Office of Solid Waste and Emergency Response
1200 Pennsylvania Avenue, NW
Washington, D.C. 20460
U.S. EPAUSEPA, Region V 5
230 S. Dearborn Street
77 West Jackson Boulevard
Chicago, IL 60604
2) | The Board will mail copies of all opinions and orders to |
3) | In conjunction with the normal updating of the RCRA regulations, the Board will maintain, in Appendix I of 35 Ill. Adm. Code 721 |
o) | The Agency may determine in a permit or a letter directed to a generator that, based on 35 Ill. Adm. Code 721, a waste from a particular source is not subject to these regulations. Such a finding is evidence against the Agency in any subsequent proceedings but |
p) | Any petition to delist directed to the Board or request for determination directed to the Agency must include a showing that the waste will be generated or managed in Illinois. |
q) | The Board will not grant any petition that would render the Illinois RCRA program less stringent than if the decision were made by |
r) | Delistings apply only within Illinois. Generators |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 720.123 | Petitions for Regulation as Universal Waste |
a) | Any person seeking to add a hazardous waste or a category of hazardous waste to the universal waste regulations of 35 Ill. Adm. Code 733 may petition for a regulatory amendment under this Section, Section 720.120, and Subpart G of 35 Ill. Adm. Code 733 |
b) | Petition and Demonstration. |
1) | To be successful, the petitioner must demonstrate each of the following: |
A) | That regulation under the universal waste regulations of 35 Ill. Adm. Code 733 is appropriate for the waste or category of waste; |
B) | That regulation under 35 Ill. Adm. Code 733 will improve management practices for the waste or category of waste; and |
C) | That regulation under 35 Ill. Adm. Code 733 will improve implementation of the hazardous waste program. |
2) | The petition must include the information required by Section 720.120(b). The petition should also address as many of the factors listed in 35 Ill. Adm. Code 733.181 as are appropriate for the waste or category of waste addressed in the petition. |
c) | The Board will grant or deny a petition using the factors listed in 35 Ill. Adm. Code 733.181. The decision will be based on the weight of evidence that shows the following with regard to regulation under 35 Ill. Adm. Code 733: |
1) | That it is appropriate for the waste or category of waste, |
2) | That it will improve management practices for the waste or category of waste, and |
3) | That it will improve implementation of the hazardous waste program. |
d) | The Board may request additional information to that set forth in 35 Ill. Adm. Code 733.181, as needed to evaluate the merits of the petition. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 720.132 | Boiler Determinations |
In accordance with the standards and criteria in Section 720.110 (definition of “boiler”), and the procedures in 720.133, the Board will determine on a case-by-case basis that certain enclosed devices using controlled flame combustion are boilers, even though they do not otherwise meet the definition of boiler contained in Section 720.110, after considering the following criteria:
a) | The extent to which the unit has provisions for recovering and exporting thermal energy in the form of steam, heated fluids or heated gases; |
b) | The extent to which the combustion chamber and energy recovery equipment are of integral design; |
c) | The efficiency of energy recovery, calculated in terms of the recovered energy compared with the thermal value of the fuel; |
d) | The extent to which exported energy is utilized; |
e) | The extent to which the device is in common and customary use as a “boiler” functioning primarily to produce steam, heated fluids or heated gases; and |
f) | Other relevant factors. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 720.133 | Procedures for Determinations |
The Board will use the procedures of Subpart D of 35 Ill. Adm. Code 106 104 for determining whether a material is a solid waste or for determining whether a particular enclosed flame combustion device is a boiler.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 720.140 | Additional |
a) | The Agency may decide on a case-by-case basis that persons accumulating or storing the recyclable materials described in 35 Ill. Adm. Code 721.106(a)(2)(D) should be regulated under 35 Ill. Adm. Code 721.106(b) and (c) rather than under the provisions of Subpart F of 35 Ill. Adm. Code 726 |
1) | The types of materials accumulated or stored and the amounts accumulated or stored; |
2) | The method of accumulation or storage; |
3) | The length of time the materials have been accumulated or stored before being reclaimed; |
4) | Whether any contaminants are being released into the environment, or are likely to be so released; and |
5) | Other relevant factors. |
b) | The procedures for this decision are set forth in Section 720.141. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 720.141 | Procedures for |
The Agency shall must use the following procedures when determining whether to regulate hazardous waste recycling activities described in 35 Ill. Adm. Code 721.106(a)(2)(D) under the provisions of 35 Ill Adm. Code 721.106(b) and (c) rather than under the provisions of Subpart F of 35 Ill. Adm. Code 726.Subpart F.
a) | If a generator is accumulating the waste, the Agency |
b) | If the person is accumulating the recyclable material as a storage facility, the notice must state that the person |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 720.Appendix A | Overview of 40 CFR, Subtitle C Regulations |
See Appendix I to 40 CFR 260.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 721
IDENTIFICATION AND LISTING OF HAZARDOUS WASTE
SUBPART A: GENERAL PROVISIONS
Section
721.101 | Purpose and Scope |
721.102 | Definition of Solid Waste |
721.103 | Definition of Hazardous Waste |
721.104 | Exclusions |
721.105 | Special Requirements for Hazardous Waste Generated by Small Quantity Generators |
721.106 | Requirements for Recyclable Materials |
721.107 | Residues of Hazardous Waste in Empty Containers |
721.108 | PCB Wastes Regulated under TSCA |
721.109 | Requirements for Universal Waste |
SUBPART B: CRITERIA FOR IDENTIFYING THE CHARACTERISTICS OF HAZARDOUS WASTE AND FOR LISTING HAZARDOUS WASTES
Section
721.110 | Criteria for Identifying the Characteristics of Hazardous Waste |
721.111 | Criteria for Listing Hazardous Waste |
SUBPART C: CHARACTERISTICS OF HAZARDOUS WASTE
Section
721.120 | General |
721.121 | Characteristic of Ignitability |
721.122 | Characteristic of Corrosivity |
721.123 | Characteristic of Reactivity |
721.124 | Toxicity Characteristic |
SUBPART D: LISTS OF HAZARDOUS WASTE
Section
721.130 | General |
721.131 | Hazardous Wastes from Nonspecific Sources |
721.132 | Hazardous Waste from Specific Sources |
721.133 | Discarded Commercial Chemical Products, Off-Specification Species, Container Residues, and Spill Residues Thereof |
721.135 | Wood Preserving Wastes |
721.138 | Comparable or Syngas Fuel Exclusion |
Representative Sampling Methods | |
Method 1311 Toxicity Characteristic Leaching Procedure (TCLP) | |
Chemical Analysis Test Methods | |
Table A | Analytical Characteristics of Organic Chemicals (Repealed) |
Table B | Analytical Characteristics of Inorganic Species (Repealed) |
Table C | Sample Preparation/Sample Introduction Techniques (Repealed) |
Basis for Listing Hazardous Wastes | |
Hazardous Constituents | |
Wastes Excluded by Administrative Action | |
Table A | Wastes Excluded by |
Table B | Wastes Excluded by USEPA under 40 CFR 260.20 and 260.22 from Specific Sources |
Table C | Wastes Excluded by |
Table D | Wastes Excluded by the Board by Adjusted Standard |
Method of Analysis for Chlorinated Dibenzo-p-Dioxins and Dibenzofurans (Repealed) | |
Table to Section 721.138 | |
Table to Section 721.102 | |
AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].
SOURCE: Adopted in R81-22 at 5 Ill. Reg. 9781, effective May 17, 1982; amended and codified in R81-22 at 6 Ill. Reg. 4828, effective May 17, 1982; amended in R82-18 at 7 Ill. Reg. 2518, effective February 22, 1983; amended in R82-19 at 7 Ill. Reg. 13999, effective October 12, 1983; amended in R84-34, 61 at 8 Ill. Reg. 24562, effective December 11, 1984; amended in R84-9 at 9 Ill. Reg. 11834, effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 998, effective January 2, 1986; amended in R85-2 at 10 Ill. Reg. 8112, effective May 2, 1986; amended in R86-1 at 10 Ill. Reg. 14002, effective August 12, 1986; amended in R86-19 at 10 Ill. Reg. 20647, effective December 2, 1986; amended in R86-28 at 11 Ill. Reg. 6035, effective March 24, 1987; amended in R86-46 at 11 Ill. Reg. 13466, effective August 4, 1987; amended in R87-32 at 11 Ill. Reg. 16698, effective September 30, 1987; amended in R87-5 at 11 Ill. Reg. 19303, effective November 12, 1987; amended in R87-26 at 12 Ill. Reg. 2456, effective January 15, 1988; amended in R87-30 at 12 Ill. Reg. 12070, effective July 12, 1988; amended in R87-39 at 12 Ill. Reg. 13006, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 382, effective December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18300, effective November 13, 1989; amended in R90-2 at 14 Ill. Reg. 14401, effective August 22, 1990; amended in R90-10 at 14 Ill. Reg. 16472, effective September 25, 1990; amended in R90-17 at 15 Ill. Reg. 7950, effective May 9, 1991; amended in R90-11 at 15 Ill. Reg. 9332, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14473, effective September 30, 1991; amended in R91-12 at 16 Ill. Reg. 2155, effective January 27, 1992; amended in R91-26 at 16 Ill. Reg. 2600, effective February 3, 1992; amended in R91-13 at 16 Ill. Reg. 9519, effective June 9, 1992; amended in R92-1 at 16 Ill. Reg. 17666, effective November 6, 1992; amended in R92-10 at 17 Ill. Reg. 5650, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20568, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6741, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12175, effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17490, effective November 23, 1994; amended in R95-6 at 19 Ill. Reg. 9522, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 10963, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 275, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7615, effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17531, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1718, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9135, effective July 26, 1999; amended in R00-13 at 24 Ill. Reg. 9481, effective June 20, 2000; amended in R01-3 at 25 Ill. Reg. 1281, effective January 11, 2001; amended in R01-21/R01-23 at 25 Ill. Reg. 9108, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. 6584, effective April 22, 2002; amended in R03-18 at 27 Ill. Reg. ________, effective ______________________.
SUBPART A: GENERAL PROVISIONS
Section 721.101 | Purpose and Scope |
a) | This Part identifies those solid wastes |
1) | Subpart A of this Part defines the terms “solid waste” and “hazardous waste,” identifies those wastes |
2) | Subpart B of this Part sets forth the criteria used to identify characteristics of hazardous waste and to list particular hazardous wastes. |
3) | Subpart C of this Part identifies characteristics of hazardous wastes. |
4) | Subpart D of this Part lists particular hazardous wastes. |
b) | Limitations on definition of solid waste |
1) | The definition of solid waste contained in this Part applies only to wastes that also are hazardous for purposes of the regulations implementing Subtitle C of RCRA. For example, it does not apply to materials (such as non-hazardous scrap, paper, textiles or rubber) that are not otherwise hazardous wastes and that are recycled. |
2) | This Part identifies only some of the materials |
c) | For the purposes of Sections 721.102 and 721.106 the following definitions apply: |
1) | A “spent material” is any material that has been used and as a result of contamination can no longer serve the purpose for which it was produced without processing. |
2) | “Sludge” has the same meaning used in 35 Ill. Adm. Code 720.110. |
3) | A “by-product” is a material that is not one of the primary products of a production process and is not solely or separately produced by the production process. Examples are process residues such as slags or distillation column bottoms. The term does not include a co-product that is produced for the general public’s use and is ordinarily used in the form it is produced by the process. |
4) | A material is “reclaimed” if it is processed to recover a usable product, or if it is regenerated. Examples are recovery of lead values from spent batteries and regeneration of spent solvents. |
5) | A material is “used or reused” if |
A) | |
B) | |
6) | “Scrap metal” is bits and pieces of metal parts (e.g., bars, turnings, rods, sheets, wire) or metal pieces that may be combined together with bolts or soldering (e.g., radiators, scrap automobiles, railroad box cars) |
7) | A material is “recycled” if it is used, reused or reclaimed. |
8) | A material is “accumulated speculatively” if it is accumulated before being recycled. A material is not accumulated speculatively, however, if the person accumulating it can show that the material is potentially recyclable and has a feasible means of being recycled; and that, |
9) | “Excluded scrap metal” is processed scrap metal, unprocessed home scrap metal, and unprocessed prompt scrap metal. |
10) | “Processed scrap metal” is scrap metal that has been manually or physically altered to either separate it into distinct materials to enhance economic value or to improve the handling of materials. Processed scrap metal includes, but is not limited to, scrap metal that has been baled, shredded, sheared, chopped, crushed, flattened, cut, melted, or separated by metal type (i.e., sorted), and fines, drosses and related materials that have been agglomerated. (Note: shredded circuit boards being sent for recycling are not considered processed scrap metal. They are covered under the exclusion from the definition of solid waste for shredded circuit boards being recycled (Section 721.104(a)(13))). |
11) | “Home scrap metal” is scrap metal as generated by steel mills, foundries, and refineries, such as turnings, cuttings, punchings, and borings. |
12) | “Prompt scrap metal” is scrap metal as generated by the metal working/fabrication industries, and it includes such scrap metal as turnings, cuttings, punchings, and borings. Prompt scrap metal is also known as industrial or new scrap metal. |
d) | The Agency has inspection authority pursuant to Section 3007 of RCRA and Section 4 of the Environmental Protection Act [415 ILCS 5/4]. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.102 | Definition of Solid Waste |
a) | Solid waste. |
1) | A solid waste is any discarded material that is not excluded by Section 721.104(a) or that is not excluded pursuant to 35 Ill. Adm. Code 720.130 and 720.131. |
2) | A discarded material is any material that is described as follows: |
A) | Abandoned, as explained in subsection (b) of this Section; |
B) | Recycled, as explained in subsection (c) of this Section; |
C) | Considered inherently waste-like, as explained in subsection (d) of this Section; or |
D) | A military munition identified as a solid waste in 35 Ill. Adm. Code 726.302. |
b) | |
1) | |
2) | |
3) | |
c) | |
1) | |
A) | |
i) | |
ii) | |
B) | However, a commercial chemical |
2) | |
A) | |
i) | |
ii) | |
iii) | |
B) | However, a commercial chemical |
3) | Reclaimed. |
4) | Accumulated speculatively. |
d) | Inherently waste-like materials. The following materials are solid wastes when they are recycled in any manner: |
1) | Hazardous waste numbers F020, F021 (unless used as an ingredient to make a product at the site of generation), F022, F023, F026, and F028. |
2) | |
A) | The material must contain a bromine concentration of at least 45 percent; |
B) | The material must contain less than a total of one percent of toxic organic compounds listed in Appendix H of this Part; and |
C) | The material is processed continually on-site in the halogen acid furnace via direct conveyance (hard piping). |
3) | The following criteria are used to add wastes to the list: |
A) | Disposal method or toxicity. |
i) | The |
ii) | The |
B) | The material may pose a substantial hazard to human health and the environment when recycled. |
e) | Materials that are not solid waste when recycled. |
1) | |
A) | |
B) | |
C) | |
2) | The following materials are solid wastes, even if the recycling involves use, reuse, or return to the original process (described in subsections (e)(1)(A) through (e)(1)(C) of this Section): |
A) | |
B) | |
C) | |
D) | |
f) | Documentation of claims that |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.103 | Definition of Hazardous Waste |
a) | A solid waste, as defined in Section 721.102, is a hazardous waste if the following is true of the waste: |
1) | It is not excluded from regulation as a hazardous waste under Section 721.104(b); and |
2) | It meets any of the following criteria: |
A) | It exhibits any of the characteristics of hazardous waste identified in Subpart C of this Part. However, any mixture of a waste from the extraction, beneficiation, and processing of ores and minerals excluded under Section 721.104(b)(7) and any other solid waste exhibiting a characteristic of hazardous waste under Subpart C of this Part is a hazardous waste only if it exhibits a characteristic that would not have been exhibited by the excluded waste alone if such mixture had not occurred, or if the mixture continues to exhibit any of the characteristics exhibited by the non-excluded wastes prior to mixture. Further, for the purposes of applying the toxicity characteristic to such mixtures, the mixture is also a hazardous waste if it exceeds the maximum concentration for any contaminant listed in Section 721.124 that would not have been exceeded by the excluded waste alone if the mixture had not occurred or if it continues to exceed the maximum concentration for any contaminant exceeded by the nonexempt waste prior to mixture. |
B) | It is listed in Subpart D of this Part and has not been excluded from the lists in Subpart D of this Part under 35 Ill. Adm. Code 720.120 and 720.122. |
C) | This subsection corresponds with 40 CFR 261.3(a)(2)(iii), which USEPA removed and marked as “reserved” at 66 Fed. Reg. 27266 (May 16, 2001). This statement maintains structural consistency with the federal regulations. |
D) | It is a mixture of solid waste and one or more hazardous wastes listed in Subpart D of this Part and has not been excluded from this subsection (a)(2) under 35 Ill. Adm. Code 720.120 and 720.122, subsection (g) of this Section, or subsection (h) of this Section; however, the following mixtures of solid wastes and hazardous wastes listed in Subpart D of this Part are not hazardous wastes (except by application of subsection (a)(2)(A) or (a)(2)(B) of this Section) if the generator demonstrates that the mixture consists of wastewater the discharge of which is subject to regulation under either 35 Ill. Adm. Code 309 or 310 (including wastewater at facilities that have eliminated the discharge of wastewater) and the following is true of the waste: |
i) | |
ii) | |
iii) | |
iv) | |
v) | |
vi) | |
vii) | |
E) | Rebuttable presumption for used oil. Used oil containing more than 1,000 ppm total halogens is presumed to be a hazardous waste because it has been mixed with halogenated hazardous waste listed in Subpart D of this Part. Persons may rebut this presumption by demonstrating that the used oil does not contain hazardous waste (for example, by using an analytical method from SW-846, incorporated by reference at 35 Ill. Adm. Code 720.111, to show that the used oil does not contain significant concentrations of halogenated hazardous constituents listed in Appendix H of this Part). |
i) | The rebuttable presumption does not apply to a metalworking |
ii) | The rebuttable presumption does not apply to a used |
b) | A solid waste that is not excluded from regulation under subsection (a)(1) of this Section becomes a hazardous waste when any of the following events occur: |
1) | In the case of a waste listed in Subpart D of this Part, when the waste first meets the listing description set forth in Subpart D of this Part. |
2) | In the case of a mixture of solid waste and one or more listed hazardous wastes, when a hazardous waste listed in Subpart D of this Part is first added to the solid waste. |
3) | In the case of any other waste (including a waste mixture), when the waste exhibits any of the characteristics identified in Subpart C of this Part. |
c) | Unless and until it meets the criteria of subsection (d) of this Section, a hazardous waste will remain a hazardous waste. |
BOARD NOTE: This subsection corresponds with 40 CFR 261.3(c)(1). The Board has codified 40 CFR 261.3(c)(2) at subsection (e) of this Section.
d) | Any solid waste described in subsection |
1) | In the case of any solid waste, it does not exhibit any of the characteristics of hazardous waste identified in Subpart C of this Part. (However, wastes that exhibit a characteristic at the point of generation may still be subject to the requirements of 35 Ill. Adm. Code 728, even if they no longer exhibit a characteristic at the point of land disposal.) |
2) | In the case of a waste that is a listed waste under Subpart D of this Part, a waste that contains a waste listed under Subpart D of this Part, or a waste that is derived from a waste listed in Subpart D of this Part, it also has been excluded from subsection |
e) | Specific inclusions and exclusions. |
1) | Except as otherwise provided in subsection (e)(2), (g), or (h) of this Section, any solid waste generated from the treatment, storage, or disposal of a hazardous waste, including any sludge, spill residue, ash, emission control dust, or leachate (but not including precipitation run-off), is a hazardous waste. (However, materials that are reclaimed from solid wastes and that are used beneficially are not solid wastes and hence are not hazardous wastes under this provision unless the reclaimed material is burned for energy recovery or used in a manner constituting disposal.) |
2) | The following solid wastes are not hazardous even though they are generated from the treatment, storage, or disposal of a hazardous waste, unless they exhibit one or more of the characteristics of hazardous waste: |
A) | Waste pickle liquor sludge generated by lime stabilization of spent pickle liquor from the iron and steel industry (SIC Codes 331 and 332). |
B) | Wastes from burning any of the materials exempted from regulation by Section 721.106(a)(3)(C) and (a)(3)(D). |
C) | Nonwastewater residues, such as slag, resulting from high temperature metal recovery (HTMR) processing of K061, K062, or F006 waste in the units identified in this subsection (e)(2) that are disposed of in non-hazardous waste units, provided that these residues meet the generic exclusion levels identified in the tables in this subsection (e)(2)(C) for all constituents and the residues exhibit no characteristics of hazardous waste. The types of units identified are rotary kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors, rotary hearth furnace/electric furnace combinations, or the following types of industrial furnaces (as defined in 35 Ill. Adm. Code 720.110): blast furnaces |
i) | Testing requirements must be incorporated in a facility’s waste analysis plan or a generator’s self-implementing waste analysis plan; at a minimum, composite samples of residues must be collected and analyzed quarterly and when the process or operation generating the waste changes. |
ii) | Persons claiming this exclusion in an enforcement action will have the burden of proving by clear and convincing evidence that the material meets all of the exclusion requirements. The generic exclusion levels are the following: |
|
|
Generic exclusion levels for K061 and K062 nonwastewater HTMR residues.:
Constituent |
Maximum for any single composite sample (mg/L) |
Antimony |
0.10 |
Arsenic |
0.50 |
Barium |
7.6 |
Beryllium |
0.010 |
Cadmium |
0.050 |
Chromium (total) |
0.33 |
Lead |
0.15 |
Mercury |
0.009 |
Nickel |
1.0 |
Selenium |
0.16 |
Silver |
0.30 |
Thallium |
0.020 |
Vanadium |
1.26 |
Zinc |
70 |
Generic exclusion levels for F006 nonwastewater HTMR residues:
Constituent |
Maximum for any single composite sample (mg/L) |
Antimony |
0.10 |
Arsenic |
0.50 |
Barium |
7.6 |
Beryllium |
0.010 |
Cadmium |
0.050 |
Chromium (total) |
0.33 |
Cyanide (total) (mg/kg) |
1.8 |
Lead |
0.15 |
Mercury |
0.009 |
Nickel |
1.0 |
Selenium |
0.16 |
Silver |
0.30 |
Thallium |
0.020 |
Zinc |
70 |
iii) | A one-time notification and certification must be placed in the facility’s files and sent to the Agency (or, for out-of-State shipments, to the appropriate Regional Administrator of USEPA or the state agency authorized to implement 40 CFR 268 requirements) for K061, K062, or F006 HTMR residues that meet the generic exclusion levels for all constituents, |
“I certify under penalty of law that the generic exclusion levels for all constituents have been met without impermissible dilution and that no characteristic of hazardous waste is exhibited. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.”
D) | Biological treatment sludge from the treatment of one of the following wastes listed in Section 721.132: organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes (USEPA Hazardous Waste No. K156) and wastewaters from the production of carbamates and carbamoyl oximes (USEPA Hazardous Waste No. K157). |
E) | Catalyst inert support media separated from one of the following wastes listed in Section 721.132: spent hydrotreating catalyst (USEPA hazardous waste number K171) and spent hydrorefining catalyst (USEPA hazardous waste number K172). |
BOARD NOTE: This subsection would normally correspond with 40 CFR 261.3(e), a subsection which that has been deleted and marked “reserved” by USEPA. Rather, this subsection (e) corresponds with 40 CFR 261.3(c)(2), which the Board codified here to comport with codification requirements and to enhance clarity.
f) | Notwithstanding subsections (a) through (e) of this Section and provided the debris, as defined in 35 Ill. Adm. Code 728.102, does not exhibit a characteristic identified at Subpart C of this Part, the following materials are not subject to regulation under 35 Ill. Adm. Code 702, 703, 720, 721 to 726, or 728 |
1) | Hazardous debris as defined in 35 Ill. Adm. Code 728.102 that has been treated using one of the required extraction or destruction technologies specified in Table F to 35 Ill. Adm. Code 728 |
2) | Debris, as defined in 35 Ill. Adm. Code 728.102, that the Agency, considering the extent of contamination, has determined is no longer contaminated with hazardous waste. |
g) | Exclusion of certain wastes listed in Subpart D of this Part solely because they exhibit a characteristic of ignitability, corrosivity, or reactivity. |
1) | A hazardous waste that is listed in Subpart D of this Part solely because it exhibits one or more characteristics of ignitability, as defined under Section 721.121; corrosivity, as defined under Section 721.122; or reactivity, as defined under Section 721.123 is not a hazardous waste if the waste no longer exhibits any characteristic of hazardous waste identified in Subpart C of this Part. |
2) | The exclusion described in subsection (g)(1) of this Section also pertains to the following: |
A) | Any mixture of a solid waste and a hazardous waste listed in Subpart D of this Part solely because it exhibits the characteristics of ignitability, corrosivity, or reactivity, as regulated under subsection (a)(2)(D) of this Section; and |
B) | Any solid waste generated from treating, storing, or disposing of a hazardous waste listed in Subpart D of this Part solely because it exhibits the characteristics of ignitability, corrosivity, or reactivity, as regulated under subsection (e)(1) of this Section. |
3) | Wastes excluded under this subection (g) are subject to 35 Ill. Adm. Code 728 (as applicable), even if they no longer exhibit a characteristic at the point of land disposal. |
h) | Eligible radioactive mixed waste. |
1) | Hazardous waste containing radioactive waste is no longer a hazardous waste when it meets the eligibility criteria and conditions of Subpart N of 35 Ill. Adm. Code 726 |
2) | The exemption described in subsection (h)(1) of this Section also pertains to the following: |
A) | Any mixture of a solid waste and an eligible radioactive mixed waste; and |
B) | Any solid waste generated from treating, storing, or disposing of an eligible radioactive mixed waste. |
3) | Waste exempted under this subsection (h) must meet the eligibility criteria and specified conditions in 35 Ill. Adm. Code 726.325 and 726.330 (for storage and treatment) and in 35 Ill. Adm. Code 726.410 and 726.415 (for transportation and disposal). Waste that fails to satisfy these eligibility criteria and conditions is regulated as hazardous waste. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.104 | Exclusions |
a) | Materials that are not solid wastes. The following materials are not solid wastes for the purpose of this Part: |
1) | Sewage |
A) | Domestic sewage (untreated sanitary wastes that pass through a sewer system); and |
B) | Any mixture of domestic sewage and other waste that passes through a sewer system to publicly-owned treatment works for treatment. |
2) | Industrial wastewater discharges that are point source discharges with National Pollutant Discharge Elimination System (NPDES) permits issued by the Agency pursuant to Section 12(f) of the Environmental Protection Act and 35 Ill. Adm. Code 309. |
BOARD NOTE: This exclusion applies only to the actual point source discharge. It does not exclude industrial wastewaters while they are being collected, stored, or treated before discharge, nor does it exclude sludges that are generated by industrial wastewater treatment.
3) | Irrigation return flows. |
4) | Source, by-product, or special nuclear material, as defined by the Atomic Energy Act of 1954, as amended (42 USC 2011 et seq.). |
5) | Materials subjected to in-situ mining techniques that are not removed from the ground as part of the extraction process. |
6) | Pulping liquors (i.e., black liquors) that are reclaimed in a pulping liquor recovery furnace and then reused in the pulping process, unless it is accumulated speculatively, as defined in Section 721.101(c). |
7) | Spent sulfuric acid used to produce virgin sulfuric acid, unless it is accumulated speculatively, as defined in Section 721.101(c). |
8) | Secondary materials that are reclaimed and returned to the original process or processes in which they were generated, where they are reused in the production process, provided that the following is true: |
A) | Only tank storage is involved, and the entire process through completion of reclamation is closed by being entirely connected with pipes or other comparable enclosed means of conveyance; |
B) | Reclamation does not involve controlled flame combustion (such as occurs in boilers, industrial furnaces, or incinerators); |
C) | The secondary materials are never accumulated in such tanks for over |
D) | The reclaimed material is not used to produce a fuel or used to produce products that are used in a manner constituting disposal. |
9) | Wood preserving wastes. |
A) | Spent wood preserving solutions that have been used and which are reclaimed and reused for their original intended purpose; |
B) | Wastewaters from the wood preserving process that have been reclaimed and which are reused to treat wood; and |
C) | Prior to reuse, the wood preserving wastewaters and spent wood preserving solutions described in subsections (a)(9)(A) and (a)(9)(B) of this Section, so long as they meet all of the following conditions: |
i) | The wood preserving wastewaters and spent wood preserving solutions are reused on-site at |
ii) | Prior to reuse, the wastewaters and spent wood preserving solutions are managed to prevent release to either land or groundwater or both; |
iii) | Any unit used to manage wastewaters or spent wood preserving solutions prior to reuse can be visually or otherwise determined to prevent such releases; |
iv) | Any drip pad used to manage the wastewaters or spent wood preserving solutions prior to reuse complies with the standards in Subpart W of 35 Ill. Adm. Code 725 |
v) | Prior to operating pursuant to this exclusion, the plant owner or operator submits a one-time notification to the Agency stating that the plant intends to claim the exclusion, giving the date on which the plant intends to begin operating under the exclusion, and containing the following language: “I have read the applicable regulation establishing an exclusion for wood preserving wastewaters and spent wood preserving solutions and understand it requires me to comply at all times with the conditions set out in the regulation.” The plant must maintain a copy of that document in its on-site records for a period of no less than three years from the date specified in the notice. The exclusion applies only so long as the plant meets all of the conditions. If the plant goes out of compliance with any condition, it may apply to the Agency for reinstatement. The Agency must reinstate the exclusion in writing if it finds that the plant has returned to compliance with all conditions and that violations are not likely to recur. If the Agency denies an application, it must transmit to the applicant specific, detailed statements in writing as to the reasons it denied the application. The applicant under this subsection (a)(9)(C)(v) may appeal the Agency’s determination to deny the reinstatement, to grant the reinstatement with conditions, or to terminate a reinstatement before the Board pursuant to Section 40 of the Act [415 ILCS 5/40]. |
10) | Hazardous waste numbers K060, K087, K141, K142, K143, K144, K145, K147, and K148, and any wastes from the coke by-products processes that are hazardous only because they exhibit the toxicity characteristic specified in Section 721.124, when subsequent to generation these materials are recycled to coke ovens, to the tar recovery process as a feedstock to produce coal tar, or are mixed with coal tar prior to the tar’s sale or refining. This exclusion is conditioned on there being no land disposal of the waste from the point it is generated to the point it is recycled to coke ovens, to tar recovery, to the tar refining processes, or prior to when it is mixed with coal. |
11) | Nonwastewater splash condenser dross residue from the treatment of hazardous waste number K061 in high temperature metals recovery units, provided it is shipped in drums (if shipped) and not land disposed before recovery. |
12) | Certain oil-bearing hazardous secondary materials and recovered oil, as follows: |
A) | Oil-bearing hazardous secondary materials (i.e., sludges, by-products, or spent materials) that are generated at a petroleum refinery (standard industrial classification (SIC code 2911) and are inserted into the petroleum refining process (SIC code 2911: including, but not limited to, distillation, catalytic cracking, fractionation, or thermal cracking units (i.e., cokers)), unless the material is placed on the land, or speculatively accumulated before being so recycled. Materials inserted into thermal cracking units are excluded under this subsection (a)(12), provided that the coke product also does not exhibit a characteristic of hazardous waste. Oil-bearing hazardous secondary materials may be inserted into the same petroleum refinery where they are generated or sent directly to another petroleum refinery and still be excluded under this provision. Except as provided in subsection (a)(12)(B) of this Section, oil-bearing hazardous secondary materials generated elsewhere in the petroleum industry (i.e., from sources other than petroleum refineries) are not excluded under this |
B) | Recovered oil that is recycled in the same manner and with the same conditions as described in subsection (a)(12)(A) of this Section. Recovered oil is oil that has been reclaimed from secondary materials (including wastewater) generated from normal petroleum industry practices, including refining, exploration and production, bulk storage, and transportation incident thereto (SIC codes 1311, 1321, 1381, 1382, 1389, 2911, 4612, 4613, 4922, 4923, 4789, 5171, and 5172). Recovered oil does not include oil-bearing hazardous wastes listed in Subpart D of this Part; however, oil recovered from such wastes may be considered recovered oil. Recovered oil does not include used oil, as defined in 35 Ill. Adm. Code 739.100. |
13) | Excluded scrap metal (processed scrap metal, unprocessed home scrap metal, and unprocessed prompt scrap metal) being recycled. |
14) | Shredded circuit boards being recycled, provided that they meet the following conditions: |
A) | The circuit boards are stored in containers sufficient to prevent a release to the environment prior to recovery; and |
B) | The circuit boards are free of mercury switches, mercury relays, |
15) | Condensates derived from the overhead gases from kraft mill steam strippers that are used to comply with federal Clean Air Act regulation 40 CFR 63.446(e). The exemption applies only to combustion at the mill generating the condensates. |
16) | Comparable fuels or comparable syngas fuels (i.e., comparable or syngas fuels) that meet the requirements of Section 721.138. |
17) | Spent materials (as defined in Section 721.101) (other than hazardous wastes listed in Subpart D of this Part) generated within the primary mineral processing industry from which minerals, acids, cyanide, water, or other values are recovered by mineral processing or by benefication, provided that the following is true: |
A) | The spent material is legitimately recycled to recover minerals, acids, cyanide, water, or other values; |
B) | The spent material is not accumulated speculatively; |
C) | Except as provided in subsection (a)(17)(D) of this Section, the spent material is stored in tanks, containers, or buildings that meet the following minimum integrity standards: a building must be an engineered structure with a floor, walls, and a roof all of which are made of non-earthen materials providing structural support (except that smelter buildings may have partially earthen floors, provided that the spent material is stored on the non-earthen portion), and have a roof suitable for diverting rainwater away from the foundation; a tank must be free standing, not be a surface impoundment (as defined in 35 Ill. Adm. Code 720.110), and be manufactured of a material suitable for containment of its contents; a container must be free standing and be manufactured of a material suitable for containment of its contents. If a tank or container contains any particulate |
D) | The Agency must allow by permit that solid mineral processing spent materials only may be placed on pads, rather than in tanks, containers, or buildings if the facility owner or operator can demonstrate the following: the solid mineral processing secondary materials do not contain any free liquid; the pads are designed, constructed, and operated to prevent significant releases of the spent material into the environment; and the pads provide the same degree of containment afforded by the non-RCRA tanks, containers, and buildings eligible for exclusion. |
i) | The Agency must also consider whether storage on pads poses the potential for significant releases via groundwater, surface water, and air exposure pathways. Factors to be considered for assessing the groundwater, surface water, and air exposure pathways must include the following: the volume and physical and chemical properties of the spent material, including its potential for migration off the pad; the potential for human or environmental exposure to hazardous constituents migrating from the pad via each exposure pathway; and the possibility and extent of harm to human and environmental receptors via each exposure pathway. |
ii) | Pads must meet the following minimum standards: they must be designed of non-earthen material that is compatible with the chemical nature of the mineral processing spent material; they must be capable of withstanding physical stresses associated with placement and removal; they must have runon and runoff controls; they must be operated in a manner |
iii) | Before making a determination under this subsection (a)(17)(D), the Agency must provide notice and the opportunity for comment to all persons potentially interested in the determination. This can be accomplished by placing notice of this action in major local newspapers, or broadcasting notice over local radio stations. |
BOARD NOTE: See Subpart D of 35 Ill. Adm. Code 703.Subpart D for the RCRA Subtitle C permit public notice requirements.
E) | The owner or operator provides a notice to the Agency, providing the following information: the types of materials to be recycled, the type and location of the storage units and recycling processes, and the annual quantities expected to be placed in non-land-based units. This notification must be updated when there is a change in the type of materials recycled or the location of the recycling process. |
F) | For purposes of subsection (b)(7) of this Section, mineral processing spent materials must be the result of mineral processing and may not include any listed hazardous wastes. Listed hazardous wastes and characteristic hazardous wastes generated by non-mineral processing industries are not eligible for the conditional exclusion from the definition of solid waste. |
18) | Petrochemical recovered oil from an associated organic chemical manufacturing facility, where the oil is to be inserted into the petroleum refining process (SIC code 2911) along with normal petroleum refinery process streams, provided that both of the following conditions are true of the oil: |
A) | The oil is hazardous only because it exhibits the characteristic of ignitability (as defined in Section 721.121) or toxicity for benzene (Section 721.124, USEPA hazardous waste code D018); |
B) | The oil generated by the organic chemical manufacturing facility is not placed on the land, or speculatively accumulated before being recycled into the petroleum refining process. An “associated organic chemical manufacturing facility” is a facility for which all of the following is true: its primary SIC code is 2869, but its operations may also include SIC codes 2821, 2822, and 2865; it is physically co-located with a petroleum refinery; and the petroleum refinery to which the oil being recycled is returned also provides hydrocarbon feedstocks to the organic chemical manufacturing facility. “Petrochemical recovered oil” is oil that has been reclaimed from secondary materials (i.e., sludges, by-products, or spent materials, including wastewater) from normal organic chemical manufacturing operations, as well as oil recovered from organic chemical manufacturing processes. |
19) | Spent caustic solutions from petroleum refining liquid treating processes used as a feedstock to produce cresylic or naphthenic acid, unless the material is placed on the land |
20) | Hazardous secondary materials used to make zinc fertilizers, provided that the following conditions are satisfied: |
A) | Hazardous secondary materials used to make zinc micronutrient fertilizers must not be accumulated speculatively, as defined in Section 721.101(c)(8). |
B) | A generator or intermediate handler of zinc-bearing hazardous secondary materials that are to be incorporated into zinc fertilizers must fulfill the following conditions: |
i) | It must submit a one-time notice to the Agency that contains the name, address, and USEPA identification number of the generator or intermediate handler facility, that provides a brief description of the secondary material that will be subject to the exclusion, and which identifies when the manufacturer intends to begin managing excluded zinc-bearing hazardous secondary materials under the conditions specified in this subsection (a)(20). |
ii) | It must store the excluded secondary material in tanks, containers, or buildings that are constructed and maintained in a way which prevents releases of the secondary materials into the environment. At a minimum, any building used for this purpose must be an engineered structure made of non-earthen materials that provide structural support, and it must have a floor, walls, and a roof that prevent wind dispersal and contact with rainwater. A tank used for this purpose must be structurally sound and, if outdoors, it must have a roof or cover that prevents contact with wind and rain. A container used for this purpose must be kept closed, except when it is necessary to add or remove material, and it must be in sound condition. Containers that are stored outdoors must be managed within storage areas that fulfill the conditions of subsection (a)(20)(F) of this Section: |
iii) | With each off-site shipment of excluded hazardous secondary materials, it must provide written notice to the receiving facility that the material is subject to the conditions of this subsection (a)(20). |
iv) | It must maintain records at the generator’s or intermediate handler’s facility for no less than three years of all shipments of excluded hazardous secondary materials. For each shipment these records must, at a minimum, contain the information specified in subsection (a)(20)(G) of this Section. |
C) | A manufacturer of zinc fertilizers or zinc fertilizer ingredients made from excluded hazardous secondary materials must fulfill the following conditions: |
i) | It must store excluded hazardous secondary materials in accordance with the storage requirements for generators and intermediate handlers, as specified in subsection (a)(20)(B)(ii) of this Section. |
ii) | It must submit a one-time notification to the Agency that, at a minimum, specifies the name, address, and USEPA identification number of the manufacturing facility and which identifies when the manufacturer intends to begin managing excluded zinc-bearing hazardous secondary materials under the conditions specified in this subsection (a)(20). |
iii) | It must maintain for a minimum of three years records of all shipments of excluded hazardous secondary materials received by the manufacturer, which must at a minimum identify for each shipment the name and address of the generating facility, the name of transporter, and the date on which the materials were received, the quantity received, and a brief description of the industrial process that generated the material. |
iv) | It must submit an annual report to the Agency that identifies the total quantities of all excluded hazardous secondary materials that were used to manufacture zinc fertilizers or zinc fertilizer ingredients in the previous year, the name and address of each generating facility, and the industrial processes from which the hazardous secondary materials were generated. |
D) | Nothing in this Section preempts, overrides, or otherwise negates the provision in 35 Ill. Adm. Code 722.111 that requires any person who generates a solid waste to determine if that waste is a hazardous waste. |
E) | Interim status and permitted storage units that have been used to store only zinc-bearing hazardous wastes prior to the submission of the one-time notice described in subsection (a)(20)(B)(i) of this Section, and that afterward will be used only to store hazardous secondary materials excluded under this subsection (a)(20), are not subject to the closure requirements of 35 Ill. Adm. Code 724 and 725. |
F) | A container used to store excluded secondary material must fulfill the following conditions: |
i) | It must have containment structures or systems sufficiently impervious to contain leaks, spills, and accumulated precipitation; |
ii) | It must provide for effective drainage and removal of leaks, spills, and accumulated precipitation; and |
iii) | It must prevent run-on into the containment system. |
BOARD NOTE: Subsections (a)(20)(F)(i) through (a)(20)(F)(iii) are derived from 40 CFR 261.4(a)(20)(ii)(B)(1) through (a)(20)(ii)(B)(3). The Board added the preamble to these federal paragraphs as subsection (a)(20)(F) to comport with Illinois Administrative Code codification requirements.
G) | Required records of shipments of excluded hazardous secondary materials must, at a minimum, contain the following information: |
i) | The name of the transporter and date of the shipment; |
ii) | The name and address of the facility that received the excluded material, along with documentation confirming receipt of the shipment; and |
iii) | The type and quantity of excluded secondary material in each shipment. |
BOARD NOTE: Subsections (a)(20)(G)(i) through (a)(20)(G)(iii) are derived from 40 CFR 261.4(a)(20)(ii)(D)(1) through (a)(20)(ii)(D)(3). The Board added the preamble to these federal paragraphs as subsection (a)(20)(G) to comport with Illinois Administrative Code codification requirements.
21) | Zinc fertilizers made from hazardous wastes or hazardous secondary materials that are excluded under subsection (a)(20) of this Section, provided that the following conditions are fulfilled: |
A) | The fertilizers meet the following contaminant limits: |
i) | For metal contaminants: |
Constituent |
Maximum Allowable Total Concentration in Fertilizer, per Unit (1%) of Zinc (ppm) |
Arsenic |
0.3 |
Cadmium |
1.4 |
Chromium |
0.6 |
Lead |
2.8 |
Mercury |
0.3 |
ii) | For dioxin contaminants, the fertilizer must contain no more than eight parts per trillion of dioxin, measured as toxic equivalent (TEQ). |
B) | The manufacturer performs sampling and analysis of the fertilizer product to determine compliance with the contaminant limits for metals no less frequently than once every six months, and for dioxins no less frequently than once every 12 months. Testing must also be performed whenever changes occur to manufacturing processes or ingredients that could significantly affect the amounts of contaminants in the fertilizer product. The manufacturer may use any reliable analytical method to demonstrate that no constituent of concern is present in the product at concentrations above the applicable limits. It is the responsibility of the manufacturer to ensure that the sampling and analysis are unbiased, precise, and representative of the products introduced into commerce. |
C) | The manufacturer maintains for no less than three years records of all sampling and analyses performed for purposes of determining compliance with the requirements of subsection (a)(21)(B) of this Section. Such records must at a minimum include the following: |
i) | The dates and times product samples were taken, and the dates the samples were analyzed; |
ii) | The names and qualifications of the persons taking the samples; |
iii) | A description of the methods and equipment used to take the samples; |
iv) | The name and address of the laboratory facility at which analyses of the samples were performed; |
v) | A description of the analytical methods used, including any cleanup and sample preparation methods; and |
vi) | All laboratory analytical results used to determine compliance with the contaminant limits specified in this subsection (a)(21). |
b) | Solid wastes that are not hazardous wastes. The following solid wastes are not hazardous wastes: |
1) | Household waste, including household waste that has been collected, transported, stored, treated, disposed, recovered (e.g., refuse-derived fuel), or reused. “Household waste” means any waste material (including garbage, trash, and sanitary wastes in septic tanks) derived from households (including single and multiple residences, hotels, and motels, bunkhouses, ranger stations, crew quarters, campgrounds, picnic grounds, and day-use recreation areas). A resource recovery facility managing municipal solid waste must not be deemed to be treating, storing, disposing of, or otherwise managing hazardous wastes for the purposes of regulation under this Part, if the following describe the |
A) | |
i) | Household waste (from single and multiple dwellings, hotels, motels, and other residential sources); |
ii) | Solid waste from commercial or industrial sources that does not contain hazardous waste; and |
B) | |
BOARD NOTE: The U.S. Supreme Court determined, in City of Chicago v. Environmental Defense Fund, Inc., 511 U.S. 328, 114 S. Ct. 1588, 128 L. Ed. 2d 302 (1994), that this exclusion and RCRA section 3001(i) (42 USC 6921(i)) do not exclude the ash from facilities covered by this subsection (b)(1) from regulation as a hazardous waste. At 59 Fed. Reg. 29372 (June 7, 1994), USEPA granted facilities managing ash from such facilities that is determined a hazardous waste under Subpart C of this Part until December 7, 1994 to file a Part A permit application pursuant to 35 Ill. Adm. Code 703.181. At 60 Fed. Reg. 6666 (Feb. 3, 1995), USEPA stated that it interpreted that the point at which ash becomes subject to RCRA Subtitle C regulation is when that material leaves the combustion building (including connected air pollution control equipment).
2) | Solid wastes generated by any of the following that are returned to the soil as fertilizers: |
A) | The growing and harvesting of agricultural crops, or |
B) | The raising of animals, including animal manures. |
3) | Mining overburden returned to the mine site. |
4) | Fly ash waste, bottom ash waste, slag waste, and flue gas emission control waste generated primarily from the combustion of coal or other fossil fuels, except as provided in 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste. |
5) | Drilling fluids, produced waters, and other wastes associated with the exploration, development, or production of crude oil, natural gas, or geothermal energy. |
6) | Chromium wastes |
A) | Wastes that fail the test for the toxicity characteristic ( |
i) | The chromium in the waste is exclusively (or nearly exclusively) trivalent chromium; |
ii) | The waste is generated from an industrial process that uses trivalent chromium exclusively (or nearly exclusively) and the process does not generate hexavalent chromium; and |
iii) | The waste is typically and frequently managed in non-oxidizing environments. |
B) | |
i) | Chrome (blue) trimmings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling; |
ii) | Chrome (blue) shavings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling; |
iii) | Buffing dust generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue; |
iv) | Sewer screenings generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling; |
v) | Wastewater treatment sludges generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no beamhouse, through-the-blue, and shearling; |
vi) | Wastewater treatment sludges generated by the following subcategories of the leather tanning and finishing industry: hair pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet finish, and through-the-blue; |
vii) | Waste scrap leather from the leather tanning industry, the shoe manufacturing industry, and other leather product manufacturing industries; and |
viii) | Wastewater treatment sludges from the production of titanium dioxide pigment using chromium-bearing ores by the chloride process. |
7) | Solid waste from the extraction, beneficiation, and processing of ores and minerals (including coal, phosphate rock, and overburden from the mining of uranium ore), except as provided by 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste. |
A) | For purposes of this subsection (b)(7), beneficiation of ores and minerals is restricted to the following activities: crushing; grinding; washing; dissolution; crystallization; filtration; sorting; sizing; drying; sintering; pelletizing; briquetting; calcining to remove water or carbon dioxide; roasting; autoclaving or chlorination in preparation for leaching (except where the roasting (or autoclaving or chlorination) and leaching sequence produces a final or intermediate product that does not undergo further beneficiation or processing); gravity concentration; magnetic separation; electrostatic separation; floatation; ion exchange; solvent extraction; electrowinning; precipitation; amalgamation; and heap, dump, vat tank, and in situ leaching. |
B) | For the purposes of this subsection (b)(7), solid waste from the processing of ores and minerals includes only the following wastes as generated: |
i) | Slag from primary copper processing; |
ii) | Slag from primary lead processing; |
iii) | Red and brown muds from bauxite refining; |
iv) | Phosphogypsum from phosphoric acid production; |
v) | Slag from elemental phosphorus production; |
vi) | Gasifier ash from coal gasification; |
vii) | Process wastewater from coal gasification; |
viii) | Calcium sulfate wastewater treatment plant sludge from primary copper processing; |
ix) | Slag tailings from primary copper processing; |
x) | Fluorogypsum from hydrofluoric acid production; |
xi) | Process wastewater from hydrofluoric acid production; |
xii) | Air pollution control dust or sludge from iron blast furnaces; |
xiii) | Iron blast furnace slag; |
xiv) | Treated residue from roasting and leaching of chrome ore; |
xv) | Process wastewater from primary magnesium processing by the anhydrous process; |
xvi) | Process wastewater from phosphoric acid production; |
xvii) | Basic oxygen furnace and open hearth furnace air pollution control dust or sludge from carbon steel production; |
xviii) | Basic oxygen furnace and open hearth furnace slag from carbon steel production; |
xix) | Chloride processing waste solids from titanium tetrachloride production; and |
xx) | Slag from primary zinc production. |
C) | A residue derived from co-processing mineral processing secondary materials with normal beneficiation raw materials or with normal mineral processing raw materials remains excluded under this subsection (b) if the following conditions are fulfilled: |
i) | The owner or operator processes at least 50 percent by weight normal beneficiation raw materials or normal mineral processing raw materials; and |
ii) | The owner or operator legitimately reclaims the secondary mineral processing materials. |
8) | Cement kiln dust waste, except as provided by 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous waste. |
9) | Solid waste that consists of discarded arsenical-treated wood or wood products that fails the test for the toxicity characteristic for hazardous waste codes D004 through D017 and which is not a hazardous waste for any other reason if the waste is generated by persons that utilize the arsenical-treated wood and wood products for these materials’ intended end use. |
10) | Petroleum-contaminated media and debris that fail the test for the toxicity characteristic of Section 721.124 (hazardous waste codes D018 through D043 only) and which are subject to corrective action regulations under 35 Ill. Adm. Code 731. |
11) | This subsection (b)(11) corresponds with 40 CFR 261.4(b)(11), which expired by its own terms on January 25, 1993. This statement maintains structural parity with USEPA regulations. |
12) | Used chlorofluorocarbon refrigerants from totally enclosed heat transfer equipment, including mobile air conditioning systems, mobile refrigeration, and commercial and industrial air conditioning and refrigeration systems, that use chlorofluorocarbons as the heat transfer fluid in a refrigeration cycle, provided the refrigerant is reclaimed for further use. |
13) | Non-terne plated used oil filters that are not mixed with wastes listed in Subpart D of this Part, if these oil filters have been gravity hot-drained using one of the following methods: |
A) | Puncturing the filter anti-drain back valve or the filter dome end and hot-draining; |
B) | Hot-draining and crushing; |
C) | Dismantling and hot-draining; or |
D) | Any other equivalent hot-draining method that will remove used oil. |
14) | Used oil re-refining distillation bottoms that are used as feedstock to manufacture asphalt products. |
15) | Leachate or gas condensate collected from landfills where certain solid wastes have been disposed of, under |
A) | The following conditions must be fulfilled: |
i) | The solid wastes disposed of would meet one or more of the listing descriptions for the following USEPA hazardous waste numbers that |
USEPA Hazardous Waste Numbers
|
Listing Effective Date |
K169, K170, K171, and K172
|
February 8, 1999 |
K174 and K175
|
May 7, 2001 |
K176, K177, and K178 |
May 20, 2002 |
ii) | The solid wastes described in subsection (b)(15)(A)(i) of this Section were disposed of prior to the effective date of the listing (as set forth in that subsection); |
iii) | The leachate or gas condensate does not exhibit any characteristic of hazardous waste nor is derived from any other listed hazardous waste; and |
iv) | Discharge of the leachate or gas condensate, including leachate or gas condensate transferred from the landfill to a POTW by truck, rail, or dedicated pipe, is subject to regulation under section 307(b) or 402 of the federal Clean Water Act. |
c) | Hazardous wastes that are exempted from certain regulations. A hazardous waste that is generated in a product or raw material storage tank, a product or raw material transport vehicle or vessel, a product or raw material pipeline, or in a manufacturing process unit, or an associated non-waste-treatment manufacturing unit, is not subject to regulation under 35 Ill. Adm. Code 702, 703, |
d) | Samples. |
1) | Except as provided in subsection (d)(2) of this Section, a sample of solid waste or a sample of water, soil, or air that is collected for the sole purpose of testing to determine its characteristics or composition is not subject to any requirements of this Part or 35 Ill. Adm. Code 702, 703, |
A) | The sample is being transported to a laboratory for the purpose of testing; |
B) | The sample is being transported back to the sample collector after testing; |
C) | The sample is being stored by the sample collector before transport to a laboratory for testing; |
D) | The sample is being stored in a laboratory before testing; |
E) | The sample is being stored in a laboratory for testing but before it is returned to the sample collector; or |
F) | The sample is being stored temporarily in the laboratory after testing for a specific purpose (for example, until conclusion of a court case or enforcement action where further testing of the sample may be necessary). |
2) | In order to qualify for the exemption in subsection (d)(1)(A) or (d)(1)(B) of this Section, a sample collector shipping samples to a laboratory and a laboratory returning samples to a sample collector must do the following: |
A) | Comply with U.S. Department of Transportation (USDOT), U.S. Postal Service (USPS), or any other applicable shipping requirements; or |
B) | Comply with the following requirements if the sample collector determines that USDOT, USPS, or other shipping requirements do not apply to the shipment of the sample: |
i) | Assure that the following information accompanies the sample: The sample collector’s name, mailing address, and telephone number; the laboratory’s name, mailing address, and telephone number; the quantity of the sample; the date of the shipment; and a description of the sample |
ii) | Package the sample so that it does not leak, spill, or vaporize from its packaging. |
3) | This exemption does not apply if the laboratory determines that the waste is hazardous but the laboratory is no longer meeting any of the conditions stated in subsection (d)(1) of this Section. |
e) | Treatability study samples. |
1) | Except as is provided in subsection (e)(2) of this Section, a person that generates or collects samples for the purpose of conducting treatability studies, as defined in 35 Ill. Adm. Code 720.110, are not subject to any requirement of 35 Ill. Adm. Code 721 through 723 or to the notification requirements of section 3010 of the Resource Conservation and Recovery Act. Nor are such samples included in the quantity determinations of Section 721.105 and 35 Ill. Adm. Code 722.134(d) when: |
A) | The sample is being collected and prepared for transportation by the generator or sample collector; |
B) | The sample is being accumulated or stored by the generator or sample collector prior to transportation to a laboratory or testing facility; or |
C) | The sample is being transported to the laboratory or testing facility for the purpose of conducting a treatability study. |
2) | The exemption in subsection (e)(1) of this Section is applicable to samples of hazardous waste being collected and shipped for the purpose of conducting treatability studies provided that the following conditions are fulfilled: |
A) | The generator or sample collector uses (in “treatability studies”) no more than 10,000 kg of media contaminated with non-acute hazardous waste, 1000 kg of non-acute hazardous waste other than contaminated media, 1 kg of acute hazardous waste, or 2500 kg of media contaminated with acute hazardous waste for each process being evaluated for each generated waste stream; |
B) | The mass of each shipment does not exceed 10,000 kg; the 10,000 kg quantity may be all media contaminated with non-acute hazardous waste, or may include 2500 kg of media contaminated with acute hazardous waste, 1000 kg of hazardous waste, and 1 kg of acute hazardous waste; |
C) | The sample must be packaged so that it does not leak, spill, or vaporize from its packaging during shipment and the requirements of subsections (e)(2)(C)(i) or (e)(2)(C)(ii) of this Section are met. |
i) | The transportation of each sample shipment complies with U.S. Department of Transportation (USDOT), U.S. Postal Service (USPS), or any other applicable shipping requirements; or |
ii) | If the USDOT, USPS, or other shipping requirements do not apply to the shipment of the sample, the following information must accompany the sample: The name, mailing address, and telephone number of the originator of the sample; the name, address, and telephone number of the facility that will perform the treatability study; the quantity of the sample; the date of the shipment; and, a description of the sample, including its USEPA hazardous waste number; |
D) | The sample is shipped to a laboratory or testing facility that is exempt under subsection (f) of this Section, or has an appropriate RCRA permit or interim status; |
E) | The generator or sample collector maintains the following records for a period ending three years after completion of the treatability study: |
i) | Copies of the shipping documents; |
ii) | A copy of the contract with the facility conducting the treatability study; and |
iii) | Documentation showing the following: The amount of waste shipped under this exemption; the name, address, and USEPA identification number of the laboratory or testing facility that received the waste; the date the shipment was made; and whether or not unused samples and residues were returned to the generator; and |
F) | The generator reports the information required in subsection (e)(2)(E)(iii) of this Section in its report under 35 Ill. Adm. Code 722.141. |
3) | The Agency may grant requests on a case-by-case basis for up to an additional two years for treatability studies involving bioremediation. The Agency may grant requests, on a case-by-case basis, for quantity limits in excess of those specified in subsections (e)(2)(A), (e)(2)(B), and (f)(4) of this Section, for up to an additional 5000 kg of media contaminated with non-acute hazardous waste, 500 kg of non-acute hazardous waste, 2500 kg of media contaminated with acute hazardous waste, and 1 kg of acute hazardous waste under the circumstances set forth in either subsection (e)(3)(A) or (e)(3)(B) of this Section, subject to the limitations of subsection (e)(3)(C) of this Section: |
A) | In response to requests for authorization to ship, store, and conduct further treatability studies on additional quantities in advance of commencing treatability studies. Factors to be considered in reviewing such requests include the nature of the technology, the type of process (e.g., batch versus continuous), the size of the unit undergoing testing (particularly in relation to scale-up considerations), the time or quantity of material required to reach steady-state operating conditions, or test design considerations, such as mass balance calculations. |
B) | In response to requests for authorization to ship, store, and conduct treatability studies on additional quantities after initiation or completion of initial treatability studies when the following occurs: There has been an equipment or mechanical failure during the conduct of the treatability study, there is need to verify the results of a previously-conducted treatability study, there is a need to study and analyze alternative techniques within a previously-evaluated treatment process, or there is a need to do further evaluation of an ongoing treatability study to determine final specifications for treatment. |
C) | The additional quantities allowed and timeframes allowed in subsections (e)(3)(A) and (e)(3)(B) of this Section are subject to all the provisions in subsections (e)(1) and (e)(2)(B) through (e)(2)(F) of this Section. The generator or sample collector must apply to the Agency and provide in writing the following information: |
i) | The reason why the generator or sample collector requires additional time or quantity of sample for the treatability study evaluation and the additional time or quantity needed; |
ii) | Documentation accounting for all samples of hazardous waste from the waste stream that have been sent for or undergone treatability studies, including the date each previous sample from the waste stream was shipped, the quantity of each previous shipment, the laboratory or testing facility to which it was shipped, what treatability study processes were conducted on each sample shipped, and the available results of each treatability study; |
iii) | A description of the technical modifications or change in specifications that will be evaluated and the expected results; |
iv) | If such further study is being required due to equipment or mechanical failure, the applicant must include information regarding the reason for the failure or breakdown and also include what procedures or equipment improvements have been made to protect against further breakdowns; and |
v) | Such other information as the Agency determines is necessary. |
4) | Final Agency determinations pursuant to this subsection (e) may be appealed to the Board. |
f) | Samples undergoing treatability studies at laboratories or testing facilities. Samples undergoing treatability studies and the laboratory or testing facility conducting such treatability studies (to the extent such facilities are not otherwise subject to RCRA requirements) are not subject to any requirement of this Part, or of 35 Ill. Adm. Code 702, 703, |
1) | No less than 45 days before conducting treatability studies, the facility notifies the Agency in writing that it intends to conduct treatability studies under this subsection (f). |
2) | The laboratory or testing facility conducting the treatability study has a USEPA identification number. |
3) | No more than a total of 10,000 kg of “as received” media contaminated with non-acute hazardous waste, 2500 kg of media contaminated with acute hazardous waste, or 250 kg of other “as received” hazardous waste is subject to initiation of treatment in all treatability studies in any single day. “As received” waste refers to the waste as received in the shipment from the generator or sample collector. |
4) | The quantity of “as received” hazardous waste stored at the facility for the purpose of evaluation in treatability studies does not exceed 10,000 kg, the total of which can include 10,000 kg of media contaminated with non-acute hazardous waste, 2500 kg of media contaminated with acute hazardous waste, 1000 kg of non-acute hazardous wastes other than contaminated media, and 1 kg of acute hazardous waste. This quantity limitation does not include treatment materials (including non-hazardous solid waste) added to “as received” hazardous waste. |
5) | No more than 90 days have elapsed since the treatability study for the sample was completed, or no more than one year (two years for treatability studies involving bioremediation) has elapsed since the generator or sample collector shipped the sample to the laboratory or testing facility, whichever date first occurs. Up to 500 kg of treated material from a particular waste stream from treatability studies may be archived for future evaluation up to five years from the date of initial receipt. Quantities of materials archived are counted against the total storage limit for the facility. |
6) | The treatability study does not involve the placement of hazardous waste on the land or open burning of hazardous waste. |
7) | The facility maintains records for three years following completion of each study that show compliance with the treatment rate limits and the storage time and quantity limits. The following specific information must be included for each treatability study conducted: |
A) | The name, address, and USEPA identification number of the generator or sample collector of each waste sample; |
B) | The date the shipment was received; |
C) | The quantity of waste accepted; |
D) | The quantity of “as received” waste in storage each day; |
E) | The date the treatment study was initiated and the amount of “as received” waste introduced to treatment each day; |
F) | The date the treatability study was concluded; |
G) | The date any unused sample or residues generated from the treatability study were returned to the generator or sample collector or, if sent to a designated facility, the name of the facility and the USEPA identification number. |
8) | The facility keeps, on-site, a copy of the treatability study contract and all shipping papers associated with the transport of treatability study samples to and from the facility for a period ending three years from the completion date of each treatability study. |
9) | The facility prepares and submits a report to the Agency by March 15 of each year that estimates the number of studies and the amount of waste expected to be used in treatability studies during the current year, and includes the following information for the previous calendar year: |
A) | The name, address, and USEPA identification number of the facility conducting the treatability studies; |
B) | The types (by process) of treatability studies conducted; |
C) | The names and addresses of persons for whom studies have been conducted (including their USEPA identification numbers); |
D) | The total quantity of waste in storage each day; |
E) | The quantity and types of waste subjected to treatability studies; |
F) | When each treatability study was conducted; and |
G) | The final disposition of residues and unused sample from each treatability study. |
10) | The facility determines whether any unused sample or residues generated by the treatability study are hazardous waste under Section 721.103 and, if so, are subject to 35 Ill. Adm. Code 702, 703, and 721 through 728, unless the residues and unused samples are returned to the sample originator under the exemption of subsection (e) of this Section. |
11) | The facility notifies the Agency by letter when the facility is no longer planning to conduct any treatability studies at the site. |
g) | Dredged material that is not a hazardous waste. Dredged material that is subject to the requirements of a permit that has been issued under section 404 of the Federal Water Pollution Control Act (33 USC 1344) is not a hazardous waste. For the purposes of this subsection (g), the following definitions apply: |
“Dredged material” has the same meaning as in 40 CFR 232.2, incorporated by reference in 35 Ill. Adm. Code 720.111.
“Permit” means any of the following:
A permit issued by the U.S. Army Corps of Engineers (Army Corps) under section 404 of the Federal Water Pollution Control Act (33 USC 1344);
A permit issued by the Army Corps under section 103 of the Marine Protection, Research, and Sanctuaries Act of 1972 (33 USC 1413); or
In the case of Army Corps civil works projects, the administrative equivalent of the permits referred to in the preceding two paragraphs of this definition, as provided for in Army Corps regulations (for example, see 33 CFR 336.1, 336.2, and 337.6).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.105 | Special Requirements for Hazardous Waste Generated by Small Quantity Generators |
a) | A generator is a conditionally exempt small quantity generator in a calendar month if it generates no more than 100 kilograms of hazardous waste in that month. |
b) | Except for those wastes identified in subsections (e), (f), (g), and (j) of this Section, a conditionally exempt small quantity generator’s hazardous wastes are not subject to regulation under 35 Ill. Adm. Code 702, 703, |
c) | When making the quantity determinations of this Part and 35 Ill. Adm. Code 722, the generator must include all hazardous waste that it generates, except the following hazardous waste: |
1) | Hazardous waste that is exempt from regulation under Section 721.104(c) through (f), 721.106(a)(3), 721.107(a)(1), or 721.108; |
2) | Hazardous waste that is managed immediately upon generation only in on-site elementary neutralization units, wastewater treatment units, or totally enclosed treatment facilities, as defined in 35 Ill. Adm. Code 720.110; |
3) | Hazardous waste that is recycled, without prior storage or accumulation, only in an on-site process subject to regulation under Section 721.106(c)(2); |
4) | Hazardous waste that is used oil managed under the requirements of Section 721.106(a)(4) and 35 Ill. Adm. Code 739; |
5) | Hazardous waste that is spent lead-acid batteries managed under the requirements of Subpart G of 35 Ill. Adm. Code 726 |
6) | Hazardous waste that is universal waste managed under Section 721.109 and 35 Ill. Adm. Code 733. |
d) | In determining the quantity of hazardous waste it generates, a generator need not include the following: |
1) | Hazardous waste when it is removed from on-site storage; |
2) | Hazardous waste produced by on-site treatment (including reclamation) of its hazardous waste so long as the hazardous waste that is treated was counted once; |
3) | Spent materials that are generated, reclaimed, and subsequently reused on-site, so long as such spent materials have been counted once. |
e) | If a generator generates acute hazardous waste in a calendar month in quantities greater than set forth below, all quantities of that acute hazardous waste are subject to full regulation under 35 Ill. Adm. Code 702, 703, |
1) | A total of one kilogram of one or more of the acute hazardous wastes listed in Section 721.131, 721.132, or 721.133(e); or |
2) | A total of 100 kilograms of any residue or contaminated soil, waste, or other debris resulting from the clean-up of a spill, into or on any land or water, of any one or more of the acute hazardous wastes listed in Section 721.131, 721.132, or 721.133(e). |
BOARD NOTE: “Full regulation” means those regulations applicable to generators of greater than 1000 kg of non-acute hazardous waste in a calendar month.
f) | In order for acute hazardous wastes generated by a generator of acute hazardous wastes in quantities equal to or less than those set forth in subsection (e)(1) or (e)(2) of this Section to be excluded from full regulation under this Section, the generator must comply with the following requirements: |
1) | 35 Ill. Adm. Code 722.111. |
2) | The generator may accumulate acute hazardous waste on-site. If the generator accumulates at any time acute hazardous wastes in quantities greater than set forth in subsection (e)(1) or (e)(2) of this Section, all of those accumulated wastes are subject to regulation under 35 Ill. Adm. Code 702, 703, |
3) | A conditionally exempt small quantity generator may either treat or dispose of its acute hazardous waste in an on-site facility or ensure delivery to an off-site treatment, storage, or disposal facility, any of which, if located in the United States, meets any of the following conditions: |
A) | The facility is permitted under 35 Ill. Adm. Code 702 and 703; |
B) | The facility has interim status under 35 Ill. Adm. Code 702, 703, and 725; |
C) | The facility is authorized to manage hazardous waste by a state with a hazardous waste management program approved by USEPA pursuant to 40 CFR 271; |
D) | The facility is permitted, licensed, or registered by a state to manage municipal solid waste and, if managed in a municipal solid waste landfill facility, the landfill is subject to 35 Ill. Adm. Code 810 through 814 or 40 CFR 258; |
E) | The facility is permitted, licensed, or registered by a state to manage non-municipal non-hazardous waste and, if managed in a non-municipal non-hazardous waste disposal unit, the unit is subject to the requirements of 40 CFR 257.5 through 257.30; |
BOARD NOTE: The Illinois non-hazardous waste landfill regulations, 35 Ill. Adm. Code 810 through 814, do not allow the disposal of hazardous waste in a landfill regulated under those rules. The Board intends that subsections (f)(3)(D) and (f)(3)(E) of this Section impose a federal requirement on the hazardous waste generator. The Board specifically does not intend that these subsections authorize any disposal of conditionally-exempt small quantity generator waste in a landfill not specifically permitted to accept the particular hazardous waste.
F) | The facility is one that fulfills one of the following conditions: |
i) | |
ii) | |
G) | For universal waste managed under 35 Ill. Adm. Code 733 or 40 CFR 273, the facility is a universal waste handler or destination facility subject to the requirements of 35 Ill. Adm. Code 733 or 40 CFR 273. |
g) | In order for hazardous waste generated by a conditionally exempt small quantity generator in quantities of less than 100 kilograms of hazardous waste during a calendar month to be excluded from full regulation under this Section, the generator must comply with the following requirements: |
1) | 35 Ill. Adm. Code 722.111; |
2) | The conditionally exempt small quantity generator may accumulate hazardous waste on-site. If it accumulates at any time more than a total of 1000 kilograms of the generator’s hazardous waste, all of those accumulated wastes are subject to regulation under the special provisions of 35 Ill. Adm. Code 722 applicable to generators of between 100 kg and 1000 kg of hazardous waste in a calendar month, as well as the requirements of 35 Ill. Adm. Code 702, 703, |
3) | A conditionally exempt small quantity generator may either treat or dispose of its hazardous waste in an on-site facility or ensure delivery to an off-site treatment, storage, or disposal facility, any of which, if located in the United States, meets any of the following conditions: |
A) | The facility is permitted under 35 Ill. Adm. Code 702 and 703; |
B) | The facility has interim status under 35 Ill. Adm. Code 702, 703, and 725; |
C) | The facility is authorized to manage hazardous waste by a state with a hazardous waste management program approved by USEPA under 40 CFR 271 |
D) | The facility is permitted, licensed, or registered by a state to manage municipal solid waste and, if managed in a municipal solid waste landfill facility, the landfill is subject to 35 Ill. Adm. Code 810 through 814 or 40 CFR 258; |
E) | The facility is permitted, licensed, or registered by a state to manage non-municipal non-hazardous waste and, if managed in a non-municipal non-hazardous waste disposal unit, the unit is subject to the requirements of 40 CFR 257.5 through 257.30; |
BOARD NOTE: The Illinois non-hazardous waste landfill regulations, 35 Ill. Adm. Code 810 through 814, do not allow the disposal of hazardous waste in a landfill regulated under those rules. The Board intends that subsections (g)(3)(D) and (g)(3)(E) of this Section impose a federal requirement on the hazardous waste generator. The Board specifically does not intend that these subsections authorize any disposal of conditionally-exempt small quantity generator waste in a landfill not specifically permitted to accept the particular hazardous waste.
F) | The facility is one that fulfills the following conditions: |
i) | |
ii) | |
G) | For universal waste managed under 35 Ill. Adm. Code 733 or 40 CFR 273, the facility is a universal waste handler or destination facility subject to the requirements of 35 Ill. Adm. Code 733 or 40 CFR 273. |
h) | Hazardous waste subject to the reduced requirements of this Section may be mixed with non-hazardous waste and remain subject to these reduced requirements even though the resultant mixture exceeds the quantity limitations identified in this Section, unless the mixture meets any of the characteristics of hazardous wastes identified in Subpart C of this Part. |
i) | If a small quantity generator mixes a solid waste with a hazardous waste that exceeds a quantity exclusion level of this Section, the mixture is subject to full regulation. |
j) | If a conditionally exempt small quantity generator’s hazardous wastes are mixed with used oil, the mixture is subject to 35 Ill. Adm. Code 739 if it is destined to be burned for energy recovery. Any material produced from such a mixture by processing, blending, or other treatment is also so regulated if it is destined to be burned for energy recovery. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.106 | Requirements for Recyclable Materials |
a) | Recyclable materials: |
1) | Hazardous wastes that are recycled are subject to the requirements for generators, transporters, and storage facilities of subsections (b) and (c) of this Section, except for the materials listed in subsections (a)(2) and (a)(3) of this Section. Hazardous wastes that are recycled will be known as “recyclable materials.” |
2) | The following recyclable materials are not subject to the requirements of this Section but are regulated under Subparts C through H of 35 Ill. Adm. Code 726 |
A) | Recyclable materials used in a manner constituting disposal (Subpart C of 35 Ill. Adm. Code 726 |
B) | Hazardous wastes burned for energy recovery in boilers and industrial furnaces that are not regulated under Subpart O of 35 Ill. Adm. Code 724 |
C) | Recyclable materials from which precious metals are reclaimed (Subpart F of 35 Ill. Adm. Code 726 |
D) | Spent lead-acid batteries that are being reclaimed (Subpart G of 35 Ill. Adm. Code 726 |
3) | The following recyclable materials are not subject to regulation under 35 Ill. Adm. Code 722 through 726, 728, or 702 |
A) | Industrial ethyl alcohol that is reclaimed except that, unless provided otherwise in an international agreement as specified in 35 Ill. Adm. Code 722.158, the following requirements continue to apply: |
i) | A person initiating a shipment for reclamation in a foreign country and any intermediary arranging for the shipment |
ii) | Transporters transporting a shipment for export |
B) | Scrap metal that is not excluded under Section 721.104(a)(13); |
C) | Fuels produced from the refining of oil-bearing hazardous wastes along with normal process streams at a petroleum refining facility if such wastes result from normal petroleum refining, production, and transportation practices (this exemption does not apply to fuels produced from oil recovered from oil-bearing hazardous waste where such recovered oil is already excluded under Section 721.104(a)(12)); |
D) | Petroleum refining wastes. |
i) | Hazardous waste fuel produced from oil-bearing hazardous wastes from petroleum refining, production, or transportation practices or produced from oil reclaimed from such hazardous wastes, where such hazardous wastes are reintroduced into a process that does not use distillation or does not produce products from crude oil, so long as the resulting fuel meets the used oil specification under 35 Ill. Adm. Code 739.111 and so long as no other hazardous wastes are used to produce the hazardous waste fuel; |
ii) | Hazardous waste fuel produced from oil-bearing hazardous waste from petroleum refining production, and transportation practices, where such hazardous wastes are reintroduced into a refining process after a point at which contaminants are removed, so long as the fuel meets the used oil fuel specification under 35 Ill. Adm. Code 739.111; and |
iii) | Oil reclaimed from oil-bearing hazardous wastes from petroleum refining, production, and transportation practices, which reclaimed oil is burned as a fuel without reintroduction to a refining process, so long as the reclaimed oil meets the used oil fuel specification under 35 Ill. Adm. Code 739.111. |
4) | Used oil that is recycled and is also a hazardous waste solely because it exhibits a hazardous characteristic is not subject to the requirements of 35 Ill. Adm. Code 720 through 728, but it is regulated under 35 Ill. Adm. Code 739. Used oil that is recycled includes any used oil that is reused for any purpose following its original use (including the purpose for which the oil was originally used). Such term includes, but is not limited to, oil that is re-refined, reclaimed, burned for energy recovery, or reprocessed. |
5) | Hazardous waste that is exported to or imported from designated member countries of the Organization for Economic Cooperation and Development (OECD), as defined in Section 722.158(a)(1), for the purpose of recovery is subject to the requirements of Subpart H of 35 Ill. Adm. Code 722 |
b) | Generators and transporters of recyclable materials are subject to the applicable requirements of 35 Ill. Adm. Code 722 and 723 and the notification requirements under section 3010 of the Resource Conservation and Recovery Act, except as provided in subsection (a) of this Section. |
c) | Storage and recycling |
1) | Owners or operators of facilities that store recyclable materials before they are recycled are regulated under all applicable provisions of Subparts A through L, AA, BB, and CC of 35 Ill. Adm. Code 702, 703, and 705; 724 |
2) | Owners or operators of facilities that recycle recyclable materials without storing them before they are recycled are subject to the following requirements, except as provided in subsection (a) of this Section, the following requirements continue to apply: |
A) | Notification requirements under section 3010 of the Resource Conservation and Recovery Act, |
B) | 35 Ill. Adm. Code 725.171 and 725.172 (dealing with the use of the manifest and manifest discrepancies), and |
C) | |
d) | Owners or operators of facilities required to have a RCRA permit pursuant to 35 Ill. Adm. Code 703 with hazardous waste management units that recycle hazardous wastes are subject to Subparts AA and BB of 35 Ill. Adm. Code 724 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.107 | Residues of Hazardous Waste in Empty Containers |
a) | Applicability of rules |
1) | Any hazardous waste remaining in either an empty container or an inner liner removed from an empty container, as defined in subsection (b), is not subject to regulation under 35 Ill. Adm. Code 702, 703, |
2) | Any hazardous waste in either a container that is not empty or an inner liner that is removed from a container that is not empty, as defined in subsection (b), is subject to regulations under 35 Ill. Adm. Code 702, 703, |
b) | Definition of “empty |
1) | A container or an |
A) | All wastes have been removed that can be removed using the practices commonly employed to remove materials from that type of container, e.g., pouring, pumping, and aspirating, and |
B) | No more than 2.5 centimeters (one inch) of residue remain on the bottom of the container or inner liner, or |
C) | Weight limits |
i) | No more than |
ii) | No more than 0.3 percent by weight of the total capacity of the container remains in the container or inner liner if the container is greater than 110 gallons in size. |
2) | A container that has held a hazardous waste that is a compressed gas is empty when the pressure in the container approaches ambient atmospheric pressure. |
3) | A container or an inner liner removed from a container that has held an acute hazardous waste listed in Sections 721.131, 721.132, or 721.133(e) is empty if any of the following occurs: |
A) | The container or inner liner has been triple rinsed using a solvent capable of removing the commercial chemical product or manufacturing chemical intermediate; |
B) | The container or inner liner has been cleaned by another method that has been shown in the scientific literature, or by tests conducted by the generator, to achieve equivalent removal; or |
C) | In the case of a container, the inner liner that prevented contact of the commercial chemical product or manufacturing chemical intermediate with the container has been removed. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.108 | PCB Wastes Regulated under TSCA |
Polychlorinatedbiphenyl-(PCB-)containing dielectric fluid and electric equipment containing such fluid, which that are authorized for use and regulated under 40 CFR 761, incorporated by reference in 35 Ill. Adm. Code 720.111, and which are hazardous only because they fail the test for toxicity characteristic (hazardous waste codes D018 through D043 only), are exempt from regulation under 35 Ill. Adm. Code 702, 703, 705, 721 through 725, and 728, and from the notification requirements of Section 3010 of the Resource Conservation and Recovery Act.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.109 | Requirements for Universal Waste |
The wastes listed in this Section are exempt from regulation under 35 Ill. Adm. Code 702 through 705, 703, 722 through 726, and 728, except as specified in 35 Ill. Adm. Code 733, and are therefore not fully regulated as hazardous waste. The following wastes listed in this Section are subject to regulation under 35 Ill. Adm. Code 733:
a) | Batteries, as described in 35 Ill. Adm. Code 733.102; |
b) | Pesticides, as described in 35 Ill. Adm. Code 733.103; |
c) | Thermostats, as described in 35 Ill. Adm. Code 733.104; and |
d) | Lamps, as described in 35 Ill. Adm. Code 733.105. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART B: CRITERIA FOR IDENTIFYING THE CHARACTERISTICS OF HAZARDOUS WASTE AND FOR LISTING HAZARDOUS WASTES
Section 721.110 | Criteria for Identifying the Characteristics of Hazardous Waste |
a) | USEPA stated in corresponding 40 CFR 261.10 that it identifies and defines a characteristic of hazardous waste in Subpart C of this Part only upon determining |
1) | |
A) | |
B) | |
2) | |
A) | |
B) | |
b) | Delisting procedures are contained in 35 Ill. Adm. Code 720.122. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.111 | Criteria for Listing Hazardous Waste |
a) | USEPA stated in corresponding 40 CFR 261.11 that it lists a solid waste as a hazardous waste only upon determining that the solid waste meets one of the following criteria: |
1) | |
2) | Acute hazardous waste. |
BOARD NOTE: Waste listed in accordance with these criteria are designated Acute Hazardous Waste.
3) | Toxic waste. |
BOARD NOTE: Substances are listed in Appendix H of this Part only if they have been shown in scientific studies to have toxic, carcinogenic, mutagenic, or teratogenic effects on humans or other life forms.
A) | The nature of the toxicity presented by the constituent |
B) | The concentration of the constituent in the waste |
C) | The potential of the constituent or any toxic degradation product of the constituent to migrate from the waste into the environment under the types of improper management considered in subsection (a)(3)(G) |
D) | The persistence of the constituent or any toxic degradation product of the constituent |
E) | The potential for the constituent or any toxic degradation product of the constituent to degrade into nonharmful constituents and the rate of degradation |
F) | The degree to which the constituent or any degradation product of the constituent bioaccumulates in ecosystems |
G) | The plausible types of improper management to which the waste could be subjected |
H) | The quantities of the waste generated at individual generation sites or on a regional or national basis |
I) | The nature and severity of the human health and environmental damage that has occurred as a result of the improper management of the wastes containing the constituent |
J) | Action taken by other governmental agencies or regulatory programs based on the health or environmental hazard posed by the waste or waste constituent |
K) | Such other factors as may be appropriate. |
BOARD NOTE: Wastes listed in accordance with these criteria are designated toxic wastes.
b) | USEPA stated in corresponding 40 CFR 261.11(b) that it may list classes or types of solid waste as hazardous waste if USEPA has reason to believe that individual wastes, within the class or type of waste, typically or frequently are hazardous under the definition of hazardous waste found in Section 1004(5) of the Resource Conservation and Recovery Act (42 USC |
c) | USEPA will use the criteria for listing specified in this Section to establish the exclusion limits referred to in Section 721.105(c). |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART C: CHARACTERISTICS OF HAZARDOUS WASTE
Section 721.120 | General |
a) | A solid waste, as defined in Section 721.102, which is not excluded from regulation as a hazardous waste under Section 721.104(b), is a hazardous waste if it exhibits any of the characteristics identified in this Subpart C. |
BOARD NOTE: 35 Ill. Adm. Code 722.111 sets forth the generator’s responsibility to determine whether the generator’s waste exhibits one or more characteristics identified in this Subpart C.
b) | A hazardous waste |
c) | For purposes of this Subpart C, a sample obtained using any of the applicable sampling methods specified in Appendix A of this Part is a representative sample within the meaning of 35 Ill. Adm. Code 720. |
BOARD NOTE: Since the Appendix A sampling methods are not being formally adopted, a person who desires to employ an alternative sampling method is not required to demonstrate the equivalency of the person’s method under the procedures set forth in 35 Ill. Adm. Code 720.121.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.121 | Characteristic of Ignitability |
a) | A solid waste exhibits the characteristic of ignitability if a representative sample of the waste has any of the following properties: |
1) | It is a liquid, other than an aqueous solution containing less than 24 percent alcohol by volume, and has a flash point less than 60°C (140°F), as determined by a Pensky-Martens Closed Cup Tester, using the test method specified in ASTM D-93, incorporated by reference in 35 Ill. Adm. Code 720.111, or a Setaflash Closed Cup Tester, using the test method specified in ASTM Standard D-3828, incorporated by reference in 35 Ill. Adm. Code 720.111, or as determined by an equivalent test method approved by the Board (35 Ill. Adm. Code 720.120). |
2) | It is not a liquid and is capable, under standard temperature and pressure, of causing fire through friction, absorption of moisture, or spontaneous chemical changes and, when ignited, burns so vigorously and persistently that it creates a hazard. |
3) | It is an ignitable compressed gas, as defined in 49 CFR 173.300, incorporated by reference in 35 Ill. Adm. Code 720.111, and as determined by the test methods described in that regulation or equivalent test methods approved by the Board (35 Ill. Adm. Code 720.120). |
4) | It is an oxidizer, as defined in 49 CFR 173.151, incorporated by reference in 35 Ill. Adm. Code 720.111. |
b) | A solid waste that exhibits the characteristic of ignitability has the |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.122 | Characteristic of Corrosivity |
a) | A solid waste exhibits the characteristic of corrosivity if a representative sample of the waste has either of the following properties: |
1) | It is aqueous and has a pH less than or equal to 2 or greater than or equal to 12.5, as determined by a pH meter using Method 9040 in “Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods,” |
2) | It is a liquid and corrodes steel (SAE 1020) at a rate greater than 6.35 mm (0.250 inch) per year at a test temperature of 55° C (130° F) as determined by the test method specified in NACE (National Association of Corrosion Engineers) Standard TM-01-69 as standardized in “Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods,” |
BOARD NOTE: The corrosivity characteristic determination currently does not apply to non-liquid wastes, as discussed by U.S. EPA USEPA at 45 Fed. Reg. 33109, May 19, 1980 and at 55 Fed. Reg. 22549, June 1, 1990.
b) | A solid waste that exhibits the characteristic of corrosivity has the |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.123 | Characteristic of Reactivity |
a) | A solid waste exhibits the characteristic of reactivity if a representative sample of the waste has any of the following properties: |
1) | It is normally unstable and readily undergoes violent change without detonating. |
2) | It reacts violently with water. |
3) | It forms potentially explosive mixtures with water. |
4) | When mixed with water, it generates toxic gases, vapors, or fumes in a quantity sufficient to present a danger to human health or the environment. |
5) | It is a cyanide or sulfide bearing waste which, when exposed to pH conditions between 2 and 12.5 can generate toxic gases, vapors, or fumes in a quantity sufficient to present a danger to human health or the environment. |
6) | It is capable of detonation or explosive reaction if it is subjected to a strong initiating source or if heated under confinement. |
7) | It is readily capable of detonation or explosive decomposition or reaction at standard temperature and pressure. |
8) | It is a forbidden explosive as defined in 49 CFR 173.51, or a Class A explosive as defined in 49 CFR 173.53 or a Class B explosive, as defined in 49 CFR 173.88, incorporated by reference in 35 Ill. Adm. Code 720.111. |
b) | A solid waste that exhibits the characteristic of reactivity has the |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.124 | Toxicity Characteristic |
a) | A solid waste (except manufactured gas plant waste) exhibits the characteristic of toxicity if, using the Toxicity Characteristic Leaching Procedure (TCLP), test Method 1311 in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” |
BOARD NOTE: The reference to the “EP toxicity test” in 35 Ill. Adm. Code 808.410(b)(4) is to be understood as referencing the test required by this Section.
b) | A solid waste that exhibits the characteristic of toxicity has the USEPA hazardous waste number specified in the following table that corresponds to the toxic contaminant causing it to be hazardous. |
MAXIMUM CONCENTRATION OF CONTAMINANTS FOR THE TOXICITY CHARACTERISTIC
USEPA Hazardous Waste No. |
Contaminant |
CAS Number |
Note |
Regulatory Level (mg/L) |
D004 |
Arsenic |
7440-38-2 |
5.0 |
|
D005 |
Barium |
7440-39-3 |
100.0 |
|
D018 |
Benzene |
71-43-2 |
0.5 |
|
D006 |
Cadmium |
7440-43-9 |
1.0 |
|
D019 |
Carbon tetrachloride |
56-23-5 |
0.5 |
|
D020 |
Chlordane |
57-74-9 |
0.03 |
|
D021 |
Chlorobenzene |
108-90-7 |
100.0 |
|
D022 |
Chloroform |
67-66-3 |
6.0 |
|
D007 |
Chromium |
7440-47-3 |
5.0 |
|
D023 |
o-Cresol |
95-48-7 |
|
200.0 |
D024 |
m-Cresol |
108-39-4 |
|
200.0 |
D025 |
p-Cresol |
106-44-5 |
|
200.0 |
D026 |
Cresol |
|
200.0 |
|
D016 |
2,4-D |
94-75-7 |
10.0 |
|
D027 |
1,4-Dichlorobenzene |
106-46-7 |
7.5 |
|
D028 |
1,2-Dichloroethane |
107-06-2 |
0.5 |
|
D029 |
1,1-Dichloroethylene |
75-35-4 |
0.7 |
|
D030 |
2,4-Dinitrotoluene |
121-14-2 |
|
0.13 |
D012 |
Endrin |
72-20-8 |
0.02 |
|
D031 |
Heptachlor (and its epoxide) |
76-44-8 |
0.008 |
|
D032 |
Hexachlorobenzene |
118-74-1 |
|
0.13 |
D033 |
Hexachlorobutadiene |
87-68-3 |
0.5 |
|
D034 |
Hexachloroethane |
67-72-1 |
3.0 |
|
D008 |
Lead |
7439-92-1 |
5.0 |
|
D013 |
Lindane |
58-89-9 |
0.4 |
|
D009 |
Mercury |
7439-97-6 |
0.2 |
|
D014 |
Methoxychlor |
72-43-5 |
10.0 |
|
D035 |
Methyl ethyl ketone |
78-93-3 |
200.0 |
|
D036 |
Nitrobenzene |
98-95-3 |
2.0 |
|
D037 |
Pentachlorophenol |
87-86-5 |
100.0 |
|
D038 |
Pyridine |
110-86-1 |
|
5.0 |
D010 |
Selenium |
7782-49-2 |
1.0 |
|
D011 |
Silver |
7440-22-4 |
5.0 |
|
D039 |
Tetrachloroethylene |
127-18-4 |
0.7 |
|
D015 |
Toxaphene |
8001-35-2 |
0.5 |
|
D040 |
Trichloroethylene |
79-01-6 |
0.5 |
|
D041 |
2,4,5-Trichlorophenol |
95-95-4 |
400.0 |
|
D042 |
2,4,6-Trichlorophenol |
88-06-2 |
2.0 |
|
D017 |
2,4,5-TP (Silvex) |
93-72-1 |
1.0 |
|
D043 |
Vinyl chloride |
75-01-4 |
0.2 |
Notes to Table:
Quantitation limit is greater than the calculated regulatory level. The quantitation limit therefore becomes the regulatory level. | |
If o-, m-, p-cresol concentrations cannot be differentiated, the total cresol (D026) concentration is used. The regulatory level of total cresol is 200.0 mg/L. | |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART D: LISTS OF HAZARDOUS WASTE
Section 721.130 | General |
a) | A solid waste is a hazardous waste if it is listed in this Subpart D, unless it has been excluded from this list under 35 Ill. Adm. Code 720.120 and 720.122. |
b) | The basis for listing the classes or types of wastes listed in this Subpart D is indicated by employing one or more of the |
1) | Hazard Codes |
A) | Ignitable | (I) |
B) | Corrosive | (C) |
C) | Reactive | (R) |
D) | Toxicity Characteristic waste | (E) |
E) | Acute | (H) |
F) | Toxic | (T) |
2) | Appendix G of this Part identifies the constituent |
c) | Each hazardous waste listed in this Subpart D is assigned an |
d) | The following hazardous wastes listed in Section 721.131 or 721.132 are subject to the exclusion limits for acute hazardous wastes established in Section 721.105: hazardous wastes numbers F020, F021, F022, F023, F026, and F027. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.131 | Hazardous Wastes from Nonspecific Sources |
a) | The following solid wastes are listed hazardous wastes from non-specific sources, unless they are excluded under 35 Ill. Adm. Code 720.120 and 720.122 and listed in Appendix I of this Part. |
USEPA Hazardous Waste No. |
Industry and Hazardous Waste |
Hazard Code |
F001 |
The following spent halogenated solvents used in degreasing: tetrachloroethylene, trichloroethylene, methylene chloride, 1,1,1-trichloroethane, carbon tetrachloride, and chlorinated fluorocarbons; all spent solvent mixtures and blends used in degreasing containing, before use, a total of ten percent or more (by volume) of one or more of the above halogenated solvents or those solvents listed in F002, F004, or F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. |
(T) |
F002 |
The following spent halogenated solvents: tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, chlorobenzene, 1,1,2-trichloro-1,2,2-trifluoroethane, orthodichlorobenzene, trichlorofluoromethane, and 1,1,2-trichloroethane; all spent solvent mixtures and blends containing, before use, a total of ten percent or more (by volume) of one or more of the above halogenated solvents or those solvents listed in F001, F004, or F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. |
(T) |
F003 |
The following spent non-halogenated solvents: xylene, acetone, ethyl acetate, ethyl benzene, ethyl ether, methyl isobutyl ketone, n-butyl alcohol, cyclohexanone, and methanol; all spent solvent mixtures and blends containing, before use, only the above spent non-halogenated solvents; and all spent solvent mixtures and blends containing, before use, one or more of the above non-halogenated solvents and a total of ten percent or more (by volume) of one or more of those solvents listed in F001, F002, F004, or F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. |
(I) |
F004 |
The following spent non-halogenated solvents: cresols and cresylic acid and nitrobenzene; all spent solvent mixtures and blends containing, before use, a total of ten percent or more (by volume) of one or more of the above non-halogenated solvents or those solvents listed in F001, F002, or F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. |
(T) |
F005 |
The following spent non-halogenated solvents: toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, benzene, 2-ethoxyethanol, and 2-nitropropane; all spent solvent mixtures and blends, containing, before use, a total of ten percent or more (by volume) of one or more of the above non-halogenated solvents or those solvents listed in F001, F002, or F004; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. |
(I, T) |
F006 |
Wastewater treatment sludges from electroplating operations except from the following processes: (1) sulfuric acid anodizing of aluminum; (2) tin plating on carbon steel; (3) zinc plating (segregated basis) on carbon steel; (4) aluminum or zinc-aluminum plating on carbon steel; (5) cleaning/stripping associated with tin, zinc, and aluminum plating on carbon steel; and (6) chemical etching and milling of aluminum. |
(T) |
F007 |
Spent cyanide plating bath solutions from electroplating operations. |
(R, T) |
F008 |
Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process. |
(R, T) |
F009 |
Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process. |
(R, T) |
F010 |
Quenching bath residues from oil baths from metal |
(R, T) |
F011 |
Spent cyanide solutions from salt bath pot cleaning from metal |
(R, T) |
F012 |
Quenching wastewater treatment sludges from metal |
(T) |
F019 |
Wastewater treatment sludges from the chemical conversion coating of aluminum except from zirconium phosphating in aluminum can washing when such phosphating is an exclusive conversion coating process. |
(T) |
F020 |
Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate or component in a formulating process) of tri- or tetrachlorophenol |
(H) |
F021 |
Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate or component in a formulating process) of pentachlorophenol |
(H) |
F022 |
Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the manufacturing use (as a reactant, chemical intermediate or component in a formulating process) of tetra-, penta-, or hexachlorobenzenes under alkaline conditions. |
(H) |
F023 |
Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials on equipment previously used for the production or manufacturing use (as a reactant, chemical intermediate or component in a formulating process) of tri- and tetrachlorophenols. (This listing does not include wastes from equipment used only for the production or use of hexachlorophene from highly purified 2,4,5-trichlorophenol.) |
(H) |
F024 |
Process wastes, including but not limited to, distillation residues, heavy ends, tars, and reactor cleanout wastes, from the production of certain chlorinated aliphatic hydrocarbons by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. (This listing does not include wastewaters, wastewater treatment sludges, spent catalysts, and wastes listed in this Section or in Section 721.132.) |
(T) |
F025 |
Condensed light ends, spent filters and filter aids, and spent desiccant wastes from the production of certain chlorinated aliphatic hydrocarbons by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. |
(T) |
F026 |
Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials on equipment previously used for the manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tetra-, penta-, or hexachlorobenzene under alkaline conditions. |
(H) |
F027 |
Discarded unused formulations containing tri-, tetra- or pentachlorophenol or discarded unused formulations containing compounds derived from these chlorophenols. (This listing does not include formulations containing hexachlorophene synthesized from prepurified 2,4,5-trichlorophenol as the sole component.) |
(H) |
F028 |
Residues resulting from the incineration or thermal treatment of soil contaminated with hazardous waste numbers F020, F021, F022, F023, F026, and F027. |
(T) |
F032 |
Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that currently use or have previously used chlorophenolic formulations (except potentially cross-contaminated wastes that have had the F032 waste code deleted in accordance with Section 721.135 and where the generator does not resume or initiate use of chlorophenolic formulations). This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote or pentachlorophenol. |
(T) |
F034 |
Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use creosote formulations. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote or pentachlorophenol. |
(T) |
F035 |
Wastewaters, (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use inorganic preservatives containing arsenic or chromium. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote or pentachlorophenol. |
(T) |
F037 |
Petroleum refinery primary oil/water/solids separation sludge -- Any sludge generated from the gravitational separation of oil/water/solids during the storage or treatment of process wastewaters and oily cooling wastewaters from petroleum refineries. Such sludges include, but are not limited to, those generated in: oil/water/solids separators; tanks and impoundments; ditches and other conveyances; sumps; and stormwater units receiving dry weather flow. Sludge generated in stormwater units that do not receive dry weather flow, sludge generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludge generated in aggressive biological treatment units as defined in subsection (b)(2) of this Section (including sludge generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units), and K051 wastes are not included in this listing. This listing does include residuals generated from processing or recycling oil-bearing hazardous secondary materials excluded under Section 721.104(a)(12)(A) if those residuals are to be disposed of. |
(T) |
F038 |
Petroleum refinery secondary (emulsified) oil/water/solids separation sludge -- Any sludge or float generated from the physical or chemical separation of oil/water/solids in process wastewaters and oily cooling wastewaters from petroleum refineries. Such wastes include, but are not limited to, all sludges and floats generated in the following types of units: induced air floatation (IAF) units, tanks and impoundments, and all sludges generated in dissolved air flotation (DAF) units. Sludges generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges and floats generated in aggressive biological treatment units as defined in subsection (b)(2) of this Section (including sludges and floats generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units), F037, K048, and K051 wastes are not included in this listing. |
(T) |
F039 |
Leachate (liquids |
(T) |
BOARD NOTE: The primary hazardous properties of these materials have been indicated by the letters T (Toxicity), R (Reactivity), I (Ignitability), and C (Corrosivity). The letter H indicates Acute Hazardous Waste.
b) | |
1) | For the purpose of the F037 and F038 listings, “oil/water/solids” is defined as oil or water or solids. |
2) | For the purposes of the F037 and F038 listings, the following apply: |
A) | “Aggressive biological treatment units” are defined as units |
i) | The units employ a minimum of six horsepower per million gallons of treatment volume; and either |
ii) | The hydraulic retention time of the unit is no longer than five days; or |
iii) | The hydraulic retention time is no longer than 30 days and the unit does not generate a sludge that is a hazardous waste by the toxicity characteristic. |
B) | Generators and treatment, storage, or disposal (TSD) facilities have the burden of proving that their sludges are exempt from listing as F037 or F038 wastes under this definition. Generators and TSD facilities must maintain, in their operating or other on site records, documents and data sufficient to prove |
i) | The unit is an aggressive biological treatment unit, as defined in this subsection; and |
ii) | The sludges sought to be exempted from F037 or F038 were actually generated in the aggressive biological treatment unit. |
3) | Time of generation. For the purposes of the designated waste, the “time of generation” is defined as follows: |
A) | For the F037 listing, sludges are considered to be generated at the moment of deposition in the unit, where deposition is defined as at least a temporary cessation of lateral particle movement. |
B) | For the F038 listing: |
i) | Sludges are considered to be generated at the moment of deposition in the unit, where deposition is defined as at least a temporary cessation of lateral particle movement; and |
ii) | Floats are considered to be generated at the moment they are formed in the top of the unit. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.132 | Hazardous Waste from Specific Sources |
The following solid wastes are listed hazardous wastes from specific sources unless they are excluded under 35 Ill. Adm. Code 720.120 and 720.122 and listed in Appendix I of this Part.
USEPA Hazardous Waste No. |
Industry and Hazardous Waste |
Hazard Code |
Wood Preservation Process Wastes:
K001 |
Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote or pentachlorophenol. |
(T) |
Inorganic Pigments Production Wastes:
K002 |
Wastewater treatment sludge from the production of chrome yellow and orange pigments. |
(T) |
K003 |
Wastewater treatment sludge from the production of molybdate orange pigments. |
(T) |
K004 |
Wastewater treatment sludge from the production of zinc yellow pigments. |
(T) |
K005 |
Wastewater treatment sludge from the production of chrome green pigments. |
(T) |
K006 |
Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous and hydrated). |
(T) |
K007 |
Wastewater treatment sludge from the production of iron blue pigments. |
(T) |
K008 |
Oven residue from the production of chrome oxide green pigments. |
(T) |
Organic Chemicals Production Wastes:
K009 |
Distillation bottoms from the production of acetaldehyde from ethylene. |
(T) |
K010 |
Distillation side cuts from the production of acetaldehyde from ethylene. |
(T) |
K011 |
Bottom stream from the wastewater stripper in the production of acrylonitrile. |
(R, T) |
K013 |
Bottom stream from the acetonitrile column in the production of acrylonitrile. |
(T) |
K014 |
Bottoms from the acetonitrile purification column in the production of acrylonitrile. |
(T) |
K015 |
Still bottoms from the distillation of benzyl chloride. |
(T) |
K016 |
Heavy ends or distillation residues from the production of carbon tetrachloride. |
(T) |
K017 |
Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin. |
(T) |
K018 |
Heavy ends from the fractionation column in ethyl chloride production. |
(T) |
K019 |
Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production. |
(T) |
K020 |
Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production. |
(T) |
K021 |
Aqueous spent antimony catalyst waste from fluoromethanes production. |
(T) |
K022 |
Distillation bottom tars from the production of phenol/acetone from cumene. |
(T) |
K023 |
Distillation light ends from the production of phthalic anhydride from naphthalene. |
(T) |
K024 |
Distillation bottoms from the production of phthalic anhydride from naphthalene. |
(T) |
K093 |
Distillation light ends from the production of phthalic anhydride from ortho-xylene. |
(T) |
K094 |
Distillation bottoms from the production of phthalic anhydride from ortho-xylene. |
(T) |
K025 |
Distillation bottoms from the production of nitrobenzene by the nitration of benzene. |
(T) |
K026 |
Stripping still tails from the production of methyl ethyl pyridines. |
(T) |
K027 |
Centrifuge and distillation residues from toluene diisocyanate production. |
(R, T) |
K028 |
Spent catalyst from the hydrochlorinator reactor in the production of 1,1,1-trichloroethane. |
(T) |
K029 |
Waste from the product stream stripper in the production of 1,1,1-trichloroethane. |
(T) |
K095 |
Distillation bottoms from the production of 1,1,1-trichloroethane. |
(T) |
K096 |
Heavy ends from the heavy ends column from the production of 1,1,1-trichloroethane. |
(T) |
K030 |
Column bottoms or heavy ends from the combined production of trichloroethylene and perchloroethylene. |
(T) |
K083 |
Distillation bottoms from aniline production. |
(T) |
K103 |
Process residues from aniline extraction from the production of aniline. |
(T) |
K104 |
Combined wastewater streams generated from nitrobenzene/aniline production. |
(T) |
K085 |
Distillation or fractionation column bottoms from the production of chlorobenzenes. |
(T) |
K105 |
Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes. |
(T) |
K107 |
Column bottoms from product separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. |
(C, T) |
K108 |
Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. |
(I, T) |
K109 |
Spent filter cartridges from the product purification from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. |
(T) |
K110 |
Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. |
(T) |
K111 |
Product wastewaters from the production of dinitrotoluene via nitration of toluene. |
(C, T) |
K112 |
Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene. |
(T) |
K113 |
Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. |
(T) |
K114 |
Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. |
(T) |
K115 |
Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. |
(T) |
K116 |
Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine. |
(T) |
K117 |
Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene. |
(T) |
K118 |
Spent adsorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene. |
(T) |
K136 |
Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene. |
(T) |
K156 |
Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.) |
(T) |
K157 |
Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.) |
(T) |
K158 |
Baghouse dusts and filter/separation solids from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.) |
(T) |
K159 |
Organics from the treatment of thiocarbamate wastes. |
(T) |
K161 |
Purification solids (including filtration, evaporation, and centrifugation solids), bag house dust and floor sweepings from the production of dithiocarbamate acids and their salts. (This listing does not include K125 or K126.) |
(R, T) |
K174 |
Wastewater treatment sludges from the production of ethylene dichloride or vinyl chloride monomer (including sludges that result from commingled ethylene dichloride or vinyl chloride monomer wastewater and other wastewater), unless the sludges meet the following conditions: (1) |
(T) |
K175 |
Wastewater treatment sludges from the production of vinyl chloride monomer using mercuric chloride catalyst in an acetylene-based process. |
(T) |
Inorganic Chemicals Production Wastes:
K071 |
Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used. |
(T) |
K073 |
Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production. |
(T) |
K106 |
Wastewater treatment sludge from the mercury cell process in chlorine production. |
(T) |
K176 |
Baghouse filters from the production of antimony oxide, including filters from the production of intermediates (e.g., antimony metal or crude antimony oxide). |
(E) |
K177 |
Slag from the production of antimony oxide that is speculatively accumulated or disposed of, including slag from the production of intermediates (e.g., antimony metal or crude antimony oxide). |
(T) |
K178 |
Residues from manufacturing and manufacturing-site storage of ferric chloride from acids formed during the production of titanium dioxide using the chloride-ilmenite process. |
(T) |
Pesticides Production Wastes:
K031 |
By-product salts generated in the production of MSMA and cacodylic acid. |
(T) |
K032 |
Wastewater treatment sludge from the production of chlordane. |
(T) |
K033 |
Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane. |
(T) |
K034 |
Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane. |
(T) |
K097 |
Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane. |
(T) |
K035 |
Wastewater treatment sludges generated in the production of creosote. |
(T) |
K036 |
Still bottoms from toluene reclamation distillation in the production of disulfoton. |
(T) |
K037 |
Wastewater treatment sludges from the production of disulfoton. |
(T) |
K038 |
Wastewater from the washing and stripping of phorate production. |
(T) |
K039 |
Filter cake from the filtration of diethylphosphorodithioic acid in the production of phorate. |
(T) |
K040 |
Wastewater treatment sludge from the production of phorate. |
(T) |
K041 |
Wastewater treatment sludge from the production of toxaphene. |
(T) |
K098 |
Untreated process wastewater from the production of toxaphene. |
(T) |
K042 |
Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5-T. |
(T) |
K043 |
2,6-Dichlorophenol waste from the production of 2,4-D. |
(T) |
K099 |
Untreated wastewater from the production of 2,4-D. |
(T) |
K123 |
Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salts. |
(T) |
K124 |
Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts. |
(C, T) |
K125 |
Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts. |
(T) |
K126 |
Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts. |
(T) |
K131 |
Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide. |
(C, T) |
K132 |
Spent absorbent and wastewater separator solids from the production of methyl bromide. |
(T) |
Explosives Production Wastes:
K044 |
Wastewater treatment sludges from the manufacturing and processing of explosives. |
(R) |
K045 |
Spent carbon from the treatment of wastewater containing explosives. |
(R) |
K046 |
Wastewater treatment sludges from the manufacturing, formulation and loading of lead-based initiating compounds. |
(T) |
K047 |
Pink/red water from TNT operations. |
(R) |
Petroleum Refining Wastes:
K048 |
Dissolved air flotation (DAF) float from the petroleum refining industry. |
(T) |
K049 |
Slop oil emulsion solids from the petroleum refining industry. |
(T) |
K050 |
Heat exchanger bundle cleaning sludge from the petroleum refining industry. |
(T) |
K051 |
API separator sludge from the petroleum refining industry. |
(T) |
K052 |
Tank bottoms (leaded) from the petroleum refining industry. |
(T) |
K169 |
Crude oil storage tank sediment from petroleum refining operations. |
(T) |
K170 |
Clarified slurry oil tank sediment or in-line filter/separation solids from petroleum refining operations. |
(T) |
K171 |
Spent hydrotreating catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media). |
(I, T) |
K172 |
Spent hydrorefining catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media). |
(I, T) |
Iron and Steel Production Wastes:
K061 |
Emission control dust/sludge from the primary production of steel in electric furnaces. |
(T) |
K062 |
Spent pickle liquor generated by steel finishing operations of facilities within the iron and steel industry (SIC Codes 331 and 332) (as defined in 35 Ill. Adm. Code 720.110). |
(C, T) |
Primary Aluminum Production Wastes:
K088 |
Spent potliners from primary aluminum reduction. |
(T) |
Secondary Lead Production Wastes:
K069 |
Emission control dust/sludge from secondary lead smelting. |
(T) |
BOARD NOTE: This listing is administratively stayed for sludge generated from secondary acid scrubber systems. The stay will remain in effect until this note is removed.
K100 |
Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting. |
(T) |
Veterinary Pharmaceuticals Production Wastes:
K084 |
Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds. |
(T) |
K101 |
Distillation tar residues from the distillation of aniline-based compounds in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds. |
(T) |
K102 |
Residue from use of activated carbon for decolorization in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds. |
(T) |
Ink Formulation Wastes:
K086 |
Solvent washes and sludges, caustic washes and sludges, or water washes and sludges from cleaning tubs and equipment used in the formulation of ink from pigments, dryers, soaps and stabilizers containing chromium and lead. |
(T) |
Coking Coke Production Wastes:
K060 |
Ammonia still lime sludge from coking operations. |
(T) |
K087 |
Decanter tank tar sludge from coking operations. |
(T) |
K141 |
Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the production of coke from coal or the recovery of coke by-products produced from coal. This listing does not include K087 (decanter tank tar sludges from coking operations). |
(T) |
K142 |
Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal. |
(T) |
K143 |
Process residues from the recovery of light oil, including, but not limited to, those generated in stills, decanters, and wash oil recovery units from the recovery of coke by-products produced from coal. |
(T) |
K144 |
Wastewater sump residues from light oil refining, including, but not limited to, intercepting or contamination sump sludges from the recovery of coke by-products produced from coal. |
(T) |
K145 |
Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal. |
(T) |
K147 |
Tar storage tank residues from coal tar refining. |
(T) |
K148 |
Residues from coal tar distillation, including, but not limited to, still bottoms. |
(T) |
K149 |
Distillation bottoms from the production of a - (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. (This waste does not include still bottoms from the distillation of benzyl chloride.) |
(T) |
K150 |
Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydrochloric acid recovery processes associated with the production of a - (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. |
(T) |
K151 |
Wastewater treatment sludges, excluding neutralization and biological sludges, generated during the treatment of wastewaters from the production of a - (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. |
(T) |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.133 | Discarded Commercial Chemical Products, Off-Specification Species, Container Residues, and Spill Residues Thereof |
The following materials or items are hazardous wastes if and when they are discarded or intended to be discarded, as described in Section 721.102(a)(2)(A),; when they are mixed with waste oil or used oil or other material and applied to the land for dust suppression or road treatment,; when they are otherwise applied to the land in lieu of their original intended use or when they are contained in products that are applied to land in lieu of their original intended use,; or when, in lieu of their original intended use, they are produced for use as (or as a component of) a fuel, distributed for use as a fuel, or burned as a fuel.
a) | Any commercial chemical product or manufacturing chemical intermediate having the generic name listed in subsection (e) or (f) of this Section. |
b) | Any off-specification commercial chemical product or manufacturing chemical intermediate that, if it met specifications, would have the generic name listed in subsection (e) or (f) of this Section. |
c) | Any residue remaining in a container or inner liner removed from a container that has held any commercial chemical product or manufacturing chemical intermediate having the generic name listed in subsection (e) or (f) of this Section, unless the container is empty, as defined in Section 721.107(b)(3). |
BOARD NOTE: Unless the residue is being beneficially used or reused; legitimately recycled or reclaimed; or accumulated, stored, transported, or treated prior to such use, reuse, recycling, or reclamation, the Board considers the residue to be intended for discard, and thus a hazardous waste. An example of a legitimate reuse of the residue would be where the residue remains in the container and the container is used to hold the same commercial chemical product or manufacturing chemical intermediate it previously held. An example of the discard of the residue would be where the drum is sent to a drum reconditioner that reconditions the drum but discards the residue.
d) | Any residue or contaminated soil, water, or other debris resulting from the cleanup of a spill into or on any land or water of any commercial chemical product or manufacturing chemical intermediate having the generic name listed in subsection (e) or (f) of this Section or any residue or contaminated soil, water, or other debris resulting from the cleanup of a spill into or on any land or water of any off-specification chemical product or manufacturing chemical intermediate that, if it met specifications, would have the generic name listed in subsection (e) or (f) of this Section. |
BOARD NOTE: The phrase “commercial chemical product or manufacturing chemical intermediate having the generic name listed in ...” refers to a chemical substance that is manufactured or formulated for commercial or manufacturing use which that consists of the commercially pure grade of the chemical, any technical grades of the chemical that are produced or marketed, and all formulations in which the chemical is the sole active ingredient. It does not refer to a material, such as a manufacturing process waste, that contains any of the substances listed in subsection (e) or (f) of this Section. Where a manufacturing process waste is deemed to be a hazardous waste because it contains a substance listed in subsection (e) or (f) of this Section, such waste will be listed in either Sections 721.131 or 721.132 or will be identified as a hazardous waste by the characteristics set forth in Subpart C of this Part.
e) | The commercial chemical products, manufacturing chemical intermediates, or off-specification commercial chemical products or manufacturing chemical intermediates referred to in subsections (a) through (d) of this Section are identified as acute hazardous waste (H) and are subject to the small quantity exclusion defined in Section 721.105(e). These wastes and their corresponding USEPA |
BOARD NOTE: For the convenience of the regulated community, the primary hazardous properties of these materials have been indicated by the letters T (Toxicity), and R (Reactivity). The absence of a letter indicates that the compound is only listed for acute toxicity.
USEPA Hazardous Waste No. |
Chemical Abstracts No. (CAS No.) |
Substance |
P023 |
107-20-0 |
Acetaldehyde, chloro- |
P002 |
591-08-2 |
Acetamide, N-(aminothioxomethyl) |
P057 |
640-19-7 |
Acetamide, 2-fluoro- |
P058 |
62-74-8 |
Acetic acid, fluoro-, sodium salt |
P002 |
591-08-2 |
1-Acetyl-2-thiourea |
P003 |
107-02-8 |
Acrolein |
P070 |
116-06-3 |
Aldicarb |
P203 |
1646-88-4 |
Aldicarb sulfone |
P004 |
309-00-2 |
Aldrin |
P005 |
107-18-6 |
Allyl alcohol |
P006 |
20859-73-8 |
Aluminum phosphide (R, T) |
P007 |
2763-96-4 |
5-(Aminomethyl)-3-isoxazolol |
P008 |
504-24-5 |
4-Aminopyridine |
P009 |
131-74-8 |
Ammonium picrate (R) |
P119 |
7803-55-6 |
Ammonium vanadate |
P099 |
506-61-6 |
Argentate(1-), bis(cyano-C)-, potassium |
P010 |
7778-39-4 |
Arsenic acid H3AsO4 |
P012 |
1327-53-3 |
Arsenic oxide As2O3 |
P011 |
1303-28-2 |
Arsenic oxide As2O5 |
P011 |
1303-28-2 |
Arsenic pentoxide |
P012 |
1327-53-3 |
Arsenic trioxide |
P038 |
692-42-2 |
Arsine, diethyl- |
P036 |
696-28-6 |
Arsonous dichloride, phenyl- |
P054 |
151-56-4 |
Aziridine |
P067 |
75-55-8 |
Aziridine, 2-methyl |
P013 |
542-62-1 |
Barium cyanide |
P024 |
106-47-8 |
Benzenamine, 4-chloro- |
P077 |
100-01-6 |
Benzenamine, 4-nitro- |
P028 |
100-44-7 |
Benzene, (chloromethyl)- |
P042 |
51-43-4 |
1,2-Benzenediol, 4- |
P046 |
122-09-8 |
Benzeneethanamine, a , a -dimethyl- |
P014 |
108-98-5 |
Benzenethiol |
P127 |
1563-66-2 |
7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-, methylcarbamate |
P188 |
57-64-7 |
Benzoic acid, 2-hydroxy-, compound with (3aS-cis)-1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethylpyrrolo |
P001 |
81-81-2* |
2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, and salts, when present at concentrations greater than 0.3 percent |
P028 |
100-44-7 |
Benzyl chloride |
P015 |
7440-41-7 |
Beryllium powder |
P017 |
598-31-2 |
Bromoacetone |
P018 |
357-57-3 |
Brucine |
P045 |
39196-18-6 |
2-Butanone,3,3-dimethyl-1-(methylthio)-, O- |
P021 |
592-01-8 |
Calcium cyanide |
P021 |
592-01-8 |
Calcium cyanide Ca(CN)2 |
P189 |
55285-14-8 |
Carbamic acid, |
P191 |
644-64-4 |
Carbamic acid, dimethyl-, 1- |
P192 |
119-38-0 |
Carbamic acid, dimethyl-, 3-methyl-1-(1-methylethyl)-1H-pyrazol-5-yl ester |
P190 |
1129-41-5 |
Carbamic acid, methyl-, 3-methylphenyl ester |
P127 |
1563-66-2 |
Carbofuran |
P022 |
75-15-0 |
Carbon disulfide |
P095 |
75-44-5 |
Carbonic dichloride |
P189 |
55285-14-8 |
Carbosulfan |
P023 |
107-20-0 |
Chloroacetaldehyde |
P024 |
106-47-8 |
p-Chloroaniline |
P026 |
5344-82-1 |
1-(o-Chlorophenyl)thiourea |
P027 |
542-76-7 |
3-Chloropropionitrile |
P029 |
544-92-3 |
Copper cyanide |
P029 |
544-92-3 |
Copper cyanide CuCN |
P202 |
64-00-6 |
m-Cumenyl methylcarbamate |
P030 |
Cyanides (soluble cyanide salts), not otherwise specified |
|
P031 |
460-19-5 |
Cyanogen |
P033 |
506-77-4 |
Cyanogen chloride |
P033 |
506-77-4 |
Cyanogen chloride CNCl |
P034 |
131-89-5 |
2-Cyclohexyl-4,6-dinitrophenol |
P016 |
542-88-1 |
Dichloromethyl ether |
P036 |
696-28-6 |
Dichlorophenylarsine |
P037 |
60-57-1 |
Dieldrin |
P038 |
692-42-2 |
Diethylarsine |
P041 |
311-45-5 |
Diethyl-p-nitrophenyl phosphate |
P040 |
297-97-2 |
O,O-Diethyl O-pyrazinyl phosphorothioate |
P043 |
55-91-4 |
Diisopropylfluorophosphate (DFP) |
P191 |
644-64-4 |
Dimetilan |
P004 |
309-00-2 |
1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1 a ,4 a ,4a b ,5 a ,8 a ,8a b )- |
P060 |
465-73-6 |
1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1 a ,4 a ,4a b ,5 b ,8 b ,8a b )- |
P037 |
60-57-1 |
2,7:3,6-Dimethanonaphth |
P051 |
72-20-8* |
2,7:3,6-Dimethanonaphth |
P044 |
60-51-5 |
Dimethoate |
P046 |
122-09-8 |
a , a -Dimethylphenethylamine |
P047 |
534-52-1* |
4,6-Dinitro-o-cresol and salts |
P048 |
51-28-5 |
2,4-Dinitrophenol |
P020 |
88-85-7 |
Dinoseb |
P085 |
152-16-9 |
Diphosphoramide, octamethyl- |
P111 |
107-49-3 |
Diphosphoric acid, tetraethyl ester |
P039 |
298-04-4 |
Disulfoton |
P049 |
541-53-7 |
Dithiobiuret |
P185 |
26419-73-8 |
1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O- |
P050 |
115-29-7 |
Endosulfan |
P088 |
145-73-3 |
Endothall |
P051 |
72-20-8 |
Endrin |
P051 |
72-20-8 |
Endrin, and metabolites |
P042 |
51-43-4 |
Epinephrine |
P031 |
460-19-5 |
Ethanedinitrile |
P194 |
23135-22-0 |
Ethanimidothioc acid, 2-(dimethylamino)-N- |
P066 |
16752-77-5 |
Ethanimidothioic acid, N- |
P101 |
107-12-0 |
Ethyl cyanide |
P054 |
151-56-4 |
Ethylenimine |
P097 |
52-85-7 |
Famphur |
P056 |
7782-41-4 |
Fluorine |
P057 |
640-19-7 |
Fluoroacetamide |
P058 |
62-74-8 |
Fluoroacetic acid, sodium salt |
P198 |
23422-53-9 |
Formetanate hydrochloride |
P197 |
17702-57-7 |
Formparanate |
P065 |
628-86-4 |
Fulminic acid, mercury (2+) salt (R, T) |
P059 |
76-44-8 |
Heptachlor |
P062 |
757-58-4 |
Hexaethyl tetraphosphate |
P116 |
79-19-6 |
Hydrazinecarbothioamide |
P068 |
60-34-4 |
Hydrazine, methyl- |
P063 |
74-90-8 |
Hydrocyanic acid |
P063 |
74-90-8 |
Hydrogen cyanide |
P096 |
7803-51-2 |
Hydrogen phosphide |
P060 |
465-73-6 |
Isodrin |
P192 |
119-38-0 |
Isolan |
P202 |
64-00-6 |
3-Isopropylphenyl-N-methylcarbamate |
P007 |
2763-96-4 |
3(2H)-Isoxazolone, 5-(aminomethyl)- |
P196 |
15339-36-3 |
Manganese, bis(dimethylcarbamodithioato-S,S’)- |
P196 |
15339-36-3 |
Manganese dimethyldithiocarbamate |
P092 |
62-38-4 |
Mercury, (acetato-O)phenyl- |
P065 |
628-86-4 |
Mercury fulminate (R, T) |
P082 |
62-75-9 |
Methanamine, N-methyl-N-nitroso- |
P064 |
624-83-9 |
Methane, isocyanato- |
P016 |
542-88-1 |
Methane, oxybis |
P112 |
509-14-8 |
Methane, tetranitro- (R) |
P118 |
75-70-7 |
Methanethiol, trichloro- |
P198 |
23422-53-9 |
Methanimidamide, N,N-dimethyl-N’-[3- |
P197 |
17702-57-7 |
Methanimidamide, N,N-dimethyl-N’- |
P199 |
2032-65-7 |
Methiocarb |
P050 |
115-29-7 |
6,9-Methano-2,4,3-benzodioxathiepen, 6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide |
P059 |
76-44-8 |
4,7-Methano-1H-indene, 1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro- |
P066 |
16752-77-5 |
Methomyl |
P068 |
60-34-4 |
Methyl hydrazine |
P064 |
624-83-9 |
Methyl isocyanate |
P069 |
75-86-5 |
2-Methyllactonitrile |
P071 |
298-00-0 |
Methyl parathion |
P190 |
1129-41-5 |
Metolcarb |
P129 |
315-8-4 |
Mexacarbate |
P072 |
86-88-4 |
a -Naphthylthiourea |
P073 |
13463-39-3 |
Nickel carbonyl |
P073 |
13463-39-3 |
Nickel carbonyl Ni(CO)4, (T-4)- |
P074 |
557-19-7 |
Nickel cyanide |
P074 |
557-19-7 |
Nickel cyanide Ni(CN)2 |
P075 |
54-11-5* |
Nicotine, and salts |
P076 |
10102-43-9 |
Nitric oxide |
P077 |
100-01-6 |
p-Nitroaniline |
P078 |
10102-44-0 |
Nitrogen dioxide |
P076 |
10102-43-9 |
Nitrogen oxide NO |
P078 |
10102-44-0 |
Nitrogen oxide NO2 |
P081 |
55-63-0 |
Nitroglycerine (R) |
P082 |
62-75-9 |
N-Nitrosodimethylamine |
P084 |
4549-40-0 |
N-Nitrosomethylvinylamine |
P085 |
152-16-9 |
Octamethylpyrophosphoramide |
P087 |
20816-12-0 |
Osmium oxide OsO4, (T-4)- |
P087 |
20816-12-0 |
Osmium tetroxide |
P088 |
145-73-3 |
7-Oxabicyclo |
P194 |
23135-22-0 |
Oxamyl |
P089 |
56-38-2 |
Parathion |
P034 |
131-89-5 |
Phenol, 2-cyclohexyl-4,6-dinitro- |
P128 |
315-18-4 |
Phenol, 4-(dimethylamino)-3,5-dimethyl-, methylcarbamate (ester) |
P199 |
2032-65-7 |
Phenol, (3,5-dimethyl-4-(methylthio)-, methylcarbamate |
P048 |
51-28-5 |
Phenol, 2,4-dinitro- |
P047 |
534-52-1* |
Phenol, 2-methyl-4,6-dinitro-, and salts |
P202 |
64-00-6 |
Phenol, 3-(1-methylethyl)-, methyl carbamate |
P201 |
2631-37-0 |
Phenol, 3-methyl-5-(1-methylethyl)-, methyl carbamate |
P020 |
88-85-7 |
Phenol, 2-(1-methylpropyl)-4,6-dinitro- |
P009 |
131-74-8 |
Phenol, 2,4,6-trinitro-, ammonium salt (R) |
P092 |
62-38-4 |
Phenylmercury acetate |
P093 |
103-85-5 |
Phenylthiourea |
P094 |
298-02-2 |
Phorate |
P095 |
75-44-5 |
Phosgene |
P096 |
7803-51-2 |
Phosphine |
P041 |
311-45-5 |
Phosphoric acid, diethyl 4-nitrophenyl ester |
P039 |
298-04-4 |
Phosphorodithioic acid, O,O-diethyl S- |
P094 |
298-02-2 |
Phosphorodithioic acid, O,O-diethyl S- |
P044 |
60-51-5 |
Phosphorodithioic acid, O,O-dimethyl S- |
P043 |
55-91-4 |
Phosphorofluoridic acid, bis(1-methylethyl)ester |
P089 |
56-38-2 |
Phosphorothioic acid, O,O-diethyl O-(4-nitrophenyl) ester |
P040 |
297-97-2 |
Phosphorothioic acid, O,O-diethyl O-pyrazinyl ester |
P097 |
52-85-7 |
Phosphorothioic acid, O- |
P071 |
298-00-0 |
Phosphorothioic acid, O,O-dimethyl O-(4-nitrophenyl) ester |
P204 |
57-47-6 |
Physostigmine |
P188 |
57-64-7 |
Physostigmine salicylate |
P110 |
78-00-2 |
Plumbane, tetraethyl- |
P098 |
151-50-8 |
Potassium cyanide |
P098 |
151-50-8 |
Potassium cyanide KCN |
P099 |
506-61-6 |
Potassium silver cyanide |
P201 |
2631-37-0 |
Promecarb |
P203 |
1646-88-4 |
Propanal, 2-methyl-2-(methyl-sulfonyl)-, O- |
P070 |
116-06-3 |
Propanal, 2-methyl-2-(methylthio)-, O- |
P101 |
107-12-0 |
Propanenitrile |
P027 |
542-76-7 |
Propanenitrile, 3-chloro- |
P069 |
75-86-5 |
Propanenitrile, 2-hydroxy-2-methyl- |
P081 |
55-63-0 |
1,2,3-Propanetriol, trinitrate- (R) |
P017 |
598-31-2 |
2-Propanone, 1-bromo- |
P102 |
107-19-7 |
Propargyl alcohol |
P003 |
107-02-8 |
2-Propenal |
P005 |
107-18-6 |
2-Propen-1-ol |
P067 |
75-55-8 |
1,2-Propylenimine |
P102 |
107-19-7 |
2-Propyn-1-ol |
P008 |
504-24-5 |
4-Pyridinamine |
P075 |
54-11-5* |
Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)- and salts |
P204 |
57-47-6 |
Pyrrolo |
P114 |
12039-52-0 |
Selenious acid, dithallium (1+) salt |
P103 |
630-10-4 |
Selenourea |
P104 |
506-64-9 |
Silver cyanide |
P104 |
506-64-9 |
Silver cyanide AgCN |
P105 |
26628-22-8 |
Sodium azide |
P106 |
143-33-9 |
Sodium cyanide |
P106 |
143-33-9 |
Sodium cyanide NaCN |
P108 |
57-24-9* |
Strychnidin-10-one, and salts |
P018 |
357-57-3 |
Strychnidin-10-one, 2,3-dimethoxy- |
P108 |
57-24-9* |
Strychnine and salts |
P115 |
7446-18-6 |
Sulfuric acid, dithallium (1+) salt |
P109 |
3689-24-5 |
Tetraethyldithiopyrophosphate |
P110 |
78-00-2 |
Tetraethyl lead |
P111 |
107-49-3 |
Tetraethylpyrophosphate |
P112 |
509-14-8 |
Tetranitromethane (R) |
P062 |
757-58-4 |
Tetraphosphoric acid, hexaethyl ester |
P113 |
1314-32-5 |
Thallic oxide |
P113 |
1314-32-5 |
Thallium oxide Tl2O3 |
P114 |
12039-52-0 |
Thallium (I) selenite |
P115 |
7446-18-6 |
Thallium (I) sulfate |
P109 |
3689-24-5 |
Thiodiphosphoric acid, tetraethyl ester |
P045 |
39196-18-4 |
Thiofanox |
P049 |
541-53-7 |
Thioimidodicarbonic diamide |
P014 |
108-98-5 |
Thiophenol |
P116 |
79-19-6 |
Thiosemicarbazide |
P026 |
5344-82-1 |
Thiourea, (2-chlorophenyl)- |
P072 |
86-88-4 |
Thiourea, 1-naphthalenyl- |
P093 |
103-85-5 |
Thiourea, phenyl- |
P123 |
8001-35-2 |
Toxaphene |
P185 |
26419-73-8 |
Tirpate |
P118 |
75-70-7 |
Trichloromethanethiol |
P119 |
7803-55-6 |
Vanadic acid, ammonium salt |
P120 |
1314-62-1 |
Vanadium oxide V2O5 |
P120 |
1314-62-1 |
Vanadium pentoxide |
P084 |
4549-40-0 |
Vinylamine, N-methyl-N-nitroso- |
P001 |
81-81-2* |
Warfarin, and salts, when present at concentrations greater than 0.3 percent |
P121 |
557-21-1 |
Zinc cyanide |
P121 |
557-21-1 |
Zinc cyanide Zn(CN)2 |
P205 |
137-30-4 |
Zinc, bis(dimethylcarbamodithioato-S,S’)- |
P122 |
1314-84-7 |
Zinc phosphide Zn3P2, when present at concentrations greater than 10 percent (R, T) |
P205 |
137-30-4 |
Ziram |
BOARD NOTE: An asterisk (*) following the CAS number indicates that the CAS number is given for the parent compound only.
f) | The commercial chemical products, manufacturing chemical intermediates, or off-specification commercial chemical products referred to in subsections (a) through (d) of this Section, are identified as toxic wastes (T) unless otherwise designated and are subject to the small quantity exclusion defined in Section 721.105(a) and (g). These wastes and their corresponding USEPA |
BOARD NOTE: For the convenience of the regulated community, the primary hazardous properties of these materials have been indicated by the letters T (Toxicity), R (Reactivity), I (Ignitability), and C (Corrosivity). The absence of a letter indicates that the compound is only listed for toxicity.
USEPA Hazardous Waste No. |
Chemical Abstracts No. (CAS No.) |
Substance |
U394 |
30558-43-1 |
A2213 |
U001 |
75-07-0 |
Acetaldehyde (I) |
U034 |
75-87-6 |
Acetaldehyde, trichloro- |
U187 |
62-44-2 |
Acetamide, N-(4-ethoxyphenyl)- |
U005 |
53-96-3 |
Acetamide, N-9H-fluoren-2-yl- |
U240 |
P 94-75-7 |
Acetic acid, (2,4-dichlorophenoxy)-, salts and esters |
U112 |
141-78-6 |
Acetic acid, ethyl ester (I) |
U144 |
301-04-2 |
Acetic acid, lead (2+) salt |
U214 |
563-68-8 |
Acetic acid, thallium (1+) salt |
See F027 |
93-76-5 |
Acetic acid, (2,4,5-trichlorophenoxy)- |
U002 |
67-64-1 |
Acetone (I) |
U003 |
75-05-8 |
Acetonitrile (I, T) |
U004 |
98-86-2 |
Acetophenone |
U005 |
53-96-3 |
2-Acetylaminofluorene |
U006 |
75-36-5 |
Acetyl chloride (C, R, T) |
U007 |
79-06-1 |
Acrylamide |
U008 |
79-10-7 |
Acrylic acid (I) |
U009 |
107-13-1 |
Acrylonitrile |
U011 |
61-82-5 |
Amitrole |
U012 |
62-53-3 |
Aniline (I, T) |
U136 |
75-60-5 |
Arsinic acid, dimethyl- |
U014 |
492-80-8 |
Auramine |
U015 |
115-02-6 |
Azaserine |
U010 |
50-07-7 |
Azirino |
U280 |
101-27-9 |
Barban |
U278 |
22781-23-3 |
Bendiocarb |
U364 |
22961-82-6 |
Bendiocarb phenol |
U271 |
17804-35-2 |
Benomyl |
U157 |
56-49-5 |
Benz |
U016 |
225-51-4 |
Benz(c)acridine |
U017 |
98-87-3 |
Benzal chloride |
U192 |
23950-58-5 |
Benzamide, 3,5-dichloro-N-(1,1-dimethyl-2-propynyl)- |
U018 |
56-55-3 |
Benz |
U094 |
57-97-6 |
Benz |
U012 |
62-53-3 |
Benzenamine (I, T) |
U014 |
492-80-8 |
Benzenamine, 4,4'-carbonimidoylbis |
U049 |
3165-93-3 |
Benzenamine, 4-chloro-2-methyl-, hydrochloride |
U093 |
60-11-7 |
Benzenamine, N,N-dimethyl-4-(phenylazo)- |
U328 |
95-53-4 |
Benzenamine, 2-methyl- |
U353 |
106-49-0 |
Benzenamine, 4-methyl- |
U158 |
101-14-4 |
Benzenamine, 4,4'-methylenebis |
U222 |
636-21-5 |
Benzenamine, 2-methyl-, hydrochloride |
U181 |
99-55-8 |
Benzenamine, 2-methyl-5-nitro- |
U019 |
71-43-2 |
Benzene (I, T) |
U038 |
510-15-6 |
Benzeneacetic acid, 4-chloro- a -(4-chlorophenyl)- a -hydroxy-, ethyl ester |
U030 |
101-55-3 |
Benzene, 1-bromo-4-phenoxy- |
U035 |
305-03-3 |
Benzenebutanoic acid, 4- |
U037 |
108-90-7 |
Benzene, chloro- |
U221 |
25376-45-8 |
Benzenediamine, ar-methyl- |
U028 |
117-81-7 |
1,2-Benzenedicarboxylic acid, bis(2-ethylhexyl) ester |
U069 |
84-74-2 |
1,2-Benzenedicarboxylic acid, dibutyl ester |
U088 |
84-66-2 |
1,2-Benzenedicarboxylic acid, diethyl ester |
U102 |
131-11-3 |
1,2-Benzenedicarboxylic acid, dimethyl ester |
U107 |
117-84-0 |
1,2-Benzenedicarboxylic acid, dioctyl ester |
U070 |
95-50-1 |
Benzene, 1,2-dichloro- |
U071 |
541-73-1 |
Benzene, 1,3-dichloro- |
U072 |
106-46-7 |
Benzene, 1,4-dichloro- |
U060 |
72-54-8 |
Benzene, 1,1'-(2,2-dichloroethylidene)bis |
U017 |
98-87-3 |
Benzene, (dichloromethyl)- |
U223 |
26471-62-5 |
Benzene, 1,3-diisocyanatomethyl- (R, T) |
U239 |
1330-20-7 |
Benzene, dimethyl- (I, T) |
U201 |
108-46-3 |
1,3-Benzenediol |
U127 |
118-74-1 |
Benzene, hexachloro- |
U056 |
110-82-7 |
Benzene, hexahydro- (I) |
U220 |
108-88-3 |
Benzene, methyl- |
U105 |
121-14-2 |
Benzene, 1-methyl-2,4-dinitro- |
U106 |
606-20-2 |
Benzene, 2-methyl-1,3-dinitro- |
U055 |
98-82-8 |
Benzene, (1-methylethyl)- (I) |
U169 |
98-95-3 |
Benzene, nitro- |
U183 |
608-93-5 |
Benzene, pentachloro- |
U185 |
82-68-8 |
Benzene, pentachloronitro- |
U020 |
98-09-9 |
Benzenesulfonic acid chloride (C, R) |
U020 |
98-09-9 |
Benzenesulfonyl chloride (C, R) |
U207 |
95-94-3 |
Benzene, 1,2,4,5-tetrachloro- |
U061 |
50-29-3 |
Benzene, 1,1'-(2,2,2-trichloroethylidene)bis |
U247 |
72-43-5 |
Benzene, 1,1'-(2,2,2-trichloroethylidene)bis |
U023 |
98-07-7 |
Benzene, (trichloromethyl)- |
U234 |
99-35-4 |
Benzene, 1,3,5-trinitro- |
U021 |
92-87-5 |
Benzidene |
U202 |
P 81-07-2 |
1,2-Benzisothiazol-3(2H)-one, 1,1-dioxide, and salts |
U203 |
94-59-7 |
1,3-Benzodioxole, 5-(2-propenyl)- |
U141 |
120-58-1 |
1,3-Benzodioxole, 5-(1-propenyl)- |
U090 |
94-58-6 |
1,3-Benzodioxole, 5-propyl- |
U278 |
22781-23-3 |
1,3-Benzodioxol-4-ol, 2,2-dimethyl-, methyl carbamate |
U364 |
22961-82-6 |
1,3-Benzodioxol-4-ol, 2,2-dimethyl- |
U367 |
1563-38-8 |
7-Benzofuranol, 2,3-dihydro-2,2-dimethyl- |
U064 |
189-55-9 |
Benzo |
U248 |
P 81-81-2 |
2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, and salts, when present at concentrations of 0.3 percent or less |
U022 |
50-32-8 |
Benzo |
U197 |
106-51-4 |
p-Benzoquinone |
U023 |
98-07-7 |
Benzotrichloride (C, R, T) |
U085 |
1464-53-5 |
2,2'-Bioxirane |
U021 |
92-87-5 |
|
U073 |
91-94-1 |
|
U091 |
119-90-4 |
|
U095 |
119-93-7 |
|
U225 |
75-25-2 |
Bromoform |
U030 |
101-55-3 |
4-Bromophenyl phenyl ether |
U128 |
87-68-3 |
1,3-Butadiene, 1,1,2,3,4,4-hexachloro- |
U172 |
924-16-3 |
1-Butanamine, N-butyl-N-nitroso- |
U031 |
71-36-3 |
1-Butanol (I) |
U159 |
78-93-3 |
2-Butanone (I, T) |
U160 |
1338-23-4 |
2-Butanone, peroxide (R, T) |
U053 |
4170-30-3 |
2-Butenal |
U074 |
764-41-0 |
2-Butene, 1,4-dichloro- (I, T) |
U143 |
303-34-4 |
2-Butenoic acid, 2-methyl-, 7- |
U031 |
71-36-3 |
n-Butyl alcohol (I) |
U136 |
75-60-5 |
Cacodylic acid |
U032 |
13765-19-0 |
Calcium chromate |
U372 |
10605-21-7 |
Carbamic acid, 1H-benzimidazol-2-yl, methyl ester |
U271 |
17804-35-2 |
Carbamic acid, |
U280 |
101-27-9 |
Carbamic acid, (3-chlorophenyl)-, 4-chloro-2-butynyl ester |
U238 |
51-79-6 |
Carbamic acid, ethyl ester |
U178 |
615-53-2 |
Carbamic acid, methylnitroso-, ethyl ester |
U373 |
122-42-9 |
Carbamic acid, phenyl-, 1-methylethyl ester |
U409 |
23564-05-8 |
Carbamic acid, |
U097 |
79-44-7 |
Carbamic chloride, dimethyl- |
U114 |
P 111-54-6 |
Carbamodithioic acid, 1,2-ethanediylbis-, salts and esters |
U062 |
2303-16-4 |
Carbamothioic acid, bis(1-methylethyl)-, S-(2,3-dichloro-2-propenyl) ester |
U389 |
2303-17-5 |
Carbamothioic acid, bis(1-methylethyl)-, S-(2,3,3-trichloro-2-propenyl) ester |
U387 |
52888-80-9 |
Carbamothioic acid, dipropyl-, S-(phenylmethyl) ester |
U279 |
63-25-2 |
Carbaryl |
U372 |
10605-21-7 |
Carbendazim |
U367 |
1563-38-8 |
Carbofuran phenol |
U215 |
6533-73-9 |
Carbonic acid, dithallium (1+) salt |
U033 |
353-50-4 |
Carbonic difluoride |
U156 |
79-22-1 |
Carbonochloridic acid, methyl ester (I, T) |
U033 |
353-50-4 |
Carbon oxyfluoride (R, T) |
U211 |
56-23-5 |
Carbon tetrachloride |
U034 |
75-87-6 |
Chloral |
U035 |
305-03-3 |
Chlorambucil |
U036 |
57-74-9 |
Chlordane, a and g isomers |
U026 |
494-03-1 |
Chlornaphazin |
U037 |
108-90-7 |
Chlorobenzene |
U038 |
510-15-6 |
Chlorobenzilate |
U039 |
59-50-7 |
p-Chloro-m-cresol |
U042 |
110-75-8 |
2-Chloroethyl vinyl ether |
U044 |
67-66-3 |
Chloroform |
U046 |
107-30-2 |
Chloromethyl methyl ether |
U047 |
91-58-7 |
b -Chloronaphthalene |
U048 |
95-57-8 |
o-Chlorophenol |
U049 |
3165-93-3 |
4-Chloro-o-toluidine, hydrochloride |
U032 |
13765-19-0 |
Chromic acid H2CrO4, calcium salt |
U050 |
218-01-9 |
Chrysene |
U051 |
Creosote |
|
U052 |
1319-77-3 |
Cresol (Cresylic acid) |
U053 |
4170-30-3 |
Crotonaldehyde |
U055 |
98-82-8 |
Cumeme (I) |
U246 |
506-68-3 |
Cyanogen bromide CNBr |
U197 |
106-51-4 |
2,5-Cyclohexadiene-1,4-dione |
U056 |
110-82-7 |
Cyclohexane (I) |
U129 |
58-89-9 |
Cyclohexane, 1,2,3,4,5,6-hexachloro-, (1 a ,2 a ,3 b ,4 a ,5 a ,6 b )- |
U057 |
108-94-1 |
Cyclohexanone (I) |
U130 |
77-47-4 |
1,3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro- |
U058 |
50-18-0 |
Cyclophosphamide |
U240 |
P 94-75-7 |
2,4-D, salts and esters |
U059 |
20830-81-3 |
Daunomycin |
U060 |
72-54-8 |
DDD |
U061 |
50-29-3 |
DDT |
U062 |
2303-16-4 |
Diallate |
U063 |
53-70-3 |
Dibenz |
U064 |
189-55-9 |
Dibenzo |
U066 |
96-12-8 |
1,2-Dibromo-3-chloropropane |
U069 |
84-74-2 |
Dibutyl phthalate |
U070 |
95-50-1 |
o-Dichlorobenzene |
U071 |
541-73-1 |
m-Dichlorobenzene |
U072 |
106-46-7 |
p-Dichlorobenzene |
U073 |
91-94-1 |
3,3'-Dichlorobenzidine |
U074 |
764-41-0 |
1,4-Dichloro-2-butene (I, T) |
U075 |
75-71-8 |
Dichlorodifluoromethane |
U078 |
75-35-4 |
1,1-Dichloroethylene |
U079 |
156-60-5 |
1,2-Dichloroethylene |
U025 |
111-44-4 |
Dichloroethyl ether |
U027 |
108-60-1 |
Dichloroisopropyl ether |
U024 |
111-91-1 |
Dichloromethoxy ethane |
U081 |
120-83-2 |
2,4-Dichlorophenol |
U082 |
87-65-0 |
2,6-Dichlorophenol |
U084 |
542-75-6 |
1,3-Dichloropropene |
U085 |
1464-53-5 |
1,2:3,4-Diepoxybutane (I, T) |
U395 |
5952-26-1 |
Diethylene glycol, dicarbamate |
U108 |
123-91-1 |
1,4-Diethyleneoxide |
U028 |
117-81-7 |
Diethylhexyl phthalate |
U086 |
1615-80-1 |
N,N’-Diethylhydrazine |
U087 |
3288-58-2 |
O,O-Diethyl S-methyl dithiophosphate |
U088 |
84-66-2 |
Diethyl phthalate |
U089 |
56-53-1 |
Diethylstilbestrol |
U090 |
94-58-6 |
Dihydrosafrole |
U091 |
119-90-4 |
3,3'-Dimethoxybenzidine |
U092 |
124-40-3 |
Dimethylamine (I) |
U093 |
60-11-7 |
p-Dimethylaminoazobenzene |
U094 |
57-97-6 |
7,12-Dimethylbenz |
U095 |
119-93-7 |
3,3'-Dimethylbenzidine |
U096 |
80-15-9 |
a , a -Dimethylbenzylhydroperoxide (R) |
U097 |
79-44-7 |
Dimethylcarbamoyl chloride |
U098 |
57-14-7 |
1,1-Dimethylhydrazine |
U099 |
540-73-8 |
1,2-Dimethylhydrazine |
U101 |
105-67-9 |
2,4-Dimethylphenol |
U102 |
131-11-3 |
Dimethyl phthalate |
U103 |
77-78-1 |
Dimethyl sulfate |
U105 |
121-14-2 |
2,4-Dinitrotoluene |
U106 |
606-20-2 |
2,6-Dinitrotoluene |
U107 |
117-84-0 |
Di-n-octyl phthalate |
U108 |
123-91-1 |
1,4-Dioxane |
U109 |
122-66-7 |
1,2-Diphenylhydrazine |
U110 |
142-84-7 |
Dipropylamine (I) |
U111 |
621-64-7 |
Di-n-propylnitrosamine |
U041 |
106-89-8 |
Epichlorohydrin |
U001 |
75-07-0 |
Ethanal (I) |
U404 |
121-44-8 |
Ethanamine, N,N-diethyl- |
U174 |
55-18-5 |
Ethanamine, N-ethyl-N-nitroso- |
U155 |
91-80-5 |
1,2-Ethanediamine, N,N-dimethyl-N’-2-pyridinyl-N’-(2-thienylmethyl)- |
U067 |
106-93-4 |
Ethane, 1,2-dibromo- |
U076 |
75-34-3 |
Ethane, 1,1-dichloro- |
U077 |
107-06-2 |
Ethane, 1,2-dichloro- |
U131 |
67-72-1 |
Ethane, hexachloro- |
U024 |
111-91-1 |
Ethane, 1,1'- |
U117 |
60-29-7 |
Ethane, 1,1'-oxybis- (I) |
U025 |
111-44-4 |
Ethane, 1,1'-oxybis |
U184 |
76-01-7 |
Ethane, pentachloro- |
U208 |
630-20-6 |
Ethane, 1,1,1,2-tetrachloro- |
U209 |
79-34-5 |
Ethane, 1,1,2,2-tetrachloro- |
U218 |
62-55-5 |
Ethanethioamide |
U226 |
71-55-6 |
Ethane, 1,1,1-trichloro- |
U227 |
79-00-5 |
Ethane, 1,1,2-trichloro- |
U410 |
59669-26-0 |
Ethanimidothioic acid, N,N’- |
U394 |
30558-43-1 |
Ethanimidothioic acid, 2-(dimethylamino)-N-hydroxy-2-oxo-, methyl ester |
U359 |
110-80-5 |
Ethanol, 2-ethoxy- |
U173 |
1116-54-7 |
Ethanol, 2,2'-(nitrosoimino)bis- |
U395 |
5952-26-1 |
Ethanol, 2,2'-oxybis-, dicarbamate |
U004 |
98-86-2 |
Ethanone, 1-phenyl- |
U043 |
75-01-4 |
Ethene, chloro- |
U042 |
110-75-8 |
Ethene, (2-chloroethoxy)- |
U078 |
75-35-4 |
Ethene, 1,1-dichloro- |
U079 |
156-60-5 |
Ethene, 1,2-dichloro-, (E)- |
U210 |
127-18-4 |
Ethene, tetrachloro- |
U228 |
79-01-6 |
Ethene, trichloro- |
U112 |
141-78-6 |
Ethyl acetate (I) |
U113 |
140-88-5 |
Ethyl acrylate (I) |
U238 |
51-79-6 |
Ethyl carbamate (urethane) |
U117 |
60-29-7 |
Ethyl ether |
U114 |
P 111-54-6 |
Ethylenebisdithiocarbamic acid, salts and esters |
U067 |
106-93-4 |
Ethylene dibromide |
U077 |
107-06-2 |
Ethylene dichloride |
U359 |
110-80-5 |
Ethylene glycol monoethyl ether |
U115 |
75-21-8 |
Ethylene oxide (I, T) |
U116 |
96-45-7 |
Ethylenethiourea |
U076 |
75-34-3 |
Ethylidene dichloride |
U118 |
97-63-2 |
Ethyl methacrylate |
U119 |
62-50-0 |
Ethyl methanesulfonate |
U120 |
206-44-0 |
Fluoranthene |
U122 |
50-00-0 |
Formaldehyde |
U123 |
64-18-6 |
Formic acid (C, T) |
U124 |
110-00-9 |
Furan (I) |
U125 |
98-01-1 |
2-Furancarboxaldehyde (I) |
U147 |
108-31-6 |
2,5-Furandione |
U213 |
109-99-9 |
Furan, tetrahydro- (I) |
U125 |
98-01-1 |
Furfural (I) |
U124 |
110-00-9 |
Furfuran (I) |
U206 |
18883-66-4 |
Glucopyranose, 2-deoxy-2-(3-methyl-3-nitrosoureido)-, D- |
U206 |
18883-66-4 |
D-Glucose, 2-deoxy-2- |
U126 |
765-34-4 |
Glycidylaldehyde |
U163 |
70-25-7 |
Guanidine, N-methyl-N’-nitro-N-nitroso- |
U127 |
118-74-1 |
Hexachlorobenzene |
U128 |
87-68-3 |
Hexachlorobutadiene |
U130 |
77-47-4 |
Hexachlorocyclopentadiene |
U131 |
67-72-1 |
Hexachloroethane |
U132 |
70-30-4 |
Hexachlorophene |
U243 |
1888-71-7 |
Hexachloropropene |
U133 |
302-01-2 |
Hydrazine (R, T) |
U086 |
1615-80-1 |
Hydrazine, 1,2-diethyl- |
U098 |
57-14-7 |
Hydrazine, 1,1-dimethyl- |
U099 |
540-73-8 |
Hydrazine, 1,2-dimethyl- |
U109 |
122-66-7 |
Hydrazine, 1,2-diphenyl- |
U134 |
7664-39-3 |
Hydrofluoric acid (C, T) |
U134 |
7664-39-3 |
Hydrogen fluoride (C, T) |
U135 |
7783-06-4 |
Hydrogen sulfide |
U135 |
7783-06-4 |
Hydrogen sulfide H2S |
U096 |
80-15-9 |
Hydroperoxide, 1-methyl-1-phenylethyl- (R) |
U116 |
96-45-7 |
2-Imidazolidinethione |
U137 |
193-39-5 |
Indeno |
U190 |
85-44-9 |
1,3-Isobenzofurandione |
U140 |
78-83-1 |
Isobutyl alcohol (I, T) |
U141 |
120-58-1 |
Isosafrole |
U142 |
143-50-0 |
Kepone |
U143 |
303-34-4 |
Lasiocarpene |
U144 |
301-04-2 |
Lead acetate |
U146 |
1335-32-6 |
Lead, bis(acetato-O)tetrahydroxytri- |
U145 |
7446-27-7 |
Lead phosphate |
U146 |
1335-32-6 |
Lead subacetate |
U129 |
58-89-9 |
Lindane |
U163 |
70-25-7 |
MNNG |
U147 |
108-31-6 |
Maleic anhydride |
U148 |
123-33-1 |
Maleic hydrazide |
U149 |
109-77-3 |
Malononitrile |
U150 |
148-82-3 |
Melphalan |
U151 |
7439-97-6 |
Mercury |
U152 |
126-98-7 |
Methacrylonitrile (I, T) |
U092 |
124-40-3 |
Methanamine, N-methyl- (I) |
U029 |
74-83-9 |
Methane, bromo- |
U045 |
74-87-3 |
Methane, chloro- (I, T) |
U046 |
107-30-2 |
Methane, chloromethoxy- |
U068 |
74-95-3 |
Methane, dibromo- |
U080 |
75-09-2 |
Methane, dichloro- |
U075 |
75-71-8 |
Methane, dichlorodifluoro- |
U138 |
74-88-4 |
Methane, iodo- |
U119 |
62-50-0 |
Methanesulfonic acid, ethyl ester |
U211 |
56-23-5 |
Methane, tetrachloro- |
U153 |
74-93-1 |
Methanethiol (I, T) |
U225 |
75-25-2 |
Methane, tribromo- |
U044 |
67-66-3 |
Methane, trichloro- |
U121 |
75-69-4 |
Methane, trichlorofluoro- |
U036 |
57-74-9 |
4,7-Methano-1H-indene, 1,2,4,5,6,7,8,8-octachloro-2,3,3a,4,7,7a-hexahydro- |
U154 |
67-56-1 |
Methanol (I) |
U155 |
91-80-5 |
Methapyrilene |
U142 |
143-50-0 |
1,3,4-Metheno-2H-cyclobuta |
U247 |
72-43-5 |
Methoxychlor |
U154 |
67-56-1 |
Methyl alcohol (I) |
U029 |
74-83-9 |
Methyl bromide |
U186 |
504-60-9 |
1-Methylbutadiene (I) |
U045 |
74-87-3 |
Methyl chloride (I, T) |
U156 |
79-22-1 |
Methyl chlorocarbonate (I, T) |
U226 |
71-55-6 |
Methylchloroform |
U157 |
56-49-5 |
3-Methylcholanthrene |
U158 |
101-14-4 |
4,4'-Methylenebis(2-chloroaniline) |
U068 |
74-95-3 |
Methylene bromide |
U080 |
75-09-2 |
Methylene chloride |
U159 |
78-93-3 |
Methyl ethyl ketone (MEK) (I, T) |
U160 |
1338-23-4 |
Methyl ethyl ketone peroxide (R, T) |
U138 |
74-88-4 |
Methyl iodide |
U161 |
108-10-1 |
Methyl isobutyl ketone (I) |
U162 |
80-62-6 |
Methyl methacrylate (I, T) |
U161 |
108-10-1 |
4-Methyl-2-pentanone (I) |
U164 |
56-04-2 |
Methylthiouracil |
U010 |
50-07-7 |
Mitomycin C |
U059 |
20830-81-3 |
5,12-Naphthacenedione, 8-acetyl-10- |
U167 |
134-32-7 |
1-Naphthalenamine |
U168 |
91-59-8 |
2-Naphthalenamine |
U026 |
494-03-1 |
Naphthaleneamine, N,N’-bis(2-chloroethyl)- |
U165 |
91-20-3 |
Naphthalene |
U047 |
91-58-7 |
Naphthalene, 2-chloro- |
U166 |
130-15-4 |
1,4-Naphthalenedione |
U236 |
72-57-1 |
2,7-Naphthalenedisulfonic acid, 3,3'- |
U279 |
63-25-2 |
1-Naphthalenol, methylcarbamate |
U166 |
130-15-4 |
1,4-Naphthoquinone |
U167 |
134-32-7 |
a -Naphthylamine |
U168 |
91-59-8 |
b -Naphthylamine |
U217 |
10102-45-1 |
Nitric acid, thallium (1+) salt |
U169 |
98-95-3 |
Nitrobenzene (I, T) |
U170 |
100-02-7 |
p-Nitrophenol |
U171 |
79-46-9 |
2-Nitropropane (I, T) |
U172 |
924-16-3 |
N-Nitrosodi-n-butylamine |
U173 |
1116-54-7 |
N-Nitrosodiethanolamine |
U174 |
55-18-5 |
N-Nitrosodiethylamine |
U176 |
759-73-9 |
N-Nitroso-N-ethylurea |
U177 |
684-93-5 |
N-Nitroso-N-methylurea |
U178 |
615-53-2 |
N-Nitroso-N-methylurethane |
U179 |
100-75-4 |
N-Nitrosopiperidine |
U180 |
930-55-2 |
N-Nitrosopyrrolidine |
U181 |
99-55-8 |
5-Nitro-o-toluidine |
U193 |
1120-71-4 |
1,2-Oxathiolane, 2,2-dioxide |
U058 |
50-18-0 |
2H-1,3,2-Oxazaphosphorin-2-amine, N,N-bis(2-chloroethyl)tetrahydro-, 2-oxide |
U115 |
75-21-8 |
Oxirane (I, T) |
U126 |
765-34-4 |
Oxiranecarboxyaldehyde |
U041 |
106-89-8 |
Oxirane, (chloromethyl)- |
U182 |
123-63-7 |
Paraldehyde |
U183 |
608-93-5 |
Pentachlorobenzene |
U184 |
76-01-7 |
Pentachloroethane |
U185 |
82-68-8 |
Pentachloronitrobenzene (PCNB) |
See F027 |
87-86-5 |
Pentachlorophenol |
U161 |
108-10-1 |
Pentanol, 4-methyl- |
U186 |
504-60-9 |
1,3-Pentadiene (I) |
U187 |
62-44-2 |
Phenacetin |
U188 |
108-95-2 |
Phenol |
U048 |
95-57-8 |
Phenol, 2-chloro- |
U039 |
59-50-7 |
Phenol, 4-chloro-3-methyl- |
U081 |
120-83-2 |
Phenol, 2,4-dichloro- |
U082 |
87-65-0 |
Phenol, 2,6-dichloro- |
U089 |
56-53-1 |
Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-, (E)- |
U101 |
105-67-9 |
Phenol, 2,4-dimethyl- |
U052 |
1319-77-3 |
Phenol, methyl- |
U132 |
70-30-4 |
Phenol, 2,2'-methylenebis |
U411 |
114-26-1 |
Phenol, 2-(1-methylethoxy)-, methylcarbamate |
U170 |
100-02-7 |
Phenol, 4-nitro- |
See F027 |
87-86-5 |
Phenol, pentachloro- |
See F027 |
58-90-2 |
Phenol, 2,3,4,6-tetrachloro- |
See F027 |
95-95-4 |
Phenol, 2,4,5-trichloro- |
See F027 |
88-06-2 |
Phenol, 2,4,6-trichloro- |
U150 |
148-82-3 |
L-Phenylalanine, 4- |
U145 |
7446-27-7 |
Phosphoric acid, lead (2+) salt (2:3) |
U087 |
3288-58-2 |
Phosphorodithioic acid, O,O-diethyl S-methyl ester |
U189 |
1314-80-3 |
Phosphorus sulfide (R) |
U190 |
85-44-9 |
Phthalic anhydride |
U191 |
109-06-8 |
2-Picoline |
U179 |
100-75-4 |
Piperidine, 1-nitroso- |
U192 |
23950-58-5 |
Pronamide |
U194 |
107-10-8 |
1-Propanamine (I, T) |
U111 |
621-64-7 |
1-Propanamine, N-nitroso-N-propyl- |
U110 |
142-84-7 |
1-Propanamine, N-propyl- (I) |
U066 |
96-12-8 |
Propane, 1,2-dibromo-3-chloro- |
U083 |
78-87-5 |
Propane, 1,2-dichloro- |
U149 |
109-77-3 |
Propanedinitrile |
U171 |
79-46-9 |
Propane, 2-nitro- (I, T) |
U027 |
108-60-1 |
Propane, 2,2'-oxybis |
See F027 |
93-72-1 |
Propanoic acid, 2-(2,4,5-trichlorophenoxy)- |
U193 |
1120-71-4 |
1,3-Propane sultone |
U235 |
126-72-7 |
1-Propanol, 2,3-dibromo-, phosphate (3:1) |
U140 |
78-83-1 |
1-Propanol, 2-methyl- (I, T) |
U002 |
67-64-1 |
2-Propanone (I) |
U007 |
79-06-1 |
2-Propenamide |
U084 |
542-75-6 |
1-Propene, 1,3-dichloro- |
U243 |
1888-71-7 |
1-Propene, 1,1,2,3,3,3-hexachloro- |
U009 |
107-13-1 |
2-Propenenitrile |
U152 |
126-98-7 |
2-Propenenitrile, 2-methyl- (I, T) |
U008 |
79-10-7 |
2-Propenoic acid (I) |
U113 |
140-88-5 |
2-Propenoic acid, ethyl ester (I) |
U118 |
97-63-2 |
2-Propenoic acid, 2-methyl-, ethyl ester |
U162 |
80-62-6 |
2-Propenoic acid, 2-methyl-, methyl ester (I, T) |
U373 |
122-42-9 |
Propham |
U411 |
114-26-1 |
Propoxur |
See F027 |
93-72-1 |
Propionic acid, 2-(2,4,5-trichlorophenoxy)- |
U194 |
107-10-8 |
n-Propylamine (I, T) |
U083 |
78-87-5 |
Propylene dichloride |
U387 |
52888-80-9 |
Prosulfocarb |
U148 |
123-33-1 |
3,6-Pyridazinedione, 1,2-dihydro- |
U196 |
110-86-1 |
Pyridine |
U191 |
109-06-8 |
Pyridine, 2-methyl- |
U237 |
66-75-1 |
2,4-(1H,3H)-Pyrimidinedione, 5- |
U164 |
58-04-2 |
4(1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-thioxo- |
U180 |
930-55-2 |
Pyrrolidine, 1-nitroso- |
U200 |
50-55-5 |
Reserpine |
U201 |
108-46-3 |
Resorcinol |
U202 |
P 81-07-2 |
Saccharin and salts |
U203 |
94-59-7 |
Safrole |
U204 |
7783-00-8 |
Selenious acid |
U204 |
7783-00-8 |
Selenium dioxide |
U205 |
7488-56-4 |
Selenium sulfide |
U205 |
7488-56-4 |
Selenium sulfide SeS2 (R, T) |
U015 |
115-02-6 |
L-Serine, diazoacetate (ester) |
See F027 |
93-72-1 |
Silvex (2,4,5-TP) |
U206 |
18883-66-4 |
Streptozotocin |
U103 |
77-78-1 |
Sulfuric acid, dimethyl ester |
U189 |
1314-80-3 |
Sulfur phosphide (R) |
See F027 |
93-76-5 |
2,4,5-T |
U207 |
95-94-3 |
1,2,4,5-Tetrachlorobenzene |
U208 |
630-20-6 |
1,1,1,2-Tetrachloroethane |
U209 |
79-34-5 |
1,1,2,2-Tetrachloroethane |
U210 |
127-18-4 |
Tetrachloroethylene |
See F027 |
58-90-2 |
2,3,4,6-Tetrachlorophenol |
U213 |
109-99-9 |
Tetrahydrofuran (I) |
U214 |
563-68-8 |
Thallium (I) acetate |
U215 |
6533-73-9 |
Thallium (I) carbonate |
U216 |
7791-12-0 |
Thallium (I) chloride |
U216 |
7791-12-0 |
Thallium chloride TlCl |
U217 |
10102-45-1 |
Thallium (I) nitrate |
U218 |
62-55-5 |
Thioacetamide |
U410 |
59669-26-0 |
Thiodicarb |
U153 |
74-93-1 |
Thiomethanol (I, T) |
U244 |
137-26-8 |
Thioperoxydicarbonic diamide |
U409 |
23564-05-8 |
Thiophanate-methyl |
U219 |
62-56-6 |
Thiourea |
U244 |
137-26-8 |
Thiram |
U220 |
108-88-3 |
Toluene |
U221 |
25376-45-8 |
Toluenediamine |
U223 |
26471-62-5 |
Toluene diisocyanate (R, T) |
U328 |
95-53-4 |
o-Toluidine |
U353 |
106-49-0 |
p-Toluidine |
U222 |
636-21-5 |
o-Toluidine hydrochloride |
U389 |
2303-17-5 |
Triallate |
U011 |
61-82-5 |
1H-1,2,4-Triazol-3-amine |
U227 |
79-00-5 |
1,1,2-Trichloroethane |
U228 |
79-01-6 |
Trichloroethylene |
U121 |
75-69-4 |
Trichloromonofluoromethane |
See F027 |
95-95-4 |
2,4,5-Trichlorophenol |
See F027 |
88-06-2 |
2,4,6-Trichlorophenol |
U404 |
121-44-8 |
Triethylamine |
U234 |
99-35-4 |
1,3,5-Trinitrobenzene (R, T) |
U182 |
123-63-7 |
1,3,5-Trioxane, 2,4,6-trimethyl- |
U235 |
126-72-7 |
Tris(2,3-dibromopropyl) phosphate |
U236 |
72-57-1 |
Trypan blue |
U237 |
66-75-1 |
Uracil mustard |
U176 |
759-73-9 |
Urea, N-ethyl-N-nitroso- |
U177 |
684-93-5 |
Urea, N-methyl-N-nitroso- |
U043 |
75-01-4 |
Vinyl chloride |
U248 |
P 81-81-2 |
Warfarin, and salts, when present at concentrations of 0.3 percent or less |
U239 |
1330-20-7 |
Xylene (I) |
U200 |
50-55-5 |
Yohimban-16-carboxylic acid, 11,17-dimethoxy-18- |
U249 |
1314-84-7 |
Zinc phosphide Zn3P2, when present at concentrations of 10 percent or less |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.135 | Wood Preserving Wastes |
a) | Wastes from wood preserving processes at plants that do not resume or initiate use of chlorophenolic preservatives will not meet the listing definition of F032 once the generator has met all of the requirements of subsections (b) and (c) of this Section. These wastes may, however, continue to meet another hazardous waste listing description or may exhibit one or more of the hazardous waste characteristics. |
b) | Generators |
1) | Generators |
A) | Prepare and follow an equipment cleaning plan and clean equipment in accordance with this Section; or |
B) | Prepare and follow an equipment replacement plan and replace equipment in accordance with this Section; or |
C) | Document cleaning and replacement in accordance with this Section, carried out after termination of use of chlorophenolic preservatives. |
2) | Cleaning requirements. |
A) | |
i) | The equipment to be cleaned |
ii) | How the equipment will be cleaned |
iii) | The solvent to be used in cleaning |
iv) | How solvent rinses will be tested |
v) | How cleaning residues will be disposed of. |
B) | Equipment must be cleaned as follows: |
i) | Remove all visible residues from process equipment |
ii) | Rinse process equipment with an appropriate solvent until dioxins and dibenzofurans are not detected in the final solvent rinse. |
C) | Analytical requirements. |
i) | Rinses must be tested in accordance with SW-846, Method 8290, incorporated by reference in 35 Ill. Adm. Code 720.111. |
ii) | “Not detected” means at or below the lower method calibration limit (MCL) in Method 8290, Table 1. |
D) | The generator must manage all residues from the cleaning process as F032 waste. |
3) | Replacement requirements. |
A) | Prepare and sign a written equipment replacement plan that describes the following: |
i) | The equipment to be replaced; |
ii) | How the equipment will be replaced; and |
iii) | How the equipment will be disposed of. |
B) | The generator must manage the discarded equipment as F032 waste. |
4) | Documentation requirements. Document that previous equipment cleaning and replacement was performed in accordance with this Section and ocurred after cessation of use of chlorophenolic preservatives. |
c) | The generator |
1) | The name and address of the facility; |
2) | Formulations previously used and the date on which their use ceased in each process at the plant; |
3) | Formulations currently used in each process at the plant; |
4) | The equipment cleaning or replacement plan; |
5) | The name and address of any persons who conducted the cleaning and replacement; |
6) | The dates on which cleaning and replacement were accomplished; |
7) | The dates of sampling and testing; |
8) | A description of the sample handling and preparation techniques used for extraction, containerization, preservation and chain-of-custody of the samples; |
9) | A description of the tests performed, the date the tests were performed and the results of the tests; |
10) | The name and model numbers of the |
11) | QA/QC documentation; and |
12) | The following statement signed by the generator or the generator’s authorized representative: |
I certify under penalty of law that all process equipment required to be cleaned or replaced under 35 Ill. Adm. Code 721.135 was cleaned or replaced as represented in the equipment cleaning and replacement plan and accompanying documentation. I am aware that there are significant penalties for providing false information, including the possibility of fine or imprisonment.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.138 | Comparable or Syngas Fuel Exclusion |
Wastes that meet the following comparable or syngas fuel requirements are not solid wastes:
a) | Comparable fuel specifications. |
1) | Physical specifications. |
A) | Heating value. The heating value must exceed 5,000 Btu/lb (11,500 J/g). |
B) | Viscosity. The viscosity must not exceed 50 cs, |
2) | Constituent specifications. For the compounds listed, the constituent specification levels and minimum required detection limits (where non-detect is the constituent specification) are set forth in the table at subsection (d) of this Section. |
b) | Synthesis gas fuel specification. Synthesis gas fuel (i.e., syngas fuel) that is generated from hazardous waste must fulfill the following requirements: |
1) | It must have a minimum Btu value of 100 Btu/Scf; |
2) | It must contain less than 1 ppmv of total halogen; |
3) | It must contain less than 300 ppmv of total nitrogen other than diatomic nitrogen (N2); |
4) | It must contain less than 200 ppmv of hydrogen sulfide; and |
5) | It must contain less than 1 ppmv of each hazardous constituent in the target list of |
c) | Implementation. Waste that meets the comparable or syngas fuel specifications provided by subsection (a) or (b) of this Section (these constituent levels must be achieved by the comparable fuel when generated, or as a result of treatment or blending, as provided in subsection (c)(3) or (c)(4) of this Section) is excluded from the definition of solid waste provided that the following requirements are met: |
1) | Notices. For purposes of this Section, the person claiming and qualifying for the exclusion is called the comparable or syngas fuel generator and the person burning the comparable or syngas fuel is called the comparable or syngas burner. The person that generates the comparable fuel or syngas fuel must claim and certify to the exclusion. |
A) | Notice to the Agency. |
i) | The generator must submit a one-time notice to the Agency, certifying compliance with the conditions of the exclusion and providing documentation, as required by subsection (c)(1)(A)(iii) of this Section; |
ii) | If the generator is a company that generates comparable or syngas fuel at more than one facility, the generator must specify at which sites the comparable or syngas fuel will be generated; |
iii) | A comparable or syngas fuel generator’s notification to the Agency must contain the items listed in subsection (c)(1)(C) of this Section. |
B) | Public notice. Prior to burning an excluded comparable or syngas fuel, the burner must publish in a major newspaper of general circulation, local to the site where the fuel will be burned, a notice entitled “Notification of Burning a Comparable or Syngas Fuel Excluded Under the Resource Conservation and Recovery Act” containing the following information: |
i) | The name, address, and USEPA identification number of the generating facility; |
ii) | The name and address of the units that will burn the comparable or syngas fuel; |
iii) | A brief, general description of the manufacturing, treatment, or other process generating the comparable or syngas fuel; |
iv) | An estimate of the average and maximum monthly and annual quantity of the waste claimed to be excluded; and |
v) | The name and mailing address of the Agency office to which the claim was submitted. |
C) | Required content of comparable or syngas notification to the Agency. |
i) | The name, address, and USEPA identification number of the person or facility claiming the exclusion; |
ii) | The applicable USEPA hazardous waste codes for the hazardous waste; |
iii) | The name and address of the units that meet the requirements of subsection (c)(2) of this Section that will burn the comparable or syngas fuel; and |
iv) | The following statement, signed and submitted by the person claiming the exclusion or its authorized representative: |
Under penalty of criminal and civil prosecution for making or submitting false statements, representations, or omissions, I certify that the requirements of 35 Ill. Adm. Code 721.138 have been met for all waste identified in this notification. Copies of the records and information required by 35 Ill. Adm. Code 721.138(c)(10) are available at the comparable or syngas fuel generator’s facility. Based on my inquiry of the individuals immediately responsible for obtaining the information, the information is, to the best of my knowledge and belief, true, accurate, and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment for knowing violations.
BOARD NOTE: Subsections (c)(1)(C)(i) through (c)(1)(C)(iv) are derived from 40 CFR 261.138(c)(1)(i)(C)(1) and (c)(1)(i)(C)(4), which the Board has codified here to comport with Illinois Administrative Code format requirements.
2) | Burning. The comparable or syngas fuel exclusion for fuels that meet the requirements of subsections (a) or (b) and (c)(1) of this Section applies only if the fuel is burned in the following units that also must be subject to federal, State, and local air emission requirements, including all applicable federal Clean Air Act (CAA) maximum achievable control technology (MACT) requirements: |
A) | Industrial furnaces, as defined in 35 Ill. Adm. Code 720.110; |
B) | Boilers, as defined in 35 Ill. Adm. Code 720.110, that are further defined as follows: |
i) | Industrial boilers located on the site of a facility engaged in a manufacturing process where substances are transformed into new products, including the component parts of products, by mechanical or chemical processes; or |
ii) | Utility boilers used to produce electric power, steam, heated or cooled air, or other gases or fluids for sale; |
C) | Hazardous waste incinerators subject to regulation under Subpart O of 35 Ill. Adm. Code 724 |
D) | Gas turbines used to produce electric power, steam, heated or cooled air, or other gases or fluids for sale. |
3) | Blending to meet the viscosity specification. A hazardous waste blended to meet the viscosity specification must fulfill the following requirements: |
A) | As generated and prior to any blending, manipulation, or processing, the waste must meet the constituent and heating value specifications of subsections (a)(1)(A) and (a)(2) of this Section; |
B) | The waste must be blended at a facility that is subject to the applicable requirements of 35 Ill. Adm. Code 724 and 725 or 35 Ill. Adm. Code 722.134; and |
C) | The waste must not violate the dilution prohibition of subsection (c)(6) of this Section. |
4) | Treatment to meet the comparable fuel exclusion specifications. |
A) | A hazardous waste may be treated to meet the exclusion specifications of subsections (a)(1) and (a)(2) of this Section provided the treatment fulfills the following requirements: |
i) | The treatment destroys or removes the constituent listed in the specification or raises the heating value by removing or destroying hazardous constituents or materials; |
ii) | The treatment is performed at a facility that is subject to the applicable requirements of 35 Ill. Adm. Code 724 and 725 or 35 Ill. Adm. Code 722.134; and |
iii) | The treatment does not violate the dilution prohibition of subsection (c)(6) of this Section. |
B) | Residuals resulting from the treatment of a hazardous waste listed in Subpart D of this Part to generate a comparable fuel remain a hazardous waste. |
5) | Generation of a syngas fuel. |
A) | A syngas fuel can be generated from the processing of hazardous wastes to meet the exclusion specifications of subsection (b) of this Section provided the processing fulfills the following requirements: |
i) | The processing destroys or removes the constituent listed in the specification or raises the heating value by removing or destroying constituents or materials; |
ii) | The processing is performed at a facility that is subject to the applicable requirements of 35 Ill. Adm. Code 724 and 725 or 35 Ill. Adm. Code 722.134 or is an exempt recycling unit pursuant to Section 721.106(c); and |
iii) | The processing does not violate the dilution prohibition of subsection (c)(6) of this Section. |
B) | Residuals resulting from the treatment of a hazardous waste listed in Subpart D of this Part to generate a syngas fuel remain a hazardous waste. |
6) | Dilution prohibition for comparable and syngas fuels. No generator, transporter, handler, or owner or operator of a treatment, storage, or disposal facility must in any way dilute a hazardous waste to meet the exclusion specifications of subsection (a)(1)(A), (a)(2), or (b) of this Section. |
7) | Waste analysis plans. The generator of a comparable or syngas fuel must develop and follow a written waste analysis plan that describes the procedures for sampling and analysis of the hazardous waste to be excluded. The waste analysis plan must be developed in accordance with the applicable sections of the “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods” (SW-846). The plan must be followed and retained at the facility excluding the waste. |
A) | At a minimum, the plan must specify the following: |
i) | The parameters for which each hazardous waste will be analyzed and the rationale for the selection of those parameters; |
ii) | The test methods that will be used to test for these parameters; |
iii) | The sampling method that will be used to obtain a representative sample of the waste to be analyzed; |
iv) | The frequency with which the initial analysis of the waste will be reviewed or repeated to ensure that the analysis is accurate and up to date; and |
v) | If process knowledge is used in the waste determination, any information prepared by the generator in making such determination. |
B) | The waste analysis plan must also contain records of the following: |
i) | The dates and times waste samples were obtained, and the dates the samples were analyzed; |
ii) | The names and qualifications of the persons who obtained the samples; |
iii) | A description of the temporal and spatial locations of the samples; |
iv) | The name and address of the laboratory facility at which analyses of the samples were performed; |
v) | A description of the analytical methods used, including any clean-up and sample preparation methods; |
vi) | All quantitation limits achieved and all other quality control results for the analysis (including method blanks, duplicate analyses, matrix spikes, etc.), laboratory quality assurance data, and description of any deviations from analytical methods written in the plan or from any other activity written in the plan that occurred; |
vii) | All laboratory results demonstrating that the exclusion specifications have been met for the waste; and |
viii) | All laboratory documentation that supports the analytical results, unless a contract between the claimant and the laboratory provides for the documentation to be maintained by the laboratory for the period specified in subsection (c)(11) of this Section and also provides for the availability of the documentation to the claimant upon request. |
C) | Syngas fuel generators must submit for approval, prior to performing sampling, analysis, or any management of a syngas fuel as an excluded waste, a waste analysis plan containing the elements of subsection (c)(7)(A) of this Section to the Agency. The approval of waste analysis plans must be stated in writing and received by the facility prior to sampling and analysis to demonstrate the exclusion of a syngas. The approval of the waste analysis plan may contain such provisions and conditions as the regulatory authority deems appropriate. |
8) | Comparable fuel sampling and analysis. |
A) | General. For each waste for which an exclusion is claimed, the generator of the hazardous waste must test for all the constituents on Appendix H of this Part, except those that the generator determines, based on testing or knowledge, should not be present in the waste. The generator is required to document the basis of each determination that a constituent should not be present. The generator may not determine that any of the following categories of constituents should not be present: |
i) | A constituent that triggered the toxicity characteristic for the waste constituents that were the basis of the listing of the waste stream, or constituents for which there is a treatment standard for the waste code in 35 Ill. Adm. Code 728.140; |
ii) | A constituent detected in previous analysis of the waste; |
iii) | Constituents introduced into the process that generates the waste; or |
iv) | Constituents that are byproducts or side reactions to the process that generates the waste. |
B) | For each waste for which the exclusion is claimed where the generator of the comparable or syngas fuel is not the original generator of the hazardous waste, the generator of the comparable or syngas fuel may not use process knowledge pursuant to subsection (c)(8)(A) of this Section and must test to determine that all of the constituent specifications of subsections (a)(2) and (b) of this Section have been met. |
C) | The comparable or syngas fuel generator may use any reliable analytical method to demonstrate that no constituent of concern is present at concentrations above the specification levels. It is the responsibility of the generator to ensure that the sampling and analysis are unbiased, precise, and representative of the waste. For the waste to be eligible for exclusion, a generator must demonstrate the following: |
i) | That each constituent of concern is not present in the waste above the specification level at the 95 percent upper confidence limit around the mean; and |
ii) | That the analysis could have detected the presence of the constituent at or below the specification level at the 95 percent upper confidence limit around the mean. |
D) | Nothing in this subsection (c)(8) preempts, overrides, or otherwise negates the provision in 35 Ill. Adm. Code 722.111 that requires any person |
E) | In an enforcement action, the burden of proof to establish conformance with the exclusion specification must be on the generator claiming the exclusion. |
F) | The generator must conduct sampling and analysis in accordance with its waste analysis plan developed under subsection (c)(7) of this Section. |
G) | Syngas fuel and comparable fuel that has not been blended in order to meet the kinematic viscosity specifications must be analyzed as generated. |
H) | If a comparable fuel is blended in order to meet the kinematic viscosity specifications, the generator must undertake the following actions: |
i) | Analyze the fuel as generated to ensure that it meets the constituent and heating value specifications; and |
ii) | After blending, analyze the fuel again to ensure that the blended fuel continues to meet all comparable or syngas fuel specifications. |
I) | Excluded comparable or syngas fuel must be retested, at a minimum, annually and must be retested after a process change that could change the chemical or physical properties of the waste. |
Note to subsection (c)(8): Any claim under this Section must be valid and accurate for all hazardous constituents; a determination not to test for a hazardous constituent will not shield a generator from liability should that constituent later be found in the waste above the exclusion specifications.
9) | Speculative accumulation. Any persons handling a comparable or syngas fuel are subject to the speculative accumulation test under Section 721.102(c)(4). |
10) | Records. The generator must maintain records of the following information on-site: |
A) | All information required to be submitted to the implementing authority as part of the notification of the claim: |
i) | The owner or operator name, address, and RCRA facility USEPA identification number of the person claiming the exclusion; |
ii) | The applicable USEPA hazardous waste codes for each hazardous waste excluded as a fuel; and |
iii) | The certification signed by the person claiming the exclusion or his authorized representative; |
B) | A brief description of the process that generated the hazardous waste and process that generated the excluded fuel, if not the same; |
C) | An estimate of the average and maximum monthly and annual quantities of each waste claimed to be excluded; |
D) | Documentation for any claim that a constituent is not present in the hazardous waste, as required under subsection (c)(8)(A) of this Section; |
E) | The results of all analyses and all detection limits achieved, as required under subsection (c)(8) of this Section; |
F) | If the excluded waste was generated through treatment or blending, documentation, as required under subsection (c)(3) or (c)(4) of this Section; |
G) | If the waste is to be shipped off-site, a certification from the burner, as required under subsection (c)(12) of this Section; |
H) | A waste analysis plan and the results of the sampling and analysis that include the following: |
i) | The dates and times waste samples were obtained, and the dates the samples were analyzed; |
ii) | The names and qualifications of the persons that obtained the samples; |
iii) | A description of the temporal and spatial locations of the samples; |
iv) | The name and address of the laboratory facility at which analyses of the samples were performed; |
v) | A description of the analytical methods used, including any clean-up and sample preparation methods; |
vi) | All quantitation limits achieved and all other quality control results for the analysis (including method blanks, duplicate analyses, matrix spikes, etc.), laboratory quality assurance data, and description of any deviations from analytical methods written in the plan or from any other activity written in the plan that occurred; |
vii) | All laboratory analytical results demonstrating that the exclusion specifications have been met for the waste; and |
viii) | All laboratory documentation that supports the analytical results, unless a contract between the claimant and the laboratory provides for the documentation to be maintained by the laboratory for the period specified in subsection (c)(11) of this Section and also provides for the availability of the documentation to the claimant upon request; and |
I) | If the generator ships comparable or syngas fuel off-site for burning, the generator must retain for each shipment the following information on-site: |
i) | The name and address of the facility receiving the comparable or syngas fuel for burning; |
ii) | The quantity of comparable or syngas fuel shipped and delivered; |
iii) | The date of shipment or delivery; |
iv) | A cross-reference to the record of comparable or syngas fuel analysis or other information used to make the determination that the comparable or syngas fuel meets the specifications, as required under subsection (c)(8) of this Section; and |
v) | A one-time certification by the burner, as required under subsection (c)(12) of this Section. |
11) | Records retention. Records must be maintained for the period of three years. A generator must maintain a current waste analysis plan during that |
12) | Burner certification. Prior to submitting a notification to the Agency, a comparable or syngas fuel generator that intends to ship its fuel off-site for burning must obtain a one-time written, signed statement from the burner that includes the following: |
A) | A certification that the comparable or syngas fuel will only be burned in an industrial furnace or boiler, utility boiler, or hazardous waste incinerator, as required under subsection (c)(2) of this Section; |
B) | Identification of the name and address of the units that will burn the comparable or syngas fuel; and |
C) | A certification that the state in which the burner is located is authorized to exclude wastes as comparable or syngas fuel under the provisions of this Section. |
13) | Ineligible waste codes. Wastes that are listed because of presence of dioxins or furans, as set out in Appendix G of this Part, are not eligible for this exclusion, and any fuel produced from or otherwise containing these wastes remains a hazardous waste subject to full RCRA hazardous waste management requirements. |
d) | Table Y of this Part sets forth the table of detection and detection limit values for comparable fuel specification. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.Appendix A | |
Representative Sampling Methods | |
See Appendix I to 40 CFR 261
The methods and equipment used for sampling waste materials will vary with the form and consistency of the waste materials to be sampled. Samples collected using the sampling protocols listed below, for sampling waste with properties similar to the indicated materials, are considered by USEPA to be representative of the waste.
Extremely viscous liquid: ASTM Standard D140–70, Standard Practice for Sampling Bituminous Materials, incorporated by reference in 35 Ill. Adm. Code 720.111.
Crushed or powdered material: ASTM Standard D346–75, Standard Practice for Collection and Preparation of Coke Samples for Laboratory Analysis, incorporated by reference in 35 Ill. Adm. Code 720.111.
Soil or rock-like material: ASTM Standard D420–69, Guide to Site Characterization for Engineering, Design, incorporated by reference in 35 Ill. Adm. Code 720.111.
Soillike material: ASTM Standard D1452–65, Standard Practice for Soil Investigation and Sampling by Auger Borings, incorporated by reference in 35 Ill. Adm. Code 720.111.
Fly Ash-like material: ASTM Standard D2234–76, Standard Practice for Collection of a Gross Sample of Coal, incorporated by reference in 35 Ill. Adm. Code 720.111.
Containerized liquid wastes: “COLIWASA” described in “Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods,” SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111.
BOARD NOTE: This method is also described in “Samplers and Sampling Procedures for Hazardous Waste Streams,” EPA 600/2–80–018, January 1980.
Liquid waste in pits, ponds, lagoons, and similar reservoirs: “Pond Sampler,” described in “Test Methods for the Evaluation of Solid Waste, Physical/Chemical Methods,” SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111.
BOARD NOTE: This manual also contains additional information on application of these protocols. This method is also described in “Samplers and Sampling Procedures for Hazardous Waste Streams,” EPA 600/2–80–018, January 1980, incorporated by reference in 35 Ill. Adm. Code 720.111..
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.Appendix B | |
Method 1311 Toxicity Characteristic Leaching Procedure (TCLP) | |
NOTE: The TCLP (Method 1311) is published in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”, U.S. EPA USEPA Publication SW-846, as incorporated by reference in 35 Ill. Adm. Code 720.111.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.Appendix C | |
Chemical Analysis Test Methods | |
NOTE: Appropriate analytical procedures to determine whether a sample contains a given toxic constituent are specified in Chapter Two, “Choosing the Correct Procedure,”, found in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”, U.S. EPA USEPA Publication SW-846, as incorporated by reference in 35 Ill. Adm. Code 720.111. Prior to final sampling and analysis method selection, the individual should consult the specific section or method described in SW-846 for additional guidance on which of the approved methods should be employed for a specific sample analysis situation.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.Appendix G | |
Basis for Listing Hazardous Wastes | |
USEPA hazardous waste No. |
Hazardous constituents for which listed |
F001 |
Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, carbon tetrachloride, chlorinated fluorocarbons. |
F002 |
Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, 1,1,2-trichlorethane, chlorobenzene, 1,1,2-trichloro-1,2,2-trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane. |
F003 |
N.A. |
F004 |
Cresols and cresylic acid, nitrobenzene. |
F005 |
Toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, 2-ethoxyethanol, benzene, 2-nitropropane. |
F006 |
Cadmium, hexavalent chromium, nickel, cyanide (complexed). |
F007 |
Cyanide (salts). |
F008 |
Cyanide (salts). |
F009 |
Cyanide (salts). |
F010 |
Cyanide (salts). |
F011 |
Cyanide (salts). |
F012 |
Cyanide (complexed). |
F019 |
Hexavalent chromium, cyanide (complexed). |
F020 |
Tetra- and pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans; tri- and tetrachlorophenols and their clorophenoxy derivative acids, esters, ethers, amines, and other salts. |
F021 |
Penta- and hexachlorodibenzo-p-dioxins; penta- and hexachlorodibenzofurans; pentachlorophenol and its derivatives. |
F022 |
Tetra-, penta- and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans. |
F023 |
Tetra- and pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans; tri- and tetra- chlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines, and other salts. |
F024 |
Chloromethane, dichloromethane, trichloromethane, carbon tetrachloride, chloroethylene, 1,1-dichloroethane, 1,2-dichloroethane, trans-1,2-dichloroethylene, 1,1-dichloroethylene, 1,1,1-trichloroethane, 1,1,2-trichloroethane, trichloroethylene, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane, tetrachloroethylene, pentachloroethane, hexachloroethane, allyl chloride (3-chloropropene), dichloropropane, dichloropropene, 2-chloro-1,3-butadiene, hexachloro-1,3-butadiene, hexachlorochylopentadiene, hexachlorocylohexane, benzene, chlorobenzene, dichlorobenzenes, 1,2,4-trichlorobenzene, tetrachlorobenzenes, pentachlorobenzene, hexachlorobenzene, toluene, naphthalene. |
F025 |
Chloromethane, dicloromethane, trichloromethane; carbon tetrachloride; chloroethylene; 1,1-dichloroethane; 1,2-dichloroethane; trans-1,2-dichloroethylene; 1,1-dichloroethylene; 1,1,1-trichloroethane; 1,1,2-trichloroethane; trichloroethylene; 1,1,1,2-tetrachloroethane; 1,1,2,2-tetrachloroethane; tetrachloroethylene; pentachloroethane; hexachloroethane; allyl chloride (3-chloropropene); dichloropropane; dichloropropene; 2-chloro-1,3-butadiene; hexachloro-1,3-butadiene; hexachlorocyclopentadiene; benzene; chlorobenzene; dichlorobenzene; 1,2,4-trichlorobenzene; tetrachlorobenzene; pentachlorobenzene; hexachlorobenzene; toluene; naphthalene. |
F026 |
Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans. |
F027 |
Tetra-, penta, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans; tri-, tetra-, and pentachlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines, and other salts. |
F028 |
Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans; tri-, tetra-, and pentachlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines, and other salts. |
F032 |
Benz(a)anthracene; benzo(a)pyrene; dibenz(a,h)anthracene; indeno(1,2,3-cd)pyrene; pentachlorophenol; arsenic; chromium; tetra-, penta-, hexa-, and heptachlorordibenzo-p-dioxins; tetra-, penta-, hexa-, and heptachlorodibenzofurans. |
F034 |
Benz(a)anthracene, benzo(k)fluoranthene, benzo(a)pyrene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene, naphthalene, arsenic, chromium. |
F035 |
Arsenic, chromium, lead. |
F037 |
Benzene, benzo(a)pyrene, chrysene, lead, chromium. |
F038 |
Benzene, benzo(a)pyrene, chrysene, lead, chromium. |
F039 |
All constituents for which treatment standards are specified for multi-source leachate (wastewaters and non-wastewaters) under Table B to 35 Ill. Adm. Code 728 |
K001 |
Pentachlorophenol, phenol, 2-chlorophenol, p-chloro-m-cresol, 2,4-dimethylphenol, 2,4- dinitrophenol, trichlorophenols, tetrachlorophenols, 2,4- dinitrophenol, creosote, chrysene, naphthalene, fluoranthene, benzo(b)fluoranthene, benzo(a)pyrene, indeno(1,2,3-cd)pyrene, benz(a) anthracene, dibenz(a)anthracene, acenaphthalene. |
K002 |
Hexavalent chromium, lead. |
K003 |
Hexavalent chromium, lead. |
K004 |
Hexavalent chromium. |
K005 |
Hexavalent chromium, lead. |
K006 |
Hexavalent chromium. |
K007 |
Cyanide (complexed), hexavalent chromium. |
K008 |
Hexavalent chromium. |
K009 |
Chloroform, formaldehyde, methylene chloride, methyl chloride, paraldehyde, formic acid. |
K010 |
Chloroform, formaldehyde, methylene chloride, methyl chloride, paraldehyde, formic acid, chloroacetaldehyde. |
K011 |
Acrylonitrile, acetonitrile, hydrocyanic acid. |
K013 |
Hydrocyanic acid, acrylonitrile, acetonitrile. |
K014 |
Acetonitrile, acrylamide. |
K015 |
Benzyl chloride, chlorobenzene, toluene, benzotrichloride. |
K016 |
Hexachlorobenzene, hexachlorobutadiene, carbon tetrachloride, hexachloroethane, perchloroethylene. |
K017 |
Epichlorohydrin, chloroethers |
K018 |
1,2-dichloroethane, trichloroethylene, hexachlorobutadiene, hexachlorobenzene. |
K019 |
Ethylene dichloride, 1,1,1-trichloroethane, 1,1,2-trichloroethane, tetrachloroethanes (1,1,2,2-tetrachloroethane and 1,1,1,2-tetrachloroethane), trichloroethylene, tetrachloroethylene, carbon tetrachloride, chloroform, vinyl chloride, vinylidene chloride. |
K020 |
Ethylene dichloride, 1,1,1-trichloroethane, 1,1,2-trichloroethane, tetrachloroethanes (1,1,2,2-tetrachloroethane and 1,1,1,2-tetrachloroethane), trichloroethylene, tetrachloroethylene, carbon tetrachloride, chloroform, vinyl chloride, vinylidene chloride. |
K021 |
Antimony, carbon tetrachloride, chloroform. |
K022 |
Phenol, tars (polycyclic aromatic hydrocarbons). |
K023 |
Phthalic anhydride, maleic anhydride. |
K024 |
Phthalic anhydride, 1,4-naphthoguinone. |
K025 |
Meta-dinitrobenzene, 2,4-dinitrotoluene. |
K026 |
Paraldehyde, pyridines, 2-picoline. |
K027 |
Toluene diisocyanate, toluene-2,4-diamine. |
K028 |
1,1,1-trichloroethane, vinyl chloride. |
K029 |
1,2-dichloroethane, 1,1,1-trichloroethane, vinyl chloride, vinylidene chloride, chloroform. |
K030 |
Hexachlorobenzene, hexachlorobutadiene, hexachloroethane, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane, ethylene dichloride. |
K031 |
Arsenic. |
K032 |
Hexachlorocyclopentadiene. |
K033 |
Hexachlorocyclopentadiene. |
K034 |
Hexachlorocyclopentadiene. |
K035 |
Creosote, chrysene, naphthalene, fluoranthene, benzo(b) fluoranthene, benzo(a)-pyrene, indeno(1,2,3-cd) pyrene, benzo(a)anthracene, dibenzo(a)anthracene, acenaphthalene. |
K036 |
Toluene, phosphorodithioic and phosphorothioic acid esters. |
K037 |
Toluene, phosphorodithioic and phosphorothioic acid esters. |
K038 |
Phorate, formaldehyde, phosphorodithioic and phosphorothioic acid esters. |
K039 |
Phosphorodithioic and phosphorothioic acid esters. |
K040 |
Phorate, formaldehyde, phosphorodithioic and phosphorothioic acid esters. |
K041 |
Toxaphene. |
K042 |
Hexachlorobenzene, ortho-dichlorobenzene. |
K043 |
2,4-dichlorophenol, 2,6-dichlorophenol, 2,4,6-trichlorophenol. |
K044 |
N.A. |
K045 |
N.A. |
K046 |
Lead. |
K047 |
N.A. |
K048 |
Hexavalent chromium, lead. |
K049 |
Hexavalent chromium, lead. |
K050 |
Hexavalent chromium. |
K051 |
Hexavalent chromium, lead. |
K052 |
Lead. |
K060 |
Cyanide, naphthalene, phenolic compounds, arsenic. |
K061 |
Hexavalent chromium, lead, cadmium. |
K062 |
Hexavalent chromium, lead. |
K064 |
Lead, cadmium. |
K065 |
Lead, cadmium. |
K066 |
Lead, cadmium. |
K069 |
Hexavalent chromium, lead, cadmium. |
K071 |
Mercury. |
K073 |
Chloroform, carbon tetrachloride, hexachloroethane, trichloroethane, tetrachloroethylene, dichloroethylene, 1,1,2,2-tetrachloroethane. |
K083 |
Aniline, diphenylamine, nitrobenzene, phenylenediamine. |
K084 |
Arsenic. |
K085 |
Benzene, dichlorobenzenes, trichlorobenzenes, tetrachlorobenzenes, pentachlorobenzene, hexachlorobenzene, benzyl chloride. |
K086 |
Lead, hexavalent chromium. |
K087 |
Phenol, naphthalene. |
K088 |
Cyanide (complexes). |
K090 |
Chromium. |
K091 |
Chromium. |
K093 |
Phthalic anhydride, maleic anhydride. |
K094 |
Phthalic anhydride. |
K095 |
1,1,2-trichloroethane, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane. |
K096 |
1,2-dichloroethane, 1,1,1-trichloroethane, 1,1,2-trichloroethane. |
K097 |
Chlordane, heptachlor. |
K098 |
Toxaphene. |
K099 |
2,4-dichlorophenol, 2,4,6-trichlorophenol. |
K100 |
Hexavalent chromium, lead, cadmium. |
K101 |
Arsenic. |
K102 |
Arsenic. |
K103 |
Aniline, nitrobenzene, phenylenediamine. |
K104 |
Aniline, benzene, diphenylamine, nitrobenzene, phynylenediamine. |
K105 |
Benzene, monochlorobenzene, dichlorobenzenes, 2,4,6-trichlorophenol. |
K106 |
Mercury. |
K111 |
2,4-Dinitrotoluene. |
K112 |
2,4-Toluenediamine, o-toluidine, p-toluidine, aniline. |
K113 |
2,4-Toluenediamine, o-toluidine, p-toluidine, aniline. |
K114 |
2,4-Toluenediamine, o-toluidine, p-toluidine. |
K115 |
2,4-Toluenediamine. |
K116 |
Carbon tetrachloride, tetrachloroethylene, chloroform, phosgene. |
K117 |
Ethylene dibromide. |
K118 |
Ethylene dibromide. |
K123 |
Ethylene thiourea. |
K124 |
Ethylene thiourea. |
K125 |
Ethylene thiourea. |
K126 |
Ethylene thiourea. |
K131 |
Dimethyl sulfate, methyl bromide. |
K132 |
Methyl bromide. |
K136 |
Ethylene dibromide. |
K141 |
Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene. |
K142 |
Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene. |
K143 |
Benzene, benz(a)anthracene, benzo(b)fluoranthene, benzo(k)fluoranthene. |
K144 |
Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene. |
K145 |
Benzene, benz(a)anthracene, benzo(a)pyrene, dibenz(a,h)anthracene, naphthalene. |
K147 |
Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene. |
K148 |
Benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene. |
K149 |
Benzotrichloride, benzyl chloride, chloroform, chloromethane, chlorobenzene, 1,4-dichlorobenzene, hexachlorobenzene, pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, toluene. |
K150 |
Carbon tetrachloride, chloroform, chloromethane, 1,4-dichlorobenzene, hexachlorobenzene, pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, 1,1,2,2-tetrachloroethane, tetrachloroethylene, 1,2,4-trichlorobenzene. |
K151 |
Benzene, carbon tetrachloride, chloroform, hexachlorobenzene, pentachlorobenzene, toluene, 1,2,4,5-tetrachlorobenzene, tetrachloroethylene. |
K156 |
Benomyl, carbaryl, carbendazim, carbofuran, carbosulfan, formaldehyde, methylene chloride, triethylamine. |
K157 |
Carbon tetrachloride, formaldehyde, methyl chloride, methylene chloride, pyridine, triethylamine. |
K158 |
Benomyl, carbendazim, carbofuran, carbosulfan, chloroform, methylene chloride. |
K159 |
Benzene, butylate, EPTC, molinate, pebulate, vernolate. |
K161 |
Antimony, arsenic, metam-sodium, ziram. |
K169 |
Benzene. |
K170 |
Benzo(a)pyrene, dibenz(a,h)anthracene, benzo (a) anthracene, benzo(b)fluoranthene, benzo(k)fluoranthene, 3-methylcholanthrene, 7,12-dimethylbenz(a)anthracene. |
K171 |
Benzene, arsenic. |
K172 |
Benzene, arsenic. |
K174 |
1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD), 1,2,3,4,6,7,8-heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF), 1,2,3,4,7,8,9-heptachlorodibenzofuran (1,2,3,6,7,8,9-HpCDF), all hexachlorodibenzo-p-dioxins (HxCDDs), all hexachlorodibenzofurans (HxCDFs), all pentachlorodibenzo-p-dioxins (PeCDDs), 1,2,3,4,6,7,8,9-octachlorodibenzo-p-dioxin (OCDD), 1,2,3,4,6,7,8,9- octachlorodibenzofuran (OCDF), all pentachlorodibenzofurans (PeCDFs), all tetrachlorodibenzo-p-dioxins (TCDDs), all tetrachlorodibenzofurans (TCDFs). |
K175 |
Mercury. |
K176 |
Arsenic, lead. |
K177 |
Antimony. |
K178 |
Thallium. |
N.A.--Waste is hazardous because it fails the test for the characteristic of ignitability, corrosivity, or reactivity.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.Appendix I | |
Wastes Excluded by Administrative Action | |
Table A | Wastes Excluded by |
Facility Address |
Waste Description |
(None excluded from an Illinois source at this time) |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.Appendix I | |
Wastes Excluded by Administrative Action | |
Table B | Wastes Excluded by USEPA under 40 CFR 260.20 and 260.22 from Specific Sources |
Facility Address |
Waste Description |
Amoco Oil Company Wood River, Illinois |
150 million gallons of DAF float from petroleum refining contained in four surge ponds after treatment with the Chemfix stabilization process. This waste contains USEPA hazardous waste number K048. This exclusion applies to the 150 million gallons of waste after chemical stabilization as long as the mixing ratios of the reagent with the waste are monitored continuously and do not vary outside of the limits presented in the demonstration samples and one grab sample is taken each hour from each treatment unit, composited, and |
|
|
Conversion Systems, Inc. Horsham, Pennsylvania (Sterling, Illinois operations) |
Chemically stabilized electric arc furnace dust (CSEAFD) that is generated by Conversion Systems, Inc. (CSI) (using the Super DetoxÔ treatment process, as modified by CSI to treat electric arc furnace dust (EAFD) (USEPA hazardous waste no. K061)), at the following site and which is disposed of in a RCRA Subtitle D municipal solid waste landfill (MSWLF): Northwestern Steel, Sterling, Illinois.
CSI must implement a testing program for each site that meets the following conditions:
1. Verification testing requirements: Sample collection and analyses, including quality control procedures, must be performed according to SW-846 methodologies, incorporated by reference in 35 Ill. Adm. Code 720.111.
A. Initial verification testing: During the first 20 days of full-scale operation of a newly-constructed Super DetoxÔ treatment facility, CSI
B. Addition of new Super DetoxÔ treatment facilities to the exclusion:
Option 1: If USEPA approves additional facilities, CSI may petition the Board for identical-in substance amendment of this exclusion pursuant to Section 22.4 for the Act and 35 Ill. Adm. Code 102 and 720.120(a), or
Option 2: If USEPA has not approved such amendment, CSI may petition the Board for amendment pursuant to the general rulemaking procedures of Section 27 of the Act and 35 Ill. Adm. Code 102 and 720.120(b); or
Option 3: Alternatively to options 1 or 2 above, CSI may petition the Board for a hazardous waste delisting pursuant to Section 28.1 of the Act and Subpart D of 35 Ill. Adm. Code
If CSI pursues general rulemaking (option 2 above) or hazardous waste delisting (option 3 above), it must demonstrate that the CSEAFD generated by a specific Super DetoxÔ treatment facility consistently meets the delisting levels specified in condition 3 below.
C. Subsequent verification testing: For the approved facility, CSI
2. Waste holding and handling: CSI
3. Delisting levels: All leachable concentrations for metals must not exceed the following levels (in parts per million (ppm)): antimony--0.06; arsenic
4. Changes in operating conditions: After initiating subsequent testing, as described in condition 1C, if CSI significantly changes the stabilization process established under condition 1 (e.g., use of new stabilization reagents), CSI
5. Data submittals: At least one month prior to operation of a new Super DetoxÔ treatment facility, CSI must notify the Agency in writing when the Super DetoxÔ treatment facility is scheduled to be on-line. The data obtained through condition 1A must be submitted to the Agency within the time period specified. Records of operating conditions and analytical data from condition 1 must be compiled, summarized, and maintained on site for a minimum of five years. These records and data must be furnished to the Agency upon request and made available for inspection. Failure to submit the required data within the specified time period or to maintain the required records on site for the specified time will be considered a violation of the Act and Board regulations. All data submitted must be accompanied by a signed copy of the following certification statement to attest to the truth and accuracy of the data submitted:
“Under civil and criminal penalty of law for the making or submission of false or fraudulent statements or representations, I certify that the information contained in or accompanying this document is true, accurate, and complete.
“As to (those) identified section(s) of this document for which I cannot personally verify its (their) truth and accuracy, I certify as the company official having supervisory responsibility for the persons who, acting under my direct instructions, made the verification that this information is true, accurate, and complete.
“In the event that any of this information is determined by the Board or a court of law to be false, inaccurate, or incomplete, and upon conveyance of this fact to the company, I recognize and agree that this exclusion of waste will be void as if it never had effect or to the extent directed by the Board or court and that the company will be liable for any actions taken in contravention of the company’s obligations under the federal RCRA and Comprehensive Environmental Response, Compensation and Liability Act (42 U.S.C. §§ 9601 et seq.) and corresponding provisions of the Act premised upon the company’s reliance on the void exclusion.”
BOARD NOTE: The obligations of this exclusion are derived from but also distinct from the obligations under the corresponding federally-granted exclusion of 40 CFR 261, Appendix IX, Table 2. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.Appendix I | |
Wastes Excluded by Administrative Action | |
Table C | Wastes Excluded by |
Facility Address |
Waste Description |
(None excluded from an Illinois source at this time) |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.Appendix I | |
Wastes Excluded by Administrative Action | |
Table D | Wastes Excluded by the Board by Adjusted Standard |
The Board has entered the following orders on petitions for adjusted standards for delisting, pursuant to 35 Ill. Adm. Code 720.122.
AS91-1 | Petition of Keystone Steel and Wire Co. for Hazardous Waste Delisting, February 6, 1992, and modified at 133 PCB 189, April 23, 1992. ( |
AS91-3 | Petition of Peoria Disposal Co. for an Adjusted Standard from Subpart D of 35 Ill. Adm. Code 721 |
AS93-7 | Petition of Keystone Steel & Wire Co. for an Adjusted Standard from Subpart D of 35 Ill. Adm. Code 721 |
AS94-10 | Petition of Envirite Corporation for an Adjusted Standard from Subpart D of 35 Ill. Adm. Code 721 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.Appendix Y | |
Table to Section 721.138 | |
Chemical name |
CAS No |
Composite value (mg/kg) |
Heating value (BTU/lb) |
Concentration limit (mg/kg at 10,000 Btu/lb) |
Minimum required detection limit (mg/kg) |
Total Nitrogen as N |
NA |
9000 |
18400 |
4900 |
|
Total Halogens as Cl |
NA |
1000 |
18400 |
540 |
|
Total Organic Halogens as Cl |
NA |
-- |
-- |
(Note 1) |
|
Polychlorinated biphenyls, total |
1336-36-3 |
ND |
-- |
ND |
1.4 |
Cyanide, total |
57-12-5 |
ND |
-- |
ND |
1.0 |
Metals: |
|||||
Antimony, total |
7440-36-0 |
ND |
-- |
12 |
|
Arsenic, total |
7440-38-2 |
ND |
-- |
0.23 |
|
Barium, total |
7440-39-3 |
ND |
-- |
23 |
|
Beryllium, total |
7440-41-7 |
ND |
-- |
1.2 |
|
Cadmium, total |
7440-43-9 |
-- |
ND |
1.2 |
|
Chromium, total |
7440-47-3 |
ND |
-- |
2.3 |
|
Cobalt |
7440-48-4 |
ND |
-- |
4.6 |
|
Lead, total |
7439-92-1 |
57 |
18100 |
31 |
|
Manganese |
7439-96-5 |
ND |
-- |
1.2 |
|
Mercury, total |
7439-97-6 |
ND |
-- |
0.25 |
|
Nickel, total |
7440-02-0 |
106 |
18400 |
58 |
|
Selenium, total |
7782-49-2 |
ND |
-- |
0.23 |
|
Silver, total |
7440-22-4 |
ND |
-- |
2.3 |
|
Thallium, total |
7440-28-0 |
ND |
-- |
23 |
|
Hydrocarbons: |
|||||
Benzo |
56-55-3 |
ND |
-- |
2400 |
|
Benzene |
71-43-2 |
8000 |
19600 |
4100 |
|
Benzo |
205-99-2 |
ND |
-- |
2400 |
|
Benzo |
207-08-9 |
ND |
-- |
2400 |
|
Benzo |
50-32-8 |
ND |
-- |
2400 |
|
Chrysene |
218-01-9 |
ND |
-- |
2400 |
|
Dibenzo |
53-70-3 |
ND |
-- |
2400 |
|
7,12-Dimethylbenz |
57-97-6 |
ND |
-- |
2400 |
|
Fluoranthene |
206-44-0 |
ND |
-- |
2400 |
|
Indeno(1,2,3-cd)pyrene |
193-39-5 |
ND |
-- |
2400 |
|
3-Methylcholanthrene |
56-49-5 |
ND |
-- |
2400 |
|
Naphthalene |
91-20-3 |
6200 |
19400 |
3200 |
|
Toluene |
108-88-3 |
69000 |
19400 |
36000 |
|
Oxygenates: |
|||||
Acetophenone |
98-86-2 |
ND |
-- |
2400 |
|
Acrolein |
107-02-8 |
ND |
-- |
39 |
|
Allyl alcohol |
107-18-6 |
ND |
-- |
30 |
|
Bis(2-ethylhexyl)phthalate |
117-81-7 |
ND |
-- |
2400 |
|
Butyl benzyl phthalate |
85-68-7 |
ND |
-- |
2400 |
|
o-Cresol |
95-48-7 |
ND |
-- |
2400 |
|
m-Cresol |
108-39-4 |
ND |
-- |
2400 |
|
p-Cresol |
106-44-5 |
ND |
-- |
2400 |
|
Di-n-butyl phthalate |
84-74-2 |
ND |
-- |
2400 |
|
Diethyl phthalate |
84-66-2 |
ND |
-- |
2400 |
|
2,4-Dimethylphenol |
105-67-9 |
ND |
-- |
2400 |
|
Dimethyl phthalate |
131-11-3 |
ND |
-- |
2400 |
|
Di-n-octyl phthalate |
117-84-0 |
ND |
-- |
2400 |
|
Endothall |
145-73-3 |
ND |
-- |
100 |
|
Ethyl methacrylate |
97-63-2 |
ND |
-- |
39 |
|
2-Ethoxyethanol |
110-80-5 |
ND |
-- |
100 |
|
Isobutyl alcohol |
78-83-1 |
ND |
-- |
39 |
|
Isosafrole |
120-58-1 |
ND |
-- |
2400 |
|
Methyl ethyl ketone |
78-93-3 |
ND |
-- |
39 |
|
Methyl methacrylate |
80-62-6 |
ND |
-- |
39 |
|
1,4-Naphthoquinone |
130-15-4 |
ND |
-- |
2400 |
|
Phenol |
108-95-2 |
ND |
-- |
2400 |
|
Propargyl alcohol |
107-19-7 |
ND |
-- |
30. |
|
Safrole |
94-59-7 |
ND |
-- |
2400 |
|
Sulfonated Organics: |
|||||
Carbon disulfide |
75-15-0 |
ND |
-- |
ND |
39 |
Disulfoton |
298-04-4 |
ND |
-- |
ND |
2400 |
Ethyl methanesulfonate |
62-50-0 |
ND |
-- |
ND |
2400 |
Methyl methanesulfonate |
66-27-3 |
ND |
-- |
ND |
2400 |
Phorate |
298-02-2 |
ND |
-- |
ND |
2400 |
1,3-Propane sultone |
1120-71-4 |
ND |
-- |
ND |
100 |
Tetraethyldithiopyrophosphate |
3689-24-5 |
ND |
-- |
ND |
2400 |
Thiophenol |
108-98-5 |
ND |
-- |
ND |
30 |
O,O,O-Triethyl phosphorothioate |
126-68-1 |
ND |
-- |
ND |
2400 |
Nitrogenated Organics: |
|||||
Acetonitrile |
75-05-8 |
ND |
-- |
ND |
39 |
2-Acetylaminofluorene |
53-96-3 |
ND |
-- |
ND |
2400 |
Acrylonitrile |
107-13-1 |
ND |
-- |
ND |
39 |
4-Aminobiphenyl |
92-67-1 |
ND |
-- |
ND |
2400 |
4-Aminopyridine |
504-24-5 |
ND |
-- |
ND |
100 |
Aniline |
62-53-3 |
ND |
-- |
ND |
2400 |
Benzidine |
92-87-5 |
ND |
-- |
ND |
2400 |
Dibenz |
224-42-0 |
ND |
-- |
ND |
2400 |
O,O-Diethyl O-pyrazinyl phophoro-thioate |
297-97-2 |
ND |
-- |
ND |
2400 |
Dimethoate |
60-51-5 |
ND |
-- |
ND |
2400 |
p-(Dimethylamino)azobenzene |
60-11-7 |
ND |
-- |
ND |
2400 |
3,3'-Dimethylbenzidine |
119-93-7 |
ND |
-- |
ND |
2400 |
a,a-Dimethylphenethylamine |
122-09-8 |
ND |
-- |
ND |
2400 |
3,3'-Dimethoxybenzidine |
119-90-4 |
ND |
-- |
ND |
100 |
1,3-Dinitrobenzene |
99-65-0 |
ND |
-- |
ND |
2400 |
4,6-Dinitro-o-cresol |
534-52-1 |
ND |
-- |
ND |
2400 |
2,4-Dinitrophenol |
51-28-5 |
ND |
-- |
ND |
2400 |
2,4-Dinitrotoluene |
121-14-2 |
ND |
-- |
ND |
2400 |
2,6-Dinitrotoluene |
606-20-2 |
ND |
-- |
ND |
2400 |
Dinoseb |
88-85-7 |
ND |
-- |
ND |
2400 |
Diphenylamine |
122-39-4 |
ND |
-- |
ND |
2400 |
Ethyl carbamate |
51-79-6 |
ND |
-- |
ND |
100 |
Ethylenethiourea (2-Imidazolidinethione) |
96-45-7 |
ND |
-- |
ND |
110 |
Famphur |
52-85-7 |
ND |
-- |
ND |
2400 |
Methacrylonitrile |
126-98-7 |
ND |
-- |
ND |
39 |
Methapyrilene |
91-80-5 |
ND |
-- |
ND |
2400 |
Methomyl |
16752-77-5 |
ND |
-- |
ND |
57 |
2-Methyllactonitrile |
75-86-5 |
ND |
-- |
ND |
100 |
Methyl parathion |
298-00-0 |
ND |
-- |
ND |
2400 |
MNNG (N-Metyl-N-nitroso-N’-nitroguanidine) |
70-25-7 |
ND |
-- |
ND |
110 |
1-Naphthylamine |
134-32-7 |
ND |
-- |
ND |
2400 |
2-Naphthylamine |
91-59-8 |
ND |
-- |
ND |
2400 |
Nicotine |
54-11-5 |
ND |
-- |
ND |
100 |
4-Nitroaniline |
100-01-6 |
ND |
-- |
ND |
2400 |
Nitrobenzene |
98-95-3 |
ND |
-- |
ND |
2400 |
p-Nitrophenol |
100-02-7 |
ND |
-- |
ND |
2400 |
5-Nitro-o-toluidine |
99-55-8 |
ND |
-- |
ND |
2400 |
N-Nitrosodi-n-butylamine |
924-16-3 |
ND |
-- |
ND |
2400 |
N-Nitrosodiethylamine |
55-18-5 |
ND |
-- |
ND |
2400 |
N-Nitrosodiphenylamine |
86-30-6 |
ND |
-- |
ND |
2400 |
N-Nitroso-N-methylethylamine |
10595-95-6 |
ND |
-- |
ND |
2400 |
N-Nitrosomorpholine |
59-89-2 |
ND |
-- |
ND |
2400 |
N-Nitrosopiperidine |
100-75-4 |
ND |
-- |
ND |
2400 |
N-Nitrosopyrrolidine |
930-55-2 |
ND |
-- |
ND |
2400 |
2-Nitropropane |
79-46-9 |
ND |
-- |
ND |
30 |
Parathion |
56-38-2 |
ND |
-- |
ND |
2400 |
Phenacetin |
62-44-2 |
ND |
-- |
ND |
2400 |
1,4-Phenylene diamine, |
106-50-3 |
ND |
-- |
ND |
2400 |
N-Phenylthiourea |
103-85-5 |
ND |
-- |
ND |
57 |
2-Picoline |
109-06-8 |
ND |
-- |
ND |
2400 |
Propythioracil |
51-52-5 |
ND |
-- |
ND |
100 |
Pyridine |
110-86-1 |
ND |
-- |
ND |
2400 |
Strychnine |
57-24-9 |
ND |
-- |
ND |
100 |
Thioacetamide |
62-55-5 |
ND |
-- |
ND |
57 |
Thiofanox |
39196-18-4 |
ND |
-- |
ND |
100 |
Thiourea |
62-56-6 |
ND |
-- |
ND |
57 |
Toluene-2,4-diamine |
95-80-7 |
ND |
-- |
ND |
57 |
Toluene-2,6-diamine |
823-40-5 |
ND |
-- |
ND |
57 |
o-Toluidine |
95-53-4 |
ND |
-- |
ND |
2400 |
p-Toluidine |
106-49-0 |
ND |
-- |
ND |
100 |
1,3,5-Trinitrobenzne, |
99-35-4 |
ND |
-- |
ND |
2400 |
Halogenated Organics: |
|||||
Allyl chloride |
107-05-1 |
ND |
-- |
ND |
39 |
Aramite |
140-57-8 |
ND |
-- |
ND |
2400 |
Benzal chloride |
98-87-3 |
ND |
-- |
ND |
100 |
Benzyl chloride |
100-44-77 |
ND |
-- |
ND |
100 |
Bis(2-chloroethyl)ether |
111-44-4 |
ND |
-- |
ND |
2400 |
Bromoform |
75-25-2 |
ND |
-- |
ND |
39 |
Bromomethane |
74-83-9 |
ND |
-- |
ND |
39 |
4-Bromophenyl phenyl ether |
101-55-3 |
ND |
-- |
ND |
2400 |
Carbon tetrachloride |
56-23-5 |
ND |
-- |
ND |
39 |
Chlordane |
57-74-9 |
ND |
-- |
ND |
14 |
p-Chloroaniline |
106-47-8 |
ND |
-- |
ND |
2400 |
Chlorobenzene |
108-90-7 |
ND |
-- |
ND |
39 |
Chlorobenzilate |
510-15-6 |
ND |
-- |
ND |
2400 |
p-Chloro-m-cresol |
59-50-7 |
ND |
-- |
ND |
2400 |
2-Chloroethyl vinyl ether |
110-75-8 |
ND |
-- |
ND |
39 |
Chloroform |
67-66-3 |
ND |
-- |
ND |
39 |
Chloromethane |
74-87-3 |
ND |
-- |
ND |
39 |
2-Chloronaphthalene |
91-58-7 |
ND |
-- |
ND |
2400 |
2-Chlorophenol |
95-57-8 |
ND |
-- |
ND |
2400 |
Chloroprene |
1126-99-8 |
ND |
-- |
ND |
39 |
2,4-D |
94-75-7 |
ND |
-- |
ND |
7.0 |
Diallate |
2303-16-4 |
ND |
-- |
ND |
2400 |
1,2-Dibromo-3-chloropropane |
96-12-8 |
ND |
-- |
ND |
39 |
1,2-Dichlorobenzene |
95-50-1 |
ND |
-- |
ND |
2400 |
1,3-Dichlorobenzene |
541-73-1 |
ND |
-- |
ND |
2400 |
1,4-Dichlorobenzene |
106-46-7 |
ND |
-- |
ND |
2400 |
3,3'-Dichlorobenzidine |
91-94-1 |
ND |
-- |
ND |
2400 |
Dichlorodifluoromethane |
75-71-8 |
ND |
-- |
ND |
39 |
1,2-Dichloroethane |
107-06-2 |
ND |
-- |
ND |
39 |
1,1-Dichloroethylene |
75-35-4 |
ND |
-- |
ND |
39 |
Dichloromethoxy ethane |
111-91-1 |
ND |
-- |
ND |
2400 |
2,4-Dichlorophenol |
120-83-2 |
ND |
-- |
ND |
2400 |
2,6-Dichlorophenol |
87-65-0 |
ND |
-- |
ND |
2400 |
1,2-Dichloropropane |
78-87-5 |
ND |
-- |
ND |
39 |
cis-1,3-Dichloropropylene |
10061-01-5 |
ND |
-- |
ND |
39 |
trans-1,3-Dichloropropylene |
10061-02-6 |
ND |
-- |
ND |
39 |
1,3-Dichloro-2-propanol |
96-23-1 |
ND |
-- |
ND |
30 |
Endosulfan I |
959-98-8 |
ND |
-- |
ND |
1.4 |
Endosulfan II |
33213-65-9 |
ND |
-- |
ND |
1.4 |
Endrin |
72-20-8 |
ND |
-- |
ND |
1.4 |
Endrin aldehyde |
7421-93-4 |
ND |
-- |
ND |
1.4 |
Endrin Ketone |
53494-70-5 |
ND |
-- |
ND |
1.4 |
Epichlorohydrin |
106-89-8 |
ND |
-- |
ND |
30 |
Ethylidene dichloride |
75-34-3 |
ND |
-- |
ND |
39 |
2-Fluoroacetamide |
640-19-7 |
ND |
-- |
ND |
100 |
Heptachlor |
76-44-8 |
ND |
-- |
ND |
1.4 |
Heptachlor epoxide |
1024-57-3 |
ND |
-- |
ND |
2.8 |
Hexachlorobenzene |
118-74-1 |
ND |
-- |
ND |
2400 |
Hexachloro-1,3-butadiene |
87-68-3 |
ND |
-- |
ND |
2400 |
Hexachlorocyclopentadiene |
77-47-4 |
ND |
-- |
ND |
2400 |
Hexachloroethane |
67-72-1 |
ND |
-- |
ND |
2400 |
Hexachlorophene |
70-30-4 |
ND |
-- |
ND |
59000 |
Hexachloropropene |
1888-71-7 |
ND |
-- |
ND |
2400 |
Isodrin |
465-73-6 |
ND |
-- |
ND |
2400 |
Kepone |
143-50-0 |
ND |
-- |
ND |
4700 |
Lindane |
58-89-9 |
ND |
-- |
ND |
1.4 |
Methylene chloride |
75-09-2 |
ND |
-- |
ND |
39 |
4,4'-methylene-bis(2-chloroaniline) |
101-14-4 |
ND |
-- |
ND |
100 |
Methyl iodide |
74-88-4 |
ND |
-- |
ND |
39 |
Pentachlorobenzene |
608-93-5 |
ND |
-- |
ND |
2400 |
Pentachloroethane |
76-01-7 |
ND |
-- |
ND |
39 |
Pentachloronitrobenzene |
82-68-8 |
ND |
-- |
ND |
2400 |
Pentachlorophenol |
87-86-5 |
ND |
-- |
ND |
2400 |
Pronamide |
23950-58-5 |
ND |
-- |
ND |
2400 |
Silvex |
93-72-1 |
ND |
-- |
ND |
7.0 |
2,3,7,8-Tetrachlorodibenzo-p-dioxin |
1746-01-6 |
ND |
-- |
ND |
30 |
1,2,4,5-Tetrachlorobenzene |
95-94-3 |
ND |
-- |
ND |
2400 |
1,1,2,2-Tetrachloroethane |
79-34-5 |
ND |
-- |
ND |
39 |
Tetrachloroethylene |
127-18-4 |
ND |
-- |
ND |
39 |
2,3,4,6-Tetrachlorophenol |
58-90-2 |
ND |
-- |
ND |
2400 |
1,2,4-Trichlorobenzene |
120-82-1 |
ND |
-- |
ND |
2400 |
1,1,1-Trichloroethane |
71-55-6 |
ND |
-- |
ND |
39 |
1,1,2-Trichloroethane |
79-00-5 |
ND |
-- |
ND |
39 |
Trichloroethylene |
79-01-6 |
ND |
-- |
ND |
39 |
Trichlorofluoromethane |
75-69-4 |
ND |
-- |
ND |
39 |
2,4,5-Trichlorophenol |
95-95-4 |
ND |
-- |
ND |
2400 |
2,4,6-Trichlorophenol |
88-06-2 |
ND |
-- |
ND |
2400 |
1,2,3-Trichloropropane |
96-18-4 |
ND |
-- |
ND |
39 |
Vinyl Chloride |
75-01-4 |
ND |
-- |
ND |
39 |
NA means not applicable.
ND means nondetect.
Note 1: 25 (mg/kg at 10,000 Btu/lb) as organic halogen or as the individual halogenated organics listed in the table at the levels indicated.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 721.Appendix Z | |
Table to Section 721.102 | |
Table
1 |
2 |
3 |
4 |
|
Use constituting disposal |
Burning for energy recovery or use to produce a fuel |
Reclamation (except as provided in Section 721.104(a)(17) for mineral processing secondary materials) |
Speculative accumulation |
|
Applicable Subsection of Section 721.102: |
(c)(1) |
(c)(2) |
(c)(3) |
(c)(4) |
Spent materials |
Yes |
Yes |
Yes |
Yes |
Sludges (listed in Section 721.131 or 721.132) |
Yes |
Yes |
Yes |
Yes |
Sludges exhibiting a characteristic of hazardous waste |
Yes |
Yes |
-- |
Yes |
By-products (listed in Section 721.131 or 721.132) |
Yes |
Yes |
Yes |
Yes |
By-products exhibiting a characteristic of hazardous waste |
Yes |
Yes |
-- |
Yes |
Commercial chemical products listed in Section 721.133 |
Yes |
Yes |
-- |
-- |
Scrap metal other than excluded scrap metal (see Section 721.101(c)(9)) |
Yes |
Yes |
Yes |
Yes |
Yes - Defined as a solid waste
No - Not defined as a solid waste
BOARD NOTE: Derived from Table 1 to 40 CFR 261.2 (1997) (2002), as amended at 63 Fed. Reg. 28636 (May 26, 1998). The terms “spent materials,”, “sludges,”, “by-products,”, “scrap metal,”, and “processed scrap metal” are defined in Section 721.101.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 726
STANDARDS FOR THE MANAGEMENT OF SPECIFIC HAZARDOUS WASTE AND SPECIFIC TYPES OF HAZARDOUS WASTE MANAGEMENT FACILITIES
SUBPART C: RECYCLABLE MATERIALS USED IN A MANNER CONSTITUTING DISPOSAL
Section
726.120 | Applicability |
726.121 | Standards |
726.122 | Standards |
726.123 | Standards Applicable to Users of Materials that |
SUBPART D: HAZARDOUS WASTE BURNED FOR ENERGY RECOVERY
Section
726.130 | Applicability (Repealed) |
726.131 | Prohibitions (Repealed) |
726.132 | Standards applicable to generators of hazardous waste fuel (Repealed) |
726.133 | Standards applicable to transporters of hazardous waste fuel (Repealed) |
726.134 | Standards applicable to marketers of hazardous waste fuel (Repealed) |
726.135 | Standards applicable to burners of hazardous waste fuel (Repealed) |
726.136 | Conditional exemption for spent materials and by-products exhibiting a characteristic of hazardous waste (Repealed) |
SUBPART E: USED OIL BURNED FOR ENERGY RECOVERY
Section
726.140 | Applicability (Repealed) |
726.141 | Prohibitions (Repealed) |
726.142 | Standards applicable to generators of used oil burned for energy recovery (Repealed) |
726.143 | Standards applicable to marketers of used oil burned for energy recovery (Repealed) |
726.144 | Standards applicable to burners of used oil burned for energy recovery (Repealed) |
SUBPART F: RECYCLABLE MATERIALS UTILIZED FOR PRECIOUS METAL RECOVERY
Section
726.170 | Applicability and |
SUBPART G: SPENT LEAD-ACID BATTERIES BEING RECLAIMED
Section
726.180 | Applicability and |
SUBPART H: HAZARDOUS WASTE BURNED IN BOILERS AND INDUSTRIAL FURNACES
Section
726.200 | Applicability |
726.201 | Management |
726.202 | Permit |
726.203 | Interim Status Standards for Burners |
726.204 | Standards to Control Organic Emissions |
726.205 | Standards to |
726.206 | Standards to Control Metals Emissions |
726.207 | Standards to |
726.208 | Small |
726.209 | Low |
726.210 | Waiver of DRE |
726.211 | Standards for |
726.212 | Regulation of Residues |
726.219 | Extensions of Time |
SUBPART M: MILITARY MUNITIONS
Section
726.300 | Applicability |
726.301 | Definitions |
726.302 | Definition of Solid Waste |
726.303 | Standards Applicable to the Transportation of Solid Waste Military Munitions |
726.304 | Standards Applicable to Emergency Responses |
726.305 | Standards Applicable to the Storage of Solid Waste Military Munitions |
726.306 | Standards Applicable to the Treatment and Disposal of Waste Military Munitions |
SUBPART N: CONDITIONAL EXEMPTION FOR LOW-LEVEL MIXED WASTE STORAGE, TREATMENT, TRANSPORTATION AND DISPOSAL
Section
726.310 | Definitions |
726.320 | Storage and Treatment Conditional Exemption |
726.325 | Wastes Eligible for a Storage and Treatment Conditional Exemption for Low-Level Mixed Waste |
726.330 | Conditions to Qualify for and Maintain a Storage and Treatment Conditional Exemption |
726.335 | Treatment Allowed by a Storage and Treatment Conditional Exemption |
726.340 | Loss of a Storage and Treatment Conditional Exemption and Required Action |
726.345 | Reclaiming a Lost Storage and Treatment Conditional Exemption |
726.350 | Recordkeeping for a Storage and Treatment Conditional Exemption |
726.355 | Waste No Longer Eligible for a Storage and Treatment Conditional Exemption |
726.360 | Applicability of Closure Requirements to Storage Units |
726.405 | Transportation and Disposal Conditional Exemption |
726.410 | Wastes Eligible for a Transportation and Disposal Conditional Exemption |
726.415 | Conditions to Qualify for and Maintain a Transportation and Disposal Conditional Exemption |
726.420 | Treatment Standards for Eligible Waste |
726.425 | Applicability of the Manifest and Transportation Condition |
726.430 | Effectiveness of a Transportation and Disposal Exemption |
726.435 | Disposal of Exempted Waste |
726.440 | Containers Used for Disposal of Exempted Waste |
726.445 | Notification |
726.450 | Recordkeeping for a Transportation and Disposal Conditional Exemption |
726.455 | Loss of a Transportation and Disposal Conditional Exemption and Required Action |
726.460 | Reclaiming a Lost Transportation and Disposal Conditional Exemption |
Tier I and Tier II Feed Rate and Emissions Screening Limits for Metals | |
Tier I Feed Rate Screening Limits for Total Chlorine | |
Tier II Emission Rate Screening Limits for Free Chlorine and Hydrogen Chloride | |
Reference Air Concentrations | |
Stack Plume Rise | |
Health-Based Limits for Exclusion of Waste-Derived Residues | |
Potential PICs for Determination of Exclusion of Waste-Derived Residues | |
Methods Manual for Compliance with BIF Regulations | |
Guideline on Air Quality Models | |
Lead-Bearing Materials | |
Nickel or Chromium-Bearing Materials that | |
Mercury-Bearing Wastes | |
Exempt Quantities for Small Quantity Burner Exemption | |
AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].
SOURCE: Adopted in R85-22 at 10 Ill. Reg. 1162, effective January 2, 1986; amended in R86-1 at 10 Ill. Reg. 14156, effective August 12, 1986; amended in R87-26 at 12 Ill. Reg. 2900, effective January 15, 1988; amended in R89-1 at 13 Ill. Reg. 18606, effective November 13, 1989; amended in R90-2 at 14 Ill. Reg. 14533, effective August 22, 1990; amended in R90-11 at 15 Ill. Reg. 9727, effective June 17, 1991; amended in R91-13 at 16 Ill. Reg. 9858, effective June 9, 1992; amended in R92-10 at 17 Ill. Reg. 5865, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20904, effective November 22, 1993; amended in R94-7 at 18 Ill. Reg. 12500, effective July 29, 1994; amended in R95-6 at 19 Ill. Reg. 10006, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 11263, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 754, effective December 16, 1997; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 18042, effective September 28, 1998; amended in R99-15 at 23 Ill. Reg. 9482, effective July 26, 1999; amended in R00-13 at 24 Ill. Reg. 9853, effective June 20, 2000; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. 6667, effective April 22, 2002; amended in R03-7 at 27 Ill. Reg. 4200, effective February 14, 2003; amended in R03-18 at 27 Ill. Reg. ________, effective ______________________.
SUBPART C: RECYCLABLE MATERIALS USED IN A MANNER CONSTITUTING DISPOSAL
Section 726.120 | Applicability |
a) | The regulations of this Subpart C apply to recyclable materials that are applied to or placed on the land in either of the following ways: |
1) | Without mixing with any other |
2) | After mixing or combination with any other |
b) | |
c) | Anti-skid and deicing uses |
d) | Fertilizers that contain recyclable materials are not subject to regulation provided that the following conditions are fulfilled: |
1) | They are zinc fertilizers excluded from the definition of solid waste according to 35 Ill. Adm. Code 721.104(a)(21); or |
2) | They meet the applicable treatment standards in Subpart D of 35 Ill. Adm. Code 728 for each hazardous waste that they contain. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.121 | Standards |
Generators and transporters A generator or transporter of materials a material that are is used in a manner that constitute constitutes disposal are is subject to the applicable requirements of 35 Ill. Adm. Code 722 and 723 and the notification requirement under Section 3010 of the Resource Conservation and Recovery Act (42 U.S.C. USC 6901 et seq.).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.122 | Standards |
Owners or operators An owner or operator of facilities a facility that store stores a recyclable materials material that are is to be used in a manner that constitutes disposal, but who are which is not the ultimate users user of the materials material, are is regulated under all applicable provisions of Subparts A through L of 35 Ill. Adm. Code 724 and 725.Subparts A through L, and 35 Ill. Adm. Code 702, 703, and 705, and the notification requirement under Section 3010 of the Resource Conservation and Recovery Act.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.123 | Standards Applicable to Users of Materials that |
a) | |
b) | The use of waste or used oil or other material that is contaminated with dioxin or any other hazardous waste (other than a waste identified solely on the basis of ignitability) for dust suppression or road treatment is prohibited. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART F: RECYCLABLE MATERIALS UTILIZED FOR PRECIOUS METAL RECOVERY
Section 726.170 | Applicability and |
a) | The regulations of this |
b) | |
1) | Notification requirements under Section 3010 of the Resource Conservation and Recovery Act; |
2) | Subpart B of 35 Ill. Adm. Code 722 |
3) | For precious metals exported to or imported from designated OECD member countries for recovery, Subpart H of 35 Ill. Adm. Code 722 |
c) | |
1) | Records showing the volume of these materials stored at the beginning of the calendar year; |
2) | The amount of these materials generated or received during the calendar year; and |
3) | The amount of materials remaining at the end of the calendar year. |
d) | Recyclable materials that are regulated under this Subpart F that are accumulated speculatively (as defined in 35 Ill. Adm. Code 721.101(c)) are subject to all applicable provisions of 35 Ill. Adm. Code 702, 703, and 722 through 725 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART G: SPENT LEAD-ACID BATTERIES BEING RECLAIMED
Section 726.180 | Applicability and |
a) | |
1) | If the batteries will be reclaimed through regeneration (such as by electrolyte replacement), the owner or operator is exempt from 35 Ill. Adm. Code 702, 703, 722 through 726 (except for 35 Ill. Adm. Code 722.111), and 728 and the notification requirements of section 3010 of RCRA, but the owner or operator is subject to 35 Ill. Adm. Code 721 and 722.111. |
2) | If the batteries will be reclaimed other than through regeneration, and the owner or operator generates, collects, or transports the batteries, the owner or operator is exempt from 35 Ill. Adm. Code 702, 703, and 722 through 726 (except for 35 Ill. Adm. Code 722.111) and the notification requirements of section 3010 of RCRA, but the owner or operator is subject to 35 Ill. Adm. Code 721 and 722.111 and applicable provisions of 35 Ill. Adm. Code 728. |
3) | If the batteries will be reclaimed other than through regeneration, and the owner or operator stores the batteries, but the owner or operator is not the reclaimer, the owner or operator is exempt from 35 Ill. Adm. Code 702, 703, and 722 through 726 (except for 35 Ill. Adm. Code 722.111) and the notification requirements of section 3010 of RCRA, but the owner or operator is subject to 35 Ill. Adm. Code 721 and 722.111 and applicable provisions of 35 Ill. Adm. Code 728. |
4) | If the batteries will be reclaimed other than through regeneration, and the owner or operator stores the batteries before the owner or operator reclaims them, the owner or operator must comply with Section 726.180(b) and other requirements described in that subsection, and the owner or operator is subject to 35 Ill. Adm. Code 721 and 722.111 and applicable provisions of 35 Ill. Adm. Code 728. |
5) | If the batteries will be reclaimed other than through regeneration, and the owner or operator does not store the batteries before the owner or operator reclaims them, the owner or operator is exempt from 35 Ill. Adm. Code 702, 703, and 722 through 726 (except for 35 Ill. Adm. Code 722.111) and the notification requirements of section 3010 of RCRA, and the owner or operator is subject to 35 Ill. Adm. Code 721 and 722.111 and applicable provisions of 35 Ill. Adm. Code 728. |
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b) | |
1) | For an interim status facility, the owner or operator |
A) | The notification requirements under Section 3010 of the Resource Conservation and Recovery Act (RCRA) |
B) | All applicable provisions in Subpart A of 35 Ill. Adm. Code 725 |
C) | All applicable provisions in Subpart B of 35 Ill. Adm. Code 725 |
D) | All applicable provisions in Subparts C and D of 35 Ill. Adm. Code 725 |
E) | All applicable provisions in Subpart E of 35 Ill. Adm. Code 725 |
F) | All applicable provisions in Subparts F through L of 35 Ill. Adm. Code 725 |
G) | All applicable provisions in 35 Ill. Adm. Code 702 |
2) | For a permitted facility, the following requirements: |
A) | The notification requirements under section 3010 of RCRA |
B) | All applicable provisions in Subpart A of 35 Ill. Adm. Code 724 |
C) | All applicable provisions in Subpart B of 35 Ill. Adm. Code 724 |
D) | All applicable provisions in Subparts C and D of 35 Ill. Adm. Code 724 |
E) | All applicable provisions in Subpart E of 35 Ill. Adm. Code 724 |
F) | All applicable provisions in Subparts F through L of 35 Ill. Adm. Code 724 |
G) | All applicable provisions in 35 Ill. Adm. Code 702 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART H: HAZARDOUS WASTE BURNED IN BOILERS AND INDUSTRIAL FURNACES
Section 726.200 | Applicability |
a) | The regulations of this Subpart H apply to hazardous waste burned or processed in a boiler or industrial furnace (BIF) (as defined in 35 Ill. Adm. Code 720.110) irrespective of the purpose of burning or processing, except as provided by subsections (b), (c), (d), (g), and (h) of this Section. In this Subpart H, the term “burn” means burning for energy recovery or destruction or processing for materials recovery or as an ingredient. The emissions standards of Sections 726.204, 726.205, 726.206, and 726.207 apply to facilities operating under interim status or under a RCRA permit, as specified in Sections 726.202 and 726.203. |
b) | Integration of the MACT standards. |
1) | Except as provided by subsection (b)(2) of this Section, the standards of this Part no longer apply when an affected source demonstrates compliance with the maximum achievable control technology (MACT) requirements of 40 CFR 63, subpart EEE, incorporated by reference in 35 Ill. Adm. Code 720.111, by conducting a comprehensive performance test and submitting to the Agency a Notification of Compliance, under 40 CFR 63.1207(j) and 63.1210(b), documenting compliance with the requirements of 40 CFR 63, subpart EEE. Nevertheless, even after this demonstration of compliance with the MACT standards, RCRA permit conditions that were based on the standards of this Part will continue to be in effect until they are removed from the permit or the permit is terminated or revoked, unless the permit expressly provides otherwise. |
2) | The following standards continue to apply: |
A) | If an owner or operator elects to comply with 35 Ill. Adm. Code 703.320(a)(1)(A) to minimize emissions of toxic compounds from startup, shutdown, and malfunction events, Section 726.202(e)(1), requiring operations in accordance with the operating requirements specified in the permit at all times that hazardous waste is in the unit, and Section 726.202(e)(2)(C), requiring compliance with the emission standards and operating requirements, during startup and shutdown if hazardous waste is in the combustion chamber, except for particular hazardous wastes. These provisions apply only during startup, shutdown, and malfunction events; |
B) | The closure requirements of Sections 726.202(e)(11) and 726.203(l); |
C) | The standards for direct transfer of Section 726.211; |
D) | The standards for regulation of residues of Section 726.312; and |
E) | The applicable requirements of Subparts A through H, BB, and CC of 35 Ill. Adm. Code 724 and 725. |
BOARD NOTE: Sections 9.1 and 39.5 of the Environmental Protection Act [415 ILCS 5/9.1 and 39.5] make the federal MACT standards directly applicable to entities in Illinois and authorize the Agency to issue permits based on the federal standards. In adopting this subsection (b), USEPA stated as follows (at 64 Fed Reg. 52828, 52975 (September 30,1999)):
Under [the approach adopted by USEPA as a] final rule, MACT air emissions and related operating requirements are to be included in title V permits; RCRA permits will continue to be required for all other aspects of the combustion unit and the facility that are governed by RCRA (e.g., corrective action, general facility standards, other combustor-specific concerns such as materials handling, risk-based emissions limits and operating requirements, as appropriate, and other hazardous waste management units).
c) | The following hazardous wastes and facilities are not subject to regulation under this Subpart H: |
1) | Used oil burned for energy recovery that is also a hazardous waste solely because it exhibits a characteristic of hazardous waste identified in Subpart C of 35 Ill. Adm. Code 721. Such used oil is subject to regulation under 35 Ill. Adm. Code 739, rather than this Subpart; |
2) | Gas recovered from hazardous or solid waste landfills, when such gas is burned for energy recovery; |
3) | Hazardous wastes that are exempt from regulation under 35 Ill. Adm. Code 721.104 and 721.106(a)(3)(C) and (a)(3)(D) and hazardous wastes that are subject to the special requirements for conditionally exempt small quantity generators under 35 Ill. Adm. Code 721.105; and |
4) | Coke ovens, if the only hazardous waste burned is USEPA hazardous waste no. K087 decanter tank tar sludge from coking operations. |
d) | Owners and operators of smelting, melting, and refining furnaces (including pyrometallurgical devices, such as cupolas, sintering machines, roasters, and foundry furnaces, but not including cement kilns, aggregate kilns, or halogen acid furnaces burning hazardous waste) that process hazardous waste solely for metal recovery are conditionally exempt from regulation under this Subpart H, except for Sections 726.201 and 726.212. |
1) | To be exempt from Sections 726.202 through 726.211, an owner or operator of a metal recovery furnace or mercury recovery furnace must comply with the following requirements, except that an owner or operator of a lead or a nickel-chromium recovery furnace or a metal recovery furnace that burns baghouse bags used to capture metallic dust emitted by steel manufacturing must comply with the requirements of subsection (d)(3) of this Section, and an owner or operator of a lead recovery furnace that is subject to regulation under the Secondary Lead Smelting NESHAP of 40 CFR 63, subpart X must comply with the requirements of subsection (h) of this Section: |
A) | Provide a one-time written notice to the Agency indicating the following: |
i) | The owner or operator claims exemption under this subsection; |
ii) | The hazardous waste is burned solely for metal recovery consistent with the provisions of subsection (d)(2) of this Section; |
iii) | The hazardous waste contains recoverable levels of metals; and |
iv) | The owner or operator will comply with the sampling and analysis and recordkeeping requirements of this subsection (d); |
B) | Sample and analyze the hazardous waste and other feedstocks as necessary to comply with the requirements of this subsection (d) under procedures specified by “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111, or alternative methods that meet or exceed the SW-846 method performance capabilities. If SW-846 does not prescribe a method for a particular determination, the owner or operator must use the best available method; and |
C) | Maintain at the facility for at least three years records to document compliance with the provisions of this subsection (d), including limits on levels of toxic organic constituents and Btu value of the waste and levels of recoverable metals in the hazardous waste compared to normal non-hazardous waste feedstocks. |
2) | A hazardous waste meeting either of the following criteria is not processed solely for metal recovery: |
A) | The hazardous waste has a total concentration of organic compounds listed in Appendix H to 35 Ill. Adm. Code 721 exceeding 500 ppm by weight, as fired, and so is considered to be burned for destruction. The concentration of organic compounds in a waste as-generated may be reduced to the 500 ppm limit by bona fide treatment that removes or destroys organic constituents. Blending for dilution to meet the 500 ppm limit is prohibited, and documentation that the waste has not been impermissibly diluted must be retained in the records required by subsection (d)(1)(C) of this Section; or |
B) | The hazardous waste has a heating value of 5,000 Btu/lb or more, as-fired, and is so considered to be burned as fuel. The heating value of a waste as-generated may be reduced to below the 5,000 Btu/lb limit by bona fide treatment that removes or destroys organic constituents. Blending for dilution to meet the 5,000 Btu/lb limit is prohibited and documentation that the waste has not been impermissibly diluted must be retained in the records required by subsection (d)(1)(C) of this Section. |
3) | To be exempt from Sections 726.202 through 726.211, an owner or operator of a lead, nickel-chromium, or mercury recovery furnace, except for an owner or operator of a lead recovery furnace that is subject to regulation under the Secondary Lead Smelting NESHAP of 40 CFR 63, subpart X, or a metal recovery furnace that burns baghouse bags used to capture metallic dusts emitted by steel manufacturing must provide a one-time written notice to the Agency identifying each hazardous waste burned and specifying whether the owner or operator claims an exemption for each waste under this subsection (d)(3) or subsection (d)(1) of this Section. The owner or operator must comply with the requirements of subsection (d)(1) of this Section for those wastes claimed to be exempt under that subsection and must comply with the following requirements for those wastes claimed to be exempt under this subsection (d)(3): |
A) | The hazardous wastes listed in Appendices K, L, and M of this Part and baghouse bags used to capture metallic dusts emitted by steel manufacturing are exempt from the requirements of subsection (d)(1) of this Section, provided the following are true: |
i) | A waste listed in Appendix K of this Part must contain recoverable levels of lead, a waste listed in Appendix L of this Part must contain recoverable levels of nickel or chromium, a waste listed in Appendix M of this Part must contain recoverable levels of mercury and contain less than 500 ppm of Appendix H to 35 Ill. Adm. Code 721 organic constituents, and baghouse bags used to capture metallic dusts emitted by steel manufacturing must contain recoverable levels of metal; |
ii) | The waste does not exhibit the toxicity characteristic of 35 Ill. Adm. Code 721.124 for an organic constituent; |
iii) | The waste is not a hazardous waste listed in Subpart D of 35 Ill. Adm. Code 721 because it is listed for an organic constituent, as identified in Appendix G of 35 Ill. Adm. Code 721; and |
iv) | The owner or operator certifies in the one-time notice that hazardous waste is burned under the provisions of subsection (d)(3) of this Section and that sampling and analysis will be conducted or other information will be obtained as necessary to ensure continued compliance with these requirements. Sampling and analysis must be conducted according to subsection (d)(1)(B) of this Section, and records to document compliance with subsection (d)(3) of this Section must be kept for at least three years. |
B) | The Agency may decide, on a case-by-case basis, that the toxic organic constituents in a material listed in Appendix K, Appendix L, or Appendix M of this Part that contains a total concentration of more than 500 ppm toxic organic compounds listed in Appendix H to 35 Ill. Adm. Code 721 may pose a hazard to human health and the environment when burned in a metal recovery furnace exempt from the requirements of this Subpart H. Under these circumstances, after adequate notice and opportunity for comment, the metal recovery furnace will become subject to the requirements of this Subpart H when burning that material. In making the hazard determination, the Agency must consider the following factors: |
i) | The concentration and toxicity of organic constituents in the material; |
ii) | The level of destruction of toxic organic constituents provided by the furnace; and |
iii) | Whether the acceptable ambient levels established in Appendix D or E of this Part will be exceeded for any toxic organic compound that may be emitted based on dispersion modeling to predict the maximum annual average off-site ground level concentration. |
e) | The standards for direct transfer operations under Section 726.211 apply only to facilities subject to the permit standards of Section 726.202 or the interim status standards of Section 726.203. |
f) | The management standards for residues under Section 726.212 apply to any BIF burning hazardous waste. |
g) | Owners and operators of smelting, melting, and refining furnaces (including pyrometallurgical devices such as cupolas, sintering machines, roasters, and foundry furnaces) that process hazardous waste for recovery of economically significant amounts of the precious metals gold, silver, platinum, palladium, iridium, osmium, rhodium, ruthenium, or any combination of these metals are conditionally exempt from regulation under this Subpart H, except for Section 726.212. To be exempt from Sections 726.202 through 726.211, an owner or operator must do the following: |
1) | Provide a one-time written notice to the Agency indicating the following: |
A) | The owner or operator claims exemption under this Section, |
B) | The hazardous waste is burned for legitimate recovery of precious metal, and |
C) | The owner or operator will comply with the sampling and analysis and recordkeeping requirements of this Section; |
2) | Sample and analyze the hazardous waste, as necessary, to document that the waste is burned for recovery of economically significant amounts of precious metal, using procedures specified by Test Methods for Evaluating Solid Waste, Physical/Chemical Methods, SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111, or alternative methods that meet or exceed the SW-846 method performance capabilities. If SW-846 does not prescribe a method for a particular determination, the owner or operator must use the best available method; and |
3) | Maintain, at the facility for at least three years, records to document that all hazardous wastes burned are burned for recovery of economically significant amounts of precious metal. |
h) | An owner or operator of a lead recovery furnace that processes hazardous waste for recovery of lead and which is subject to regulation under the Secondary Lead Smelting NESHAP of 40 CFR 63, subpart X, is conditionally exempt from regulation under this Subpart, except for Section 726.201. To become exempt, an owner or operator must provide a one-time notice to the Agency identifying each hazardous waste burned and specifying that the owner or operator claims an exemption under this subsection (h). The notice also must state that the waste burned has a total concentration of non-metal compounds listed in Appendix H to 35 Ill. Adm. Code 721 of less than 500 ppm by weight, as fired and as provided in subsection (d)(2)(A) of this Section, or is listed in Appendix K to this Part. |
i) | Abbreviations and definitions. The following definitions and abbreviations are used in this Subpart H: |
“APCS” means air pollution control system.
“BIF” means boiler or industrial furnace.
“Carcinogenic metals” means arsenic, beryllium, cadmium, and chromium.
“CO” means carbon monoxide.
“Continuous monitor” is a monitor that continuously samples the regulated parameter without interruption, that evaluates the detector response at least once each 15 seconds, and that computes and records the average value at least every 60 seconds.
“DRE” means destruction or removal efficiency.
“cu m” or “m3” means cubic meters.
“E” means “ten to the power.” For example, “XE-Y” means “X times ten to the -Y power.”
“Feed rates” are measured as specified in Section 726.202(e)(6).
“Good engineering practice stack height” is as defined by 40 CFR 51.100(ii), incorporated by reference in 35 Ill. Adm. Code 720.111.
“HC” means hydrocarbon.
“HCl” means hydrogen chloride gas.
“Hourly rolling average” means the arithmetic mean of the 60 most recent one-minute average values recorded by the continuous monitoring system.
“K” means Kelvin.
“kVA” means kilovolt amperes.
“MEI” means maximum exposed individual.
“MEI location” means the point with the maximum annual average off-site (unless on-site is required) ground level concentration.
“Noncarcinogenic metals” means antimony, barium, lead, mercury, thallium, and silver.
“One hour block average” means the arithmetic mean of the one minute averages recorded during the 60-minute period beginning at one minute after the beginning of the preceding clock hour.
“PIC” means product of incomplete combustion.
“PM” means particulate matter.
“POHC” means principal organic hazardous constituent.
“ppmv” means parts per million by volume.
“QA/QC” means quality assurance and quality control.
“Rolling average for the selected averaging period” means the arithmetic mean of one hour block averages for the averaging period.
“RAC” means reference air concentration, the acceptable ambient level for the noncarcinogenic metals for purposes of this Subpart. RACs are specified in Appendix D of this Part.
“RSD” means risk-specific dose, the acceptable ambient level for the carcinogenic metals for purposes of this Subpart. RSDs are specified in Appendix E of this Part.
“SSU” means “Saybolt Seconds Universal,” a unit of viscosity measured by ASTM D 88-87 or D 2161-87, incorporated by reference in 35 Ill. Adm. Code 720.111.
“TCLP test” means the toxicity characteristic leaching procedure of 35 Ill. Adm. Code 721.124.
“TESH” means terrain-adjusted effective stack height (in meters).
“Tier I.” See Section 726.206(b).
“Tier II.” See Section 726.206(c).
“Tier III.” See Section 726.206(d).
“Toxicity equivalence” is estimated, pursuant to Section 726.204(e), using “Procedures for Estimating the Toxicity Equivalence of Chlorinated Dibenzo-p-Dioxin and Dibenzofuran Congeners,” incorporated by reference in Appendix I of this Part.
“mg” means microgram.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.201 | Management |
a) | Generators. |
b) | Transporters. |
c) | Storage and treatment facilities. |
1) | An owner or operator of a facility that stores or treats hazardous waste that is burned in a BIF is subject to the applicable provisions of 35 Ill. Adm. Code 702, 703, 724, and 725 |
2) | An owner or operator of a facility that burns, in an on-site BIF exempt from regulation under the small quantity burner provisions of Section 726.208, hazardous waste that it generates is exempt from regulation under 35 Ill. Adm. Code 702, 703, 724, and 725 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.202 | Permit |
a) | Applicability. |
1) | General. |
2) | Applicability of 35 Ill. Adm. Code 724 standards. |
A) | In Subpart A (General), 35 Ill. Adm. Code 724.104; |
B) | In Subpart B (General facility standards), 35 Ill. Adm. Code 724.111 through 724.118; |
C) | In Subpart C (Preparedness and prevention), 35 Ill. Adm. Code 724.131 through 724.137; |
D) | In Subpart D (Contingency plan and emergency procedures), 35 Ill. Adm. Code 724.151 through 724.156; |
E) | In Subpart E (Manifest system, recordkeeping and reporting), the applicable provisions of 35 Ill. Adm. Code 724.171 through 724.177; |
F) | In Subpart F (Corrective Action), 35 Ill. Adm. Code 724.190 and 724.201; |
G) | In Subpart G (Closure and post-closure), 35 Ill. Adm. Code 724.211 through 724.215; |
H) | In Subpart H (Financial requirements), 35 Ill. Adm. Code 724.241, 724.242, 724.243, and 724.247 through 724.251, except that the State of Illinois and the |
I) | Subpart BB (Air emission standards for equipment leaks), except 35 Ill. Adm. Code 724.950(a). |
b) | Hazardous waste analysis. |
1) | The owner or operator |
2) | Throughout normal operation, the owner or operator |
c) | Emissions standards. Owners and operators |
d) | Permits. |
1) | The owner or operator |
2) | Hazardous wastes not specified in the permit must not be burned until operating conditions have been specified under a new permit or permit modification, as applicable. Operating requirements for new wastes must be based on either trial burn results or alternative data included with Part B of a permit application under 35 Ill. Adm. Code 703.208. |
3) | BIFs operating under the interim status standards of Section 726.203 are permitted under procedures provided by 35 Ill. Adm. Code 703.232(g). |
4) | A permit for a new BIF (those BIFs not operating under the interim status standards) must establish appropriate conditions for each of the applicable requirements of this Section, including but not limited to allowable hazardous waste firing rates and operating conditions necessary to meet the requirements of subsection (e) |
A) | For the period beginning with initial introduction of hazardous waste and ending with initiation of the trial burn, and only for the minimum time required to bring the device to a point of operational readiness to conduct a trial burn, not to exceed a duration of 720 hours operating time when burning hazardous waste, the operating requirements must be those most likely to ensure compliance with the emission standards of Sections 726.204 through 726.207, based on the Agency’s engineering judgment. If the applicant is seeking a waiver from a trial burn to demonstrate conformance with a particular emission standard, the operating requirements during this initial period of operation must include those specified by the applicable provisions of Section 726.204, Section 726.205, Section 726.206, or Section 726.207. The Agency |
B) | For the duration of the trial burn, the operating requirements must be sufficient to demonstrate compliance with the emissions standards of Sections 726.204 through 726.207 and must be in accordance with the approved trial burn plan; |
C) | For the period immediately following completion of the trial burn, and only for the minimum period sufficient to allow sample analysis, data computation, submission of the trial burn results by the applicant, review of the trial burn results, and modification of the facility permit by the Agency to reflect the trial burn results, the operating requirements must be those most likely to ensure compliance with the emission standards Sections 726.204 through 726.207 based on the Agency’s engineering judgment. |
D) | For the remaining duration of the permit, the operating requirements must be those demonstrated in a trial burn or by alternative data specified in 35 Ill. Adm. Code 703.208, as sufficient to ensure compliance with the emissions standards of Sections 726.204 through 726.207. |
e) | Operating requirements. |
1) | General. A BIF burning hazardous waste must be operated in accordance with the operating requirements specified in the permit at all times when there is hazardous waste in the unit. |
2) | Requirements to ensure compliance with the organic emissions standards. |
A) | DRE (destruction or removal efficiency) standard. Operating conditions must be specified in either of the following ways: on a case-by-case basis for each hazardous waste burned, which conditions must be demonstrated (in a trial burn or by alternative data, as specified in 35 Ill. Adm. Code 703.208) to be sufficient to comply with the DRE performance standard of Section 726.204(a) |
i) | Feed rate of hazardous waste and other fuels measured and specified as prescribed in subsection (e)(6) |
ii) | Minimum and maximum device production rate when producing normal product expressed in appropriate units, measured and specified as prescribed in subsection (e)(6) |
iii) | Appropriate controls of the hazardous waste firing system; |
iv) | Allowable variation in BIF system design or operating procedures; |
v) | Minimum combustion gas temperature measured at a location indicative of combustion chamber temperature, measured, and specified as prescribed in subsection (e)(6) |
vi) | An appropriate indicator of combustion gas velocity, measured and specified as prescribed in subsection (e)(6) |
vii) | Such other operating requirements as are necessary to ensure that the DRE performance standard of Section 726.204(a) is met. |
B) | CO and hydrocarbon (HC) standards. The permit must incorporate a CO limit and, as appropriate, a HC limit as provided by Section 726.204(b), (c), (d), (e), and (f). The permit limits must be specified as follows: |
i) | When complying with the CO standard of Section 726.204(b)(1), the permit limit is 100 ppmv; |
ii) | When complying with the alternative CO standard under Section 726.204(c), the permit limit for CO is based on the trial burn and is established as the average over all valid runs of the highest hourly rolling average CO level of each run; and, the permit limit for HC is 20 ppmv (as defined in Section 726.204(c)(1)), except as provided in Section 726.204(f) |
iii) | When complying with the alternative HC limit for industrial furnaces under Section 726.204(f), the permit limit for HC and CO is the baseline level when hazardous waste is not burned as specified by that subsection. |
C) | Start-up and shut-down. During start-up and shut-down of the BIF, hazardous waste |
3) | Requirements to ensure conformance with the particulate matter (PM) standard. |
A) | Except as provided in subsections (e)(3)(B) and (e)(3)(C) |
i) | Total ash feed rate to the device from hazardous waste, other fuels, and industrial furnace feedstocks, measured and specified as prescribed in subsection (e)(6) |
ii) | Maximum device production rate when producing normal product expressed in appropriate units, and measured and specified as prescribed in subsection (e)(6) |
iii) | Appropriate controls on operation and maintenance of the hazardous waste firing system and any air pollution control system (APCS); |
iv) | Allowable variation in BIF system design including any APCS or operating procedures; and |
v) | Such other operating requirements as are necessary to ensure that the PM standard in Section 726.211(b) is met. |
B) | Permit conditions to ensure conformance with the PM standard must not be provided for facilities exempt from the PM standard under Section 726.205(b); |
C) | For cement kilns and light-weight aggregate kilns, permit conditions to ensure compliance with the PM standard must not limit the ash content of hazardous waste or other feed materials. |
4) | Requirements to ensure conformance with the metals emissions standard. |
A) | For conformance with the Tier I (or adjusted Tier I) metals feed rate screening limits of Section 726.206(b) or (e), the permit must specify the following operating requirements: |
i) | Total feed rate of each metal in hazardous waste, other fuels and industrial furnace feedstocks measured and specified under provisions of subsection (e)(6) |
ii) | Total feed rate of hazardous waste measured and specified as prescribed in subsection (e)(6) |
iii) | A sampling and metals analysis program for the hazardous waste, other fuels and industrial furnace feedstocks; |
B) | For conformance with the Tier II metals emission rate screening limits under Section 726.206(c) and the Tier III metals controls under Section 726.206(d), the permit must specify the following operating requirements: |
i) | Maximum emission rate for each metal specified as the average emission rate during the trial burn; |
ii) | Feed rate of total hazardous waste and pumpable hazardous waste, each measured and specified as prescribed in subsection (e)(6)(A) |
iii) | Feed rate of each metal in the following feedstreams, measured and specified as prescribed in subsections (e)(6) |
iv) | Total feed rate of chlorine and chloride in total feed streams measured and specified as prescribed in subsection (e)(6) |
v) | Maximum combustion gas temperature measured at a location indicative of combustion chamber temperature, and measured and specified as prescribed in subsection (e)(6) |
vi) | Maximum flue gas temperature at the inlet to the PM APCS measured and specified as prescribed in subsection (e)(6) |
vii) | Maximum device production rate when producing normal product expressed in appropriate units and measured and specified as prescribed in subsection (e)(6) |
viii) | Appropriate controls on operation and maintenance of the hazardous waste firing system and any APCS; |
ix) | Allowable variation in BIF system design including any APCS or operating procedures; and |
x) | Such other operating requirements as are necessary to ensure that the metals standards under Sections 726.206(c) or (d) are met. |
C) | For conformance with an alternative implementation approach approved by the Agency under Section 726.206(f), the permit must specify the following operating requirements: |
i) | Maximum emission rate for each metal specified as the average emission rate during the trial burn; |
ii) | Feed rate of total hazardous waste and pumpable hazardous waste, each measured and specified as prescribed in subsection (e)(6)(A) |
iii) | Feed rate of each metal in the following feedstreams, measured and specified as prescribed in subsection (e)(6) |
iv) | Total feed rate of chlorine and chloride in total feed streams measured and specified prescribed in subsection (e)(6) |
v) | Maximum combustion gas temperature measured at a location indicative of combustion chamber temperature, and measured and specified as prescribed in subsection (e)(6) |
vi) | Maximum flue gas temperature at the inlet to the PM APCS measured and specified as prescribed in subsection (e)(6) |
vii) | Maximum device production rate when producing normal product expressed in appropriate units and measured and specified as prescribed in subsection (e)(6) |
viii) | Appropriate controls on operation and maintenance of the hazardous waste firing system and any APCS; |
ix) | Allowable variation in BIF system design including any APCS or operating procedures; and |
x) | Such other operating requirements as are necessary to ensure that the metals standards under Sections 726.206(c) or (d) are met. |
5) | Requirements to ensure conformance with the HCl and chlorine gas standards. |
A) | For conformance with the Tier I total chlorine and chloride feed rate screening limits of Section 726.207(b)(1), the permit must specify the following operating requirements: |
i) | Feed rate of total chlorine and chloride in hazardous waste, other fuels and industrial furnace feedstocks measured and specified as prescribed in subsection (e)(6) |
ii) | Feed rate of total hazardous waste measured and specified as prescribed in subsection (e)(6) |
iii) | A sampling and analysis program for total chlorine and chloride for the hazardous waste, other fuels and industrial furnace feedstocks; |
B) | For conformance with the Tier II HCl and chlorine gas emission rate screening limits under Section 726.207(b)(2) and the Tier III HCl and chlorine gas controls under Section 726.207(c), the permit must specify the following operating requirements: |
i) | Maximum emission rate for HCl and for chlorine gas specified as the average emission rate during the trial burn; |
ii) | Feed rate of total hazardous waste measured and specified as prescribed in subsection (e)(6) |
iii) | Total feed rate of chlorine and chloride in total feed streams, measured and specified as prescribed in subsection (e)(6) |
iv) | Maximum device production rate when producing normal product expressed in appropriate units, measured and specified as prescribed in subsection (e)(6) |
v) | Appropriate controls on operation and maintenance of the hazardous waste firing system and any APCS; |
vi) | Allowable variation in BIF system design including any APCS or operating procedures; and |
vii) | Such other operating requirements as are necessary to ensure that the HCl and chlorine gas standards under Section 726.207(b)(2) or (c) are met. |
6) | Measuring parameters and establishing limits based on trial burn data. |
A) | General requirements. As specified in subsections (e)(2) through (e)(5) |
i) | Instantaneous limits. A parameter is measured and recorded on an instantaneous basis (i.e., the value that occurs at any time) and the permit limit specified as the time-weighted average during all valid runs of the trial burn; or |
ii) | Hourly rolling average. The limit for a parameter must be established and continuously monitored on an hourly rolling average basis, as defined in Section |
B) | Rolling average limits for carcinogenic metals and lead. Feed rate limits for the carcinogenic metals (as defined in Section |
i) | The feed rate of each metal must be limited at any time to ten times the feed rate that would be allowed on an hourly rolling average basis; |
ii) | Terms are as defined in Section |
iii) | The permit limit for the feed rate of each metal must be established based on trial burn data as the average over all valid test runs of the highest hourly rolling average feed rate for each run. |
C) | Feed rate limits for metals, total chlorine and chloride, and ash. Feed rate limits for metals, total chlorine and chloride, and ash are established and monitored by knowing the concentration of the substance (i.e., metals, chloride/chlorine and ash) in each feedstream and the flow rate of the feedstream. To monitor the feed rate of these substances, the flow rate of each feedstream must be monitored under the continuous monitoring requirements of subsections (e)(6)(A) and (e)(6)(B) |
D) | Conduct of trial burn testing. |
i) | If compliance with all applicable emissions standards of Sections 726.204 through 726.207 is not demonstrated simultaneously during a set of test runs, the operating conditions of additional test runs required to demonstrate compliance with remaining emissions standards must be as close as possible to the original operating conditions. |
ii) | Prior to obtaining test data for purposes of demonstrating compliance with the emissions standards of Sections 726.204 through 726.207 or establishing limits on operating parameters under this Section, the unit must operate under trial burn conditions for a sufficient period to reach steady-state operations. However, industrial furnaces that recycle collected PM back into the furnace and that comply with an alternative implementation approach for metals under Section 726.206(f) need not reach steady state conditions with respect to the flow of metals in the system prior to beginning compliance testing for metals emissions. |
iii) | Trial burn data on the level of an operating parameter for which a limit must be established in the permit must be obtained during emissions sampling for the |
7) | General requirements. |
A) | Fugitive emissions. Fugitive emissions must be controlled |
i) | |
ii) | |
iii) | |
B) | Automatic waste feed cutoff. A BIF must be operated with a functioning system that automatically cuts off the hazardous waste feed when operating conditions deviate from those established under this Section. In addition, the following requirements apply: |
i) | The permit limit for (the indicator of) minimum combustion chamber temperature must be maintained while hazardous waste or hazardous waste residues remain in the combustion chamber, |
ii) | Exhaust gases must be ducted to the APCS operated in accordance with the permit requirements while hazardous waste or hazardous waste residues remain in the combustion chamber; and |
iii) | Operating parameters for which permit limits are established must continue to be monitored during the cutoff, and the hazardous waste feed must not be restarted until the levels of those parameters comply with the permit limits. For parameters that are monitored on an instantaneous basis, the Agency |
C) | Changes. A BIF must cease burning hazardous waste when combustion properties |
8) | Monitoring and Inspections. |
A) | The owner or operator |
i) | If specified by the permit, feed rates and composition of hazardous waste, other fuels, and industrial furnace feedstocks |
ii) | If specified by the permit, CO, HCs, and oxygen on a continuous basis at a common point in the BIF downstream of the combustion zone and prior to release of stack gases to the atmosphere in accordance with operating requirements specified in subsection (e)(2)(B) |
iii) | Upon the request of the Agency, sampling and analysis of the hazardous waste (and other fuels and industrial furnace feedstocks as appropriate), residues, and exhaust emissions must be conducted to verify that the operating requirements established in the permit achieve the applicable standards of Sections 726.204, 726.205, 726.206, and 726.207. |
B) | All monitors must record data in units corresponding to the permit limit unless otherwise specified in the permit. |
C) | The BIF and associated equipment (pumps, values, pipes, fuel storage tanks, etc.) must be subjected to thorough visual inspection when it contains hazardous waste, at least daily for leaks, spills, fugitive emissions, and signs of tampering. |
D) | The automatic hazardous waste feed cutoff system and associated alarms must be tested at least once every |
E) | These monitoring and inspection data must be recorded and the records must be placed in the operating record required by 35 Ill. Adm. Code 724.173. |
9) | Direct transfer to the burner. If hazardous waste is directly transferred from a transport vehicle to a BIF without the use of a storage unit, the owner and operator |
10) | Recordkeeping. The owner or operator |
11) | Closure. At closure, the owner or operator |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.203 | Interim Status Standards for Burners |
a) | Purpose, scope, and applicability. |
1) | General. |
A) | The purpose of this Section is to establish minimum national standards for owners and operators of “existing” BIFs that burn hazardous waste where such standards define the acceptable management of hazardous waste during the period of interim status. The standards of this Section apply to owners and operators of existing facilities until either a permit is issued under Section 726.202(d) or until closure responsibilities identified in this Section are fulfilled. |
B) | “Existing” or “in existence” means a BIF for which the owner or operator filed a certification of precompliance with USEPA pursuant to 40 CFR 266.103(b), incorporated by reference in subsection (b) |
C) | If a BIF is located at a facility that already has a RCRA permit or interim status, then the owner or operator |
2) | Exemptions. The requirements of this Section do not apply to hazardous waste and facilities exempt under |
3) | Prohibition on burning dioxin-listed wastes. The following hazardous waste listed for dioxin and hazardous waste derived from any of these wastes must not be burned in a BIF operating under interim status: USEPA hazardous waste numbers F020, F021, F022, F023, F026, and F027. |
4) | Applicability of 35 Ill. Adm. Code 725 standards. |
A) | In Subpart A of |
B) | In Subpart B of |
C) | In Subpart C of |
D) | In Subpart D of |
E) | In Subpart E of |
F) | In Subpart G of |
G) | In Subpart H of |
H) | In Subpart BB of |
5) | Special requirements for furnaces. The following controls apply during interim status to industrial furnaces (e.g., kilns, cupolas) that feed hazardous waste for a purpose other than solely as an ingredient (see subsection (a)(5)(B) |
A) | Controls. |
i) | The hazardous waste must be fed at a location where combustion gas |
ii) | The owner or operator |
iii) | For cement kiln systems, the hazardous waste must be fed into the kiln; and |
iv) | The HC controls of Section 726.204(f) or subsection (c)(5) |
B) | Burning hazardous waste solely as an ingredient. A hazardous waste is burned for a purpose other than “solely as an ingredient” if it meets either of |
i) | The hazardous waste has a total concentration of nonmetal compounds listed in Appendix H of 35 Ill. Adm. Code 721 |
ii) | The hazardous waste has a heating value of 5,000 Btu/lb or more, as fired, and so is considered to be burned as fuel. The heating value of a waste as-generated may be reduced to below the 5,000 Btu/lb limit by bona fide treatment that removes or destroys organic constituents. The heating value of a waste as-generated may be reduced to below the 5,000 Btu/lb limit by bona fide treatment that removes or destroys organic constituents. Blending to augment the heating value to meet the 5,000 Btu/lb limit is prohibited and documentation that the waste has not been impermissibly blended must be retained in the facility record. |
6) | Restrictions on burning hazardous waste that is not a fuel. Prior to certification of compliance under subsection (c) |
A) | Hazardous waste may be burned solely as an ingredient; |
B) | Hazardous waste may be burned for purposes of compliance testing (or testing prior to compliance testing) for a total period of time not to exceed 720 hours; |
C) | Such waste may be burned if the Agency has documentation to show that |
i) | The BIF was operating under the interim status standards for incinerators or thermal treatment units, Subparts O or P of 35 Ill. Adm. Code 725 |
ii) | The BIF met the interim status eligibility requirements under 35 Ill. Adm. Code 703.153 for Subparts O or P of 35 Ill. Adm. Code 725 |
iii) | Hazardous waste with a heating value less than 5,000 Btu/lb was burned prior to that date; or |
D) | Such waste may be burned in a halogen acid furnace if the waste was burned as an excluded ingredient under 35 Ill. Adm. Code 721.102(e) prior to February 21, 1991, and documentation is kept on file supporting this claim. |
7) | Direct transfer to the burner. If hazardous waste is directly transferred from a transport vehicle to a BIF without the use of a storage unit, the owner or operator |
b) | Certification of precompliance. This subsection corresponds with 40 CFR 266.103(b), under which USEPA required certain owners and operators to file a certification of precompliance by August 21, 1991. No similar filing with the Agency was required, so the Board did not incorporate the federal filing requirement into the Illinois regulations. This statement maintains structural parity with the federal regulations. |
c) | Certification of compliance. The owner or operator |
1) | Limits on operating conditions. The owner or operator |
A) | Feed rate of total hazardous waste and (unless complying the Tier I or adjusted Tier I metals feed rate screening limits under Section 726.206(b) or (e)), pumpable hazardous waste; |
B) | Feed rate of each metal in the following feedstreams: |
i) | Total feedstreams, except that industrial furnaces |
BOARD NOTE: Federal subsections 266.103(c)(1)(ii)(A)(1) and (c)(1)(ii)(A)(2) are condensed into the above subsection (c)(1)(B)(i).
ii) | Total hazardous waste feed (unless complying with the Tier I or adjusted Tier I metals feed rate screening limits under Section 726.206(b) or (e)); and |
iii) | Total pumpable hazardous waste feed (unless complying with Tier I or Adjusted Tier I metals feed rate screening limits under |
C) | Total feed rate of total chlorine and chloride in total feed streams, except that facilities that comply with Tier I or Adjusted Tier I feed rate screening limits may set their operating limits at the total chlorine and chloride feed rate screening limits determined under |
D) | Total feed rate of ash in total feed streams, except that the ash feed rate for cement kilns and light-weight aggregate kilns is not limited; |
E) | CO concentration, and where required, HC concentration in stack gas. When complying with the CO controls of Section 726.204(b), the CO limit is 100 ppmv, and when complying with the HC controls of Section 726.204(c), the HC limit is 20 ppmv. When complying with the CO controls of Section 726.204(c), the CO limit is established based on the compliance test; |
F) | Maximum production rate of the device in appropriate units when producing normal product unless complying with Tier I or Adjusted Tier I feed rate screening limits for chlorine under |
G) | Maximum combustion chamber temperature where the temperature measurement is as close to the combustion zone as possible and is upstream of any quench water injection, (unless complying with the Tier I adjusted Tier I metals feed rate screening limits under Section 726.206(b) or (e)); |
H) | Maximum flue gas temperature entering a PM control device (unless complying with Tier I or adjusted Tier I metals feed rate screening limits under Section 726.206(b) or (e)); |
I) | For systems using wet scrubbers, including wet ionizing scrubbers (unless complying with the Tier I or adjusted Tier I metals feed rate screening limits under Section 726.206(b) or (e) and the total chlorine and chloride feed rate screening limits under Section 726.207(b)(1) or (e)): |
i) | Minimum liquid to flue gas ratio; |
ii) | Minimum scrubber blowdown from the system or maximum suspended solids content of scrubber water; and |
iii) | Minimum pH level of the scrubber water; |
J) | For systems using venturi scrubbers, the minimum differential gas pressure across the venturi (unless complying the Tier I or adjusted Tier I metals feed rate screening limits under Section 726.206(b) or (e) and the total chlorine and chloride feed rate screening limits under Section 726.207(b)(1) or (e)); |
K) | For systems using dry scrubbers (unless complying with the Tier I or adjusted Tier I metals feed rate screening limits under Section 726.206(b) or (e) and the total chlorine and chloride feed rate screening limits under Section 726.207(b)(1) or (e)): |
i) | Minimum caustic feed rate; and |
ii) | Maximum flue gas flow rate; |
L) | For systems using wet ionizing scrubbers or electrostatic precipitators (unless complying with the Tier I or adjusted Tier I metals feed rate screening limits under Section 726.206(b) or (e) and the total chlorine and chloride feed rate screening limits under Section 726.207(b)(1) or (e)): |
i) | Minimum electrical power in kVA to the precipitator plates; and |
ii) | Maximum flue gas flow rate; |
M) | For systems using fabric filters (baghouses), the minimum pressure drop (unless complying with the Tier I or adjusted Tier I metals feed rate screening limits under Section 726.206(b) or (e) and the total chlorine and chloride feed rate screening limits under Section 726.207(b)(1) or (e)). |
2) | Prior notice of compliance testing. At least 30 days prior to the compliance testing required by subsection (c)(3) |
A) | General facility information including: |
i) | USEPA facility ID number; |
ii) | Facility name, contact person, telephone number, and address; |
iii) | Person responsible for conducting compliance test, including company name, address, and telephone number, and a statement of qualifications; |
iv) | Planned date of the compliance test; |
B) | Specific information on each device to be tested, including the following: |
i) | A Description of BIF; |
ii) | A scaled plot plan showing the entire facility and location of the BIF; |
iii) | A description of the APCS; |
iv) | Identification of the continuous emission monitors that are installed, including the following: CO monitor; Oxygen monitor; HC monitor, specifying the minimum temperature of the system, and, if the temperature is less than 150° C, an explanation of why a heated system is not used (see subsection (c)(5) |
v) | Indication of whether the stack is shared with another device that will be in operation during the compliance test; and |
vi) | Other information useful to an understanding of the system design or operation; and |
C) | Information on the testing planned, including a complete copy of the test protocol and QA/QC plan, and a summary description for each test providing the following information at a minimum: |
i) | Purpose of the test (e.g., demonstrate compliance with emissions of PM); and |
ii) | Planned operating conditions, including levels for each pertinent parameter specified in subsection (c)(1) |
3) | Compliance testing. |
A) | General. Compliance testing must be conducted under conditions for which the owner or operator has submitted a certification of precompliance under subsection (b) |
B) | Special requirements for industrial furnaces that recycle collected PM. Owners and operators of industrial furnaces that recycle back into the furnace PM from the APCS |
i) | The special testing requirements prescribed in “Alternative Method for Implementing Metals Controls” in |
ii) | Stack emissions testing for a minimum of |
iii) | Conduct compliance testing to determine compliance with the metals standards to establish limits on the operating parameters of subsection (c)(1) |
C) | Conduct of compliance testing. |
i) | If compliance with all applicable emissions standards of Sections 726.204 through 726.207 is not demonstrated simultaneously during a set of test runs, the operating conditions of additional test runs required to demonstrate compliance with remaining emissions standards must be as close as possible to the original operating conditions. |
ii) | Prior to obtaining test data for purposes of demonstrating compliance with the applicable emissions standards of Sections 726.204 through 726.207 or establishing limits on operating parameters under this Section, the facility must operate under compliance test conditions for a sufficient period to reach steady-state operations. Industrial furnaces that recycle collected PM back into the furnace and that comply with |
iii) | Compliance test data on the level of an operating parameter for which a limit must be established in the certification of compliance must be obtained during emissions sampling for the |
4) | Certification of compliance. Within 90 days of completing compliance testing, the owner or operator |
A) | General facility and testing information, including the following: |
i) | USEPA facility ID number; |
ii) | Facility name, contact person, telephone number, and address; |
iii) | Person responsible for conducting compliance testing, including company name, address, and telephone number, and a statement of qualifications; |
iv) | |
v) | Description of BIF tested; |
vi) | Person responsible for QA/QC, title and telephone number, and statement that procedures prescribed in the QA/QC plan submitted under Section 726.203(c)(2)(C) have been followed, or a description of any changes and an explanation of why changes were necessary; |
vii) | Description of any changes in the unit configuration prior to or during testing that would alter any of the information submitted in the prior notice of compliance testing under subsection (c)(2) |
viii) | Description of any changes in the planned test conditions prior to or during the testing that alter any of the information submitted in the prior notice of compliance testing under subsection (c)(2) |
ix) | The complete report on results of emissions testing. |
B) | Specific information on each test, including the following: |
i) | |
ii) | Summary of test results for each run and for each test including the following information: |
C) | Comparison of the actual emissions during each test with the emissions limits prescribed by Sections 726.204(b), (c), and (e) |
D) | Determination of operating limits based on all valid runs of the compliance test for each applicable parameter listed in subsection (c)(1) |
i) | Instantaneous limits. A parameter must be measured and recorded on an instantaneous basis (i.e., the value that occurs at any time) and the operating limit specified as the time-weighted average during all runs of the compliance test. |
ii) | Hourly rolling average basis. The limit for a parameter must be established and continuously monitored on an hourly rolling average basis, as defined in Section |
iii) | Rolling average limits for carcinogenic metals (as defined in Section 726.200(i)) and lead. Feed rate limits for the carcinogenic metals and lead must be established either on an hourly rolling average basis as prescribed by subsection (c)(4)(D)(ii) |
iv) | Feed rate limits for metals, total chlorine and chloride, and ash. Feed rate limits for metals, total chlorine and chloride, and ash are established and monitored by knowing the concentration of the substance (i.e., metals, chloride/chlorine, and ash) in each feedstream and the flow rate of the feedstream. To monitor the feed rate of these substances, the flow rate of each feedstream must be monitored under the continuous monitoring requirements of subsections (c)(4)(D)(i) through (c)(4)(D)(iii) |
E) | Certification of compliance statement. The following statement must accompany the certification of compliance: |
“I certify under penalty of law that this information was prepared under my direction or supervision in accordance with a system designed to ensure that qualified personnel properly gathered and evaluated the information and supporting documentation. Copies of all emissions tests, dispersion modeling results, and other information used to determine conformance with the requirements of 35 Ill. Adm. Code 726.203(c) are available at the facility and can be obtained from the facility contact person listed above. Based on my inquiry of the person or persons who manage the facility, or those persons directly responsible for gathering the information, the information submitted is, to the best of my knowledge and belief, true, accurate, and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment for knowing violations.
I also acknowledge that the operating limits established pursuant to 35 Ill. Adm. Code 726.203(c)(4)(D) are enforceable limits at which the facility can legally operate during interim status until a revised certification of compliance is submitted.”
5) | Special requirements for HC monitoring systems. When an owner or operator is required to comply with the HC controls provided by |
6) | Special operating requirements for industrial furnaces that recycle collected PM. Owners and operators of industrial furnaces that recycle back into the furnace PM from the APCS must do the following: |
A) | When complying with the requirements of subsection (c)(3)(B)(i) |
B) | When complying with the requirements of subsection (c)(3)(B)(ii) |
7) | Extensions of time. |
A) | If the owner or operator does not submit a complete certification of compliance for all of the applicable emissions standards of Sections 726.204, 726.205, 726.206, and 726.207 by August 21, 1992, the owner or operator |
i) | Stop burning hazardous waste and begin closure activities under subsection (l) |
ii) | Limit hazardous waste burning only for purposes of compliance testing (and pretesting to prepare for compliance testing) a total period of 720 hours for the period of time beginning August 21, 1992, submit a notification to the Agency by August 21, 1992 stating that the facility is operating under restricted interim status and intends to resume burning hazardous waste, and submit a complete certification of compliance by August 23, 1993; or |
iii) | Obtain a case-by-case extension of time under subsection (c)(7)(B) |
B) | Case-by-case extensions of time. See Section 726.219. |
8) | Revised certification of compliance. The owner or operator may submit at any time a revised certification of compliance (recertification of compliance) under the following procedures: |
A) | Prior to submittal of a revised certification of compliance, hazardous waste must not be burned for more than a total of 720 hours under operating conditions that exceed those established under a current certification of compliance, and such burning must be conducted only for purposes of determining whether the facility can operate under revised conditions and continue to meet the applicable emissions standards of Sections 726.204, 726.205, 726.206, and 726.207; |
B) | At least 30 days prior to first burning hazardous waste under operating conditions that exceed those established under a current certification of compliance, the owner or operator |
i) | USEPA facility ID number, and facility name, contact person, telephone number, and address; |
ii) | Operating conditions that the owner or operator is seeking to revise and description of the changes in facility design or operation that prompted the need to seek to revise the operating conditions; |
iii) | A determination that, when operating under the revised operating conditions, the applicable emissions standards of Sections 726.204, 726.205, 726.206, and 726.207 are not likely to be exceeded. To document this determination, the owner or operator |
iv) | Complete emissions testing protocol for any pretesting and for a new compliance test to determine compliance with the applicable emissions standards of Sections 726.204, 726.205, 726.206, and 726.207 when operating under revised operating conditions. The protocol |
C) | Conduct a compliance test under the revised operating conditions and the protocol submitted to the Agency to determine compliance with the applicable emissions standards of Sections 726.204, 726.205, 726.206, and 726.207; and |
D) | Submit a revised certification of compliance under subsection (c)(4) |
d) | Periodic Recertifications. The owner or operator |
e) | Noncompliance with certification schedule. If the owner or operator does not comply with the interim status compliance schedule provided by subsections (b), (c), and (d) |
f) | Start-up and shut-down. Hazardous waste (except waste fed solely as an ingredient under the Tier I (or adjusted Tier I) feed rate screening limits for metals and chloride/chlorine) must not be fed into the device during start-up and shut-down of the BIF, unless the device is operating within the conditions of operation specified in the certification of compliance. |
g) | Automatic waste feed cutoff. During the compliance test required by subsection (c)(3) |
1) | To minimize emissions of organic compounds, the minimum combustion chamber temperature (or the indicator of combustion chamber temperature) that occurred during the compliance test must be maintained while hazardous waste or hazardous waste residues remain in the combustion chamber, with the minimum temperature during the compliance test defined as either of the following: |
A) | If compliance with the combustion chamber temperature limit is based on a hourly rolling average, the minimum temperature during the compliance test is considered to be the average over all runs of the lowest hourly rolling average for each run; or |
B) | If compliance with the combustion chamber temperature limit is based on an instantaneous temperature measurement, the minimum temperature during the compliance test is considered to be the time-weighted average temperature during all runs of the test; and |
2) | Operating parameters limited by the certification of compliance must continue to be monitored during the cutoff, and the hazardous waste feed must not be restarted until the levels of those parameters comply with the limits established in the certification of compliance. |
h) | Fugitive emissions. Fugitive emissions must be controlled |
1) | |
2) | |
3) | |
i) | Changes. A BIF must cease burning hazardous waste when combustion properties, or feed rates of the hazardous waste, other fuels or industrial furnace feedstocks, or the BIF design or operating conditions deviate from the limits specified in the certification of compliance. |
j) | Monitoring and Inspections. |
1) | The owner or operator |
A) | Feed rates and composition of hazardous waste, other fuels, and industrial furnace feed stocks |
B) | CO, oxygen, and, if applicable, HC |
C) | Upon the request of the Agency, sampling and analysis of the hazardous waste (and other fuels and industrial furnace feed stocks as appropriate) and the stack gas emissions must be conducted to verify that the operating conditions established in the certification of precompliance or certification of compliance achieve the applicable standards of Sections 726.204, 726.205, 726.206, and 726.207. |
2) | The BIF and associated equipment (pumps, valves, pipes, fuel storage tanks, etc.) must be subjected to thorough visual inspection when they contain hazardous waste, at least daily for leaks, spills, fugitive emissions, and signs of tampering. |
3) | The automatic hazardous waste feed cutoff system and associated alarms must be tested at least once every |
4) | These monitoring and inspection data must be recorded and the records must be placed in the operating log. |
k) | Recordkeeping. The owner or operator |
l) | Closure. At closure, the owner or operator |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.204 | Standards to Control Organic Emissions |
a) | DRE standard. |
1) | General. Except as provided in subsection (a)(3) of this Section, a BIF burning hazardous waste must achieve a DRE of 99.99 percent for all organic hazardous constituents in the waste feed. To demonstrate conformance with this requirement, 99.99 percent DRE must be demonstrated during a trial burn for each principal organic hazardous constituent (POHC) designated (under subsection (a)(2) of this Section) in its permit for each waste feed. DRE is determined for each POHC from the following equation: |
whereWhere:
I = | Mass feed rate of one POHC in the hazardous waste fired to the BIF; and |
O = | Mass emission rate of the same POHC present in stack gas prior to release to the atmosphere. |
2) | Designation of POHCs. POHCs are those compounds for which compliance with the DRE requirements of this Section must be demonstrated in a trial burn in conformance with procedures prescribed in 35 Ill. Adm. Code 703.232. One or more POHCs must be designated by the Agency for each waste feed to be burned. POHCs must be designated based on the degree of difficulty of destruction of the organic constituents in the waste and on their concentrations or mass in the waste feed considering the results of waste analyses submitted with Part B of the permit application. POHCs are most likely to be selected from among those compounds listed in Appendix H to 35 Ill. Adm. Code 721 |
3) | Dioxin-listed waste. A BIF burning hazardous waste containing (or derived from) USEPA Hazardous Wastes Nos. F020, F021, F022, F023, F026, or F027 must achieve a destruction and removal efficiency (DRE) of 99.9999 percent for each POHC designated (under subsection (a)(2) of this Section) in its permit. This performance must be demonstrated on POHCs that are more difficult to burn than tetra-, penta-, and hexachlorodibenzo-p-dioxins and dibenzofurans. DRE is determined for each POHC from the equation in subsection (a)(1) of this Section. In addition, the owner or operator of the BIF |
4) | Automatic waiver of DRE trial burn. Owners and operators of boilers operated under the special operating requirements provided by Section 726.210 are considered to be in compliance with the DRE standard of subsection (a)(1) of this Section and are exempt from the DRE trial burn. |
5) | Low risk waste. Owners and operators of BIFs that burn hazardous waste in compliance with the requirements of Section 726.209(a) are considered to be in compliance with the DRE standard of subsection (a)(1) of this Section and are exempt from the DRE trial burn. |
b) | CO standard. |
1) | Except as provided in subsection (c) of this Section, the stack gas concentration of CO from a BIF burning hazardous waste cannot exceed 100 ppmv on an hourly rolling average basis (i.e., over any 60 minute period), continuously corrected to |
2) | CO and oxygen must be continuously monitored in conformance with “Performance Specifications for Continuous Emission Monitoring of Carbon Monoxide and Oxygen for Incinerators, Boilers, and Industrial Furnaces Burning Hazardous Waste” in |
3) | Compliance with the 100 ppmv CO limit must be demonstrated during the trial burn (for new facilities or an interim status facility applying for a permit) or the compliance test (for interim status facilities). To demonstrate compliance, the highest hourly rolling average CO level during any valid run of the trial burn or compliance test must not exceed 100 ppmv. |
c) | Alternative CO standard. |
1) | The stack gas concentration of CO from a BIF burning hazardous waste may exceed the 100 ppmv limit provided that stack gas concentrations of HCs do not exceed 20 ppmv, except as provided by subsection (f) of this Section for certain industrial furnaces. |
2) | HC limits must be established under this Section on an hourly rolling average basis (i.e., over any 60 minute period), reported as propane, and continuously corrected to |
3) | HC must be continuously monitored in conformance with “Performance Specifications for Continuous Emission Monitoring of Hydrocarbons for Incinerators, Boilers, and Industrial Furnaces Burning Hazardous Waste” in |
4) | The alternative CO standard is established based on CO data during the trial burn (for a new facility) and the compliance test (for an interim status facility). The alternative CO standard is the average over all valid runs of the highest hourly average CO level for each run. The CO limit is implemented on an hourly rolling average basis, and continuously corrected to |
d) | Special requirements for furnaces. Owners and operators of industrial furnaces (e.g., kilns, cupolas) that feed hazardous waste for a purpose other than solely as an ingredient (see Section 726.203(a)(5)(B)) at any location other than the end where products are normally discharged and where fuels are normally fired must comply with the HC limits provided by subsection (c) or (f) of this Section irrespective of whether stack gas CO concentrations meet the 100 ppmv limit of subsection (b) of this Section. |
e) | Controls for dioxins and furans. Owners and operators of BIFs that are equipped with a dry PM control device that operates within the temperature range of 450º through 750° F, and industrial furnaces operating under an alternative HC limit established under subsection (f) of this Section |
1) | During the trial burn (for new facilities or an interim status facility applying for a permit) or compliance test (for interim status facilities), determine emission rates of the tetra-octa congeners of chlorinated dibenzo-p-dioxins and dibenzofurans (CDDs/CDFs) using Method 0023A, “Sampling Method for Polychlorinated Dibenzo-p-Dioxins and Polychlorinated Dibenzofurans Emissions from Stationary Sources,” USEPA Publication SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111; |
2) | Estimate the 2,3,7,8-TCDD toxicity equivalence of the tetra-octa CDDs/CDFs congeners using “Procedures for Estimating the Toxicity Equivalence of Chlorinated Dibenzo-p-Dioxin and Dibenzofuran Congeners” in |
3) | Conduct dispersion modeling using methods recommended in 40 CFR 51, Appendix W, as incorporated by reference at 35 Ill. Adm. Code 720.111 (“Guideline on Air Quality Models (Revised)” (1986) and its supplements), the “Hazardous Waste Combustion Air Quality Screening Procedure,” |
4) | The ratio of the predicted maximum annual average ground level concentration of 2,3,7,8-TCDD equivalents to the risk-specific dose (RSD) for 2,3,7,8-TCDD provided in |
f) | Monitoring CO and HC in the by-pass duct of a cement kiln. Cement kilns may comply with the CO and HC limits provided by subsections (b), (c), and (d) of this Section by monitoring in the by-pass duct provided that the following conditions are fulfilled: |
1) | Hazardous waste is fired only into the kiln and not at any location downstream from the kiln exit relative to the direction of gas flow; and |
2) | The by-pass duct diverts a minimum of 10 percent of kiln off-gas into the duct. |
g) | Use of emissions test data to demonstrate compliance and establish operating limits. Compliance with the requirements of this Section must be demonstrated simultaneously by emissions testing or during separate runs under identical operating conditions. Further, data to demonstrate compliance with the CO and HC limits of this Section or to establish alternative CO or HC limits under this Section must be obtained during the time that DRE testing, and where applicable, CDD/CDF testing under subsection (e) of this Section and comprehensive organic emissions testing under subsection (f) of this Section is conducted. |
h) | Enforcement. For the purposes of permit enforcement, compliance with the operating requirements specified in the permit (under Section 726.202) will be regarded as compliance with this Section. However, evidence that compliance with those permit conditions is insufficient to ensure compliance with the requirements of this Section is “information” justifying modification or revocation and re-issuance of a permit under 35 Ill. Adm. Code 703.270 et seq. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.205 | Standards to |
a) | A BIF burning hazardous waste must not emit PM in excess of 180 mg/dry standard |
b) | An owner or operator meeting the requirements of Section 726.209(b) for the low risk waste exemption is exempt from the PM standard. |
c) | Oxygen correction. |
1) | Measured pollutant levels must be corrected for the amount of oxygen in the stack gas according to the following formula: |
Where:
Pc | is the corrected concentration of the pollutant in the stack gas, |
Pm | is the measured concentration of the pollutant in the stack gas, |
E | is the oxygen concentration on a dry basis in the combustion air fed to the device, and |
Y | is the measured oxygen concentration on a dry basis in the stack. |
2) | For devices that feed normal combustion air, E will equal 21 percent. For devices that feed oxygen-enriched air for combustion (that is, air with an oxygen concentration exceeding 21 percent), the value of E will be the concentration of oxygen in the enriched air. |
3) | Compliance with all emission standards provided by this Subpart H must be based on correcting to seven percent oxygen using this procedure. |
d) | For the purposes of permit enforcement, compliance with the operating requirements specified in the permit (under Section 726.202) will be regarded as compliance with this Section. However, evidence that compliance with those permit conditions is insufficient to ensure compliance with the requirements of this Section is “information” justifying modification or revocation and re-issuance of a permit under 35 Ill. Adm. Code 703.270 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.206 | Standards to Control Metals Emissions |
a) | General. The owner or operator |
b) | Tier I feed rate screening limits. Feed rate screening limits for metals are specified in |
1) | Noncarcinogenic metals. The feed rates of the noncarcinogenic metals in all feed streams, including hazardous waste, fuels, and industrial furnace feed stocks must not exceed the screening limits specified in |
A) | The feed rate screening limits for antimony, barium, mercury, thallium, and silver are based on either of the following: |
i) | An hourly rolling average, as defined in Sections 726.200(g) and 726.202(e)(6)(A)(ii); or |
ii) | An instantaneous limit not to be exceeded at any time. |
B) | The feed rate screening limit for lead is based on one of the following: |
i) | An hourly rolling average, as defined in Sections 726.200(g) and 726.202(e)(6)(A)(ii); |
ii) | An averaging period of 2 to 24 hours, as defined in Section 726.202(e)(6)(B) with an instantaneous feed rate limit not to exceed 10 times the feed rate that would be allowed on an hourly rolling average basis; or |
iii) | An instantaneous limit not to be exceeded at any time. |
2) | Carcinogenic metals. |
A) | The feed rates of carcinogenic metals in all feed streams, including hazardous waste, fuels, and industrial furnace feed stocks must not exceed values derived from the screening limits specified in |
whereWhere:
S Ai/Fi | means the sum of the values of A/F for each metal “i,” |
n = | number of carcinogenic metals. |
Ai = | the actual feed rate to the device for metal “i.” |
Fi = | the feed rate screening limit provided by |
B) | The feed rate screening limits for the carcinogenic metals are based on either: |
i) | An hourly rolling average; or |
ii) | An averaging period of |
3) | TESH (terrain adjusted effective stack height). |
A) | The TESH is determined according to the following equation: |
TESH = H + P - T
whereWhere:
H = | Actual physical stack height (m). |
P = | Plume rise (in m) as determined from |
T = | Terrain rise (in m) within five kilometers of the stack. |
B) | The stack height (H) must not exceed good engineering practice stack height, as defined in Section |
C) | If the TESH calculated pursuant to subsection (b)(3)(A) of this Section is not listed in |
4) | Terrain type. The screening limits are a function of whether the facility is located in noncomplex or complex terrain. A device located where any part of the surrounding terrain within five kilometers of the stack equals or exceeds the elevation of the physical stack height (H) is considered to be in complex terrain and the screening limits for complex terrain apply. Terrain measurements are to be made from U.S. Geological Survey 7.5-minute topographic maps of the area surrounding the facility. |
5) | Land use. The screening limits are a function of whether the facility is located in an area where the land use is urban or rural. To determine whether land use in the vicinity of the facility is urban or rural, procedures provided in |
6) | Multiple stacks. |
K = H ´ V ´ T
Where:
K = | a parameter accounting for relative influence of stack height and plume rise; |
H = | physical stack height (meters); |
V = | stack gas flow rate ( |
T = | exhaust temperature (degrees K). |
7) | Criteria for facilities not eligible for screening limits. If any criteria below are met, the Tier I (and Tier II) screening limits do not apply. Owners and operators of such facilities |
A) | The device is located in a narrow valley less than one kilometer wide; |
B) | The device has a stack taller than 20 meters and is located such that the terrain rises to the physical height within one kilometer of the facility; |
C) | The device has a stack taller than 20 meters and is located within five kilometers of a shoreline of a large body of water such as an ocean or large lake; or |
D) | The physical stack height of any stack is less than 2.5 times the height of any building within five building heights or five projected building widths of the stack and the distance from the stack to the closest boundary is within five building heights or five projected building widths of the associated building. |
8) | Implementation. The feed rate of metals in each feedstream must be monitored to ensure that the feed rate screening limits are not exceeded. |
c) | Tier II emission rate screening limits. Emission rate screening limits are specified in |
1) | Noncarcinogenic metals. The emission rates of noncarcinogenic metals must not exceed the screening limits specified in |
2) | Carcinogenic metals. The emission rates of carcinogenic metals must not exceed values derived from the screening limits specified in |
whereWhere:
S Ai/Ei | means the sum of the values of A/E for each metal “i,” |
n = | number of carcinogenic metals. |
Ai = | the actual emission rate to the device for metal “i.” |
Ei = | the emission rate screening limit provided by |
3) | Implementation. The emission rate limits must be implemented by limiting feed rates of the individual metals to levels during the trial burn (for new facilities or an interim status facility applying for a permit) or the compliance test (for interim status facilities). The feed rate averaging periods are the same as provided by subsections (b)(1)(A), (b)(1)(B), and (b)(2)(B) of this Section. The feed rate of metals in each feedstream must be monitored to ensure that the feed rate limits for the feedstreams specified under Sections 726.202 or 726.203 are not exceeded. |
4) | Definitions and limitations. The definitions and limitations provided by subsection (b) of this Section and 726.200(g) for the following terms also apply to the Tier II emission rate screening limits provided by this subsection (c): TESH, good engineering practice stack height, terrain type, land use, and criteria for facilities not eligible to use the screening limits. |
5) | Multiple stacks. |
A) | |
B) | The worst-case stack is determined by procedures provided in subsection (b)(6) of this Section. |
C) | For each metal, the total emissions of the metal from those stacks must not exceed the screening limit for the worst-case stack. |
d) | Tier III site-specific risk assessment. The requirements of this subsection (d) apply to facilities complying with either the Tier III or Adjusted Tier I except where specified otherwise. |
1) | General. Conformance with the Tier III metals controls must be demonstrated by emissions testing to determine the emission rate for each metal. In addition, conformance with either Tier III or Adjusted Tier I metals controls must be demonstrated by air dispersion modeling to predict the maximum annual average off-site ground level concentration for each metal and a demonstration that acceptable ambient levels are not exceeded. |
2) | Acceptable ambient levels. |
3) | Carcinogenic metals. For the carcinogenic metals the sum of the ratios of the predicted maximum annual average off-site ground level concentrations (except that on-site concentrations must be considered if a person resides on site) to the RSD for all carcinogenic metals emitted must not exceed 1.0 as determined by the following equation: |
whereWhere:
S Pi/Ri | means the sum of the values of P/R for each metal “i,” |
n = | number of carcinogenic metals. |
Pi = | the predicted ambient concentration for metal i. |
Ri = | the RSD for metal i. |
4) | Noncarcinogenic metals. For the noncarcinogenic metals, the predicted maximum annual average off-site ground level concentration for each metal must not exceed the RAC. |
5) | Multiple stacks. Owners and operators of facilities with more than one on-site stack from a BIF, incinerator, or other thermal treatment unit subject to controls on metals emissions under a RCRA permit or interim status controls |
6) | Implementation. Under Tier III, the metals controls must be implemented by limiting feed rates of the individual metals to levels during the trial burn (for new facilities or an interim status facility applying for a permit) or the compliance test (for interim status facilities). The feed rate averaging periods are the same as provided by subsections (b)(1)(A), (b)(1)(B), and (b)(2)(B) of this Section. The feed rate of metals in each feedstream must be monitored to ensure that the feed rate limits for the feedstreams specified under Sections 726.202 or 726.203 are not exceeded. |
e) | Adjusted Tier I feed rate screening limits. The owner or operator may adjust the feed rate screening limits provided by |
f) | Alternative implementation approaches. |
1) | Pursuant to subsection (f)(2) of this Section the Agency |
2) | The emission limits provided by subsection (d) of this Section must be determined as follows: |
A) | For each noncarcinogenic metal, by back-calculating from the RAC provided in |
B) | For each carcinogenic metal by the following methods: |
i) | |
ii) | If more than one carcinogenic metal is emitted, by selecting an emission limit for each carcinogenic metal not to exceed the emission rate determined by subsection (f)(2)(B)(i) of this Section, such that the sum for all carcinogenic metals of the ratios of the selected emission limit to the emission rate determined by that subsection does not exceed 1.0. |
g) | Emission testing. |
1) | General. Emission testing for metals must be conducted using Method 0060, “Determinations of Metals in Stack Emissions,” USEPA Publication SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111. |
2) | Hexavalent chromium. Emissions of chromium are assumed to be hexavalent chromium unless the owner or operator conducts emissions testing to determine hexavalent chromium emissions using procedures prescribed in Method 0061, “Determination of Hexavalent Chromium Emissions from Stationary Sources,” USEPA Publication SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111. |
h) | Dispersion modeling. Dispersion modeling required under this Section must be conducted according to methods recommended in 40 CFR 51, appendix W (“Guideline on Air Quality Models (Revised)” (1986) and its supplements), the “Hazardous Waste Combustion Air Quality Screening Procedure” described in |
i) | Enforcement. For the purposes of permit enforcement, compliance with the operating requirements specified in the permit (under Section 726.202) will be regarded as compliance with this Section. However, evidence that compliance with those permit conditions is insufficient to ensure compliance with the requirements of this Section is “information” justifying modification or revocation and re-issuance of a permit under 35 Ill. Adm. Code 703.270 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.207 | Standards to Control HCl and Chlorine Gas Emissions |
a) | General. The owner or operator |
b) | Screening limits. |
1) | Tier I feed rate screening limits. Feed rate screening limits are specified for total chlorine in |
2) | Tier II emission rate screening limits. Emission rate screening limits for HCl and chlorine gas are specified in |
3) | Definitions and limitations. The definitions and limitations provided by |
4) | Multiple stacks. Owners and operators of facilities with more than one on-site stack from a BIF, incinerator or other thermal treatment unit subject to controls on HCl or chlorine gas emissions under a RCRA permit or interim status controls |
A) | The worst-case stack is determined by procedures provided in Section 726.206(b)(6). |
B) | Under Tier I, the total feed rate of chlorine and chloride to all subject devices must not exceed the screening limit for the worst-case stack. |
C) | Under Tier II, the total emissions of HCl and chlorine gas from all subject stacks must not exceed the screening limit for the worst-case stack. |
c) | Tier III site-specific risk assessments. |
1) | General. Conformance with the Tier III controls must be demonstrated by emissions testing to determine the emission rate for HCl and chlorine gas, air dispersion modeling to predict the maximum annual average off-site ground level concentration for each compound, and a demonstration that acceptable ambient levels are not exceeded. |
2) | Acceptable ambient levels. |
3) | Multiple stacks. Owners and operators of facilities with more than one on-site stack from a BIF, incinerator, or other thermal treatment unit subject to controls on HCl or chlorine gas emissions under a RCRA permit or interim status controls |
d) | Averaging periods. The HCl and chlorine gas controls are implemented by limiting the feed rate of total chlorine and chloride in all feedstreams, including hazardous waste, fuels, and industrial furnace feed stocks. Under Tier I, the feed rate of total chlorine and chloride is limited to the Tier I Screening Limits. Under Tier II and Tier III, the feed rate of total chlorine and chloride is limited to the feed rates during the trial burn (for new facilities or an interim status facility applying for a permit) or the compliance test (for interim status facilities). The feed rate limits are based on either of the following: |
1) | An hourly rolling average, as defined in |
2) | An instantaneous basis not to be exceeded at any time. |
e) | Adjusted Tier I feed rate screening limits. The owner or operator may adjust the feed rate screening limit provided by |
f) | Emissions testing. Emissions testing for HCl and chlorine gas (Cl2) must be conducted using the procedures described in Method 0050 or 0051, USEPA Publication SW-846, incorporated by reference in 35 Ill. Adm. Code 720.111. |
g) | Dispersion modeling. Dispersion modeling must be conducted according to the provisions of Section 726.206(h). |
h) | Enforcement. For the purposes of permit enforcement, compliance with the operating requirements specified in the permit (under Section 726.202) will be regarded as compliance with this Section. However, evidence that compliance with those permit conditions is insufficient to ensure compliance with the requirements of this Section is “information” justifying modification or revocation and re-issuance of a permit under 35 Ill. Adm. Code 703.270 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.208 | Small |
a) | Exempt quantities. |
1) | The quantity of hazardous waste burned in a device for a calendar month does not exceed the limits provided in the Table A based on the TESH, as defined in |
2) | The maximum hazardous waste firing rate does not exceed at any time |
3) | The hazardous waste has a minimum heating value of 5,000 Btu/lb, as generated; and |
4) | The hazardous waste fuel does not contain (and is not derived from) USEPA |
b) | Mixing with nonhazardous fuels. If hazardous waste fuel is mixed with a nonhazardous fuel, the quantity of hazardous waste before such mixing is used to comply with subsection (a) |
c) | Multiple stacks. If an owner or operator burns hazardous waste in more than one on-site BIF exempt under this Section, the quantity limits provided by subsection (a)(1) |
SUM(Ci/Li) ≤ 1.0
whereWhere:
the sum of the values of X for each stack i, from i = 1 to n. | |
n means the number of stacks; | |
Actual Quantity Burned means the waste quantity burned per month in device “i.” | |
Allowable Quantity Burned means the maximum allowable exempt quantity for stack “i” from Table A. | |
BOARD NOTE: Hazardous wastes that are subject to the special requirements for small quantity generators under 35 Ill. Adm. Code 721.105 may be burned in an off-site device under the exemption provided by Section 726.208, but must be included in the quantity determination for the exemption.
d) | Notification requirements. The owner or operator of facilities qualifying for the small quantity burner exemption under this Section |
1) | The combustion unit is operating as a small quantity burner of hazardous waste; |
2) | The owner and operator are in compliance with the requirements of this Section; and |
3) | The maximum quantity of hazardous waste that the facility is allowed to burn per month as provided by Section 726.208(a)(1). |
e) | Recordkeeping requirements. The owner or operator |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.209 | Low |
a) | Waiver of DRE standard. The DRE standard of Section 726.204(a) does not apply if the BIF is operated in conformance with subsection (a)(1) |
1) | The device must be operated as follows: |
A) | A minimum of 50 percent of fuel fired to the device must be fossil fuel, fuels derived from fossil fuel, tall oil, or, if approved by the Agency on a case-by-case basis, other nonhazardous fuel with combustion characteristics comparable to fossil fuel. Such fuels are termed “primary fuel” for purposes of this Section. (Tall oil is a fuel derived from vegetable and rosin fatty acids.) The 50 percent primary fuel firing rate must be determined on a total heat or mass input basis, whichever results in the greater mass feed rate of primary fuel fired; |
B) | Primary fuels and hazardous waste fuels must have a minimum as-fired heating value of 8,000 Btu/lb; |
C) | The hazardous waste is fired directly into the primary fuel flame zone of the combustion chamber; and |
D) | The device operates in conformance with the CO controls provided by Section 726.204(b)(1). Devices subject to the exemption provided by this Section are not eligible for the alternative CO controls provided by Section 726.204(c). |
2) | Procedures to demonstrate that the hazardous waste burning will not pose unacceptable adverse public health effects are as follows: |
A) | Identify and quantify those nonmetal compounds listed in Appendix H to 35 Ill. Adm. Code 721 |
B) | Calculate reasonable, worst case emission rates for each constituent identified in subsection (a)(2)(A) |
C) | For each constituent identified in subsection (a)(2)(A) |
i) | Dispersion modeling must be conducted using methods specified in Section 726.206(h). |
ii) | |
D) | Ground level concentrations of constituents predicted under subsection (a)(2)(C) |
i) | For the noncarcinogenic compounds listed in Appendix D, the levels established in Appendix D; |
ii) | For the carcinogenic compounds listed in Appendix E: |
SUM(Ai/Li) £ 1.0
whereWhere:
n means the number of carcinogenic compounds; | |
Actual ground level concentration of carcinogen “i.” | |
Level established in Appendix E for carcinogen “i”; and | |
iii) | For constituents not listed in Appendix D or E, 0.1 |
b) | Waiver of particular matter standard. The PM standard of Section 726.205 does not apply if the following occur: |
1) | The DRE standard is waived under subsection (a) |
2) | The owner or operator complies with the Tier I, or adjusted Tier I, metals feed rate screening limits provided by Section 726.206(b) or (e). |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.210 | Waiver of DRE |
Boilers that operate under the special requirements of this Section, and that do not burn hazardous waste containing (or derived from) USEPA Hazardous Waste Nos. hazardous waste numbers F020, F021, F022, F023, F026, or F027, are considered to be in conformance with the DRE standard of Section 726.204(a), and a trial burn to demonstrate DRE is waived. When burning hazardous waste:
a) | A minimum of 50 percent of fuel fired to the devices must be fossil fuel, fuels derived from fossil fuel, tall oil, or, if approved by the Agency on a case-by-case basis, other nonhazardous fuel with combustion characteristics comparable to fossil fuel. Such fuels are termed “primary fuel” for purposes of this Section. (Tall oil is a fuel derived from vegetable and rosin fatty acids.) The 50 percent primary fuel firing rate must be determined on a total heat or mass input basis, whichever results in the greater mass feed rate of primary fuel fired; |
b) | Boiler load must not be less than 40 percent. Boiler load is the ratio at any time of the total heat input to the maximum design heat input; |
c) | Primary fuels and hazardous waste fuels must have a minimum as-fired heating value of 8,000 Btu/lb, and each material fired in a burner where hazardous waste is fired must have a heating value of at least 8,000 Btu/lb, |
d) | The device must operate in conformance with the CO standard provided by Section 726.204(b)(1). Boilers subject to the waiver of the DRE trial burn provided by this Section are not eligible for the alternative CO standard provided by Section 726.204(c); |
e) | The boiler must be a water tube type boiler that does not feed fuel using a stoker or stoker type mechanism; and |
f) | The hazardous waste must be fired directly into the primary fuel flame zone of the combustion chamber with an air or steam atomization firing system, mechanical atomization system or a rotary cup atomization system under the following conditions: |
1) | Viscosity. The viscosity of the hazardous waste fuel |
2) | Particle size. When a high pressure air or steam atomizer, low pressure atomizer or mechanical atomizer is used, |
3) | Mechanical atomization systems. Fuel pressure within a mechanical atomization system and fuel flow rate must be maintained within the design range taking into account the viscosity and volatility of the fuel; |
4) | Rotary cup atomization systems. Fuel flow rate through a rotary cup atomization system must be maintained within the design range taking into account the viscosity and volatility of the fuel. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.211 | Standards for |
a) | Applicability. The regulations in this Section apply to owners and operators of BIFs subject to |
b) | Definitions. |
1) | When used in this Section, |
“Direct transfer equipment” means any device (including but not limited to, such devices as piping, fittings, flanges, valves and pumps) that is used to distribute, meter or control the flow of hazardous waste between a container (i.e., transport vehicle) and a BIF.
“Container” means any portable device in which hazardous waste is transported, stored, treated, or otherwise handled, and includes transport vehicles that are containers themselves (e.g., tank trucks, tanker-trailers, and rail tank cars) and containers placed on or in a transport vehicle.
2) | This Section references several requirements provided in Subparts I and J of 35 Ill. Adm. Code 724 and Subparts I and J of 35 Ill. Adm. Code 725 |
c) | General operating requirements. |
1) | No direct transfer of a pumpable hazardous waste must be conducted from an open-top container to a BIF. |
2) | Direct transfer equipment used for pumpable hazardous waste must always be closed, except when necessary to add or remove the waste, and must not be opened, handled, or stored in a manner that could cause any rupture or leak. |
3) | The direct transfer of hazardous waste to a BIF must be conducted so that it does not do any of the following: |
A) | Generate extreme heat or pressure, fire, explosion, or violent reaction; |
B) | Produce uncontrolled toxic mists, fumes, dusts, or gases in sufficient quantities to threaten human health; |
C) | Produce uncontrolled flammable fumes or gases in sufficient quantities to pose a risk of fire or explosions; |
D) | Damage the structural integrity of the container or direct transfer equipment containing the waste; |
E) | Adversely affect the capability of the BIF to meet the standards provided by Sections 726.204 through 726.207; or |
F) | Threaten human health or the environment. |
4) | Hazardous waste must not be placed in direct transfer equipment, if it could cause the equipment or its secondary containment system to rupture, leak, corrode, or otherwise fail. |
5) | The owner or operator of the facility |
A) | Spill prevention controls (e.g., check valves, dry discount couplings, etc.); and |
B) | Automatic waste feed cutoff to use if a leak or spill occurs from the direct transfer equipment. |
d) | Areas where direct transfer vehicles (containers) are located. Applying the definition of container under this Section, owners and operators |
1) | The containment requirements of 35 Ill. Adm. Code 724.275; |
2) | The use and management requirements of Subpart I of 35 Ill. Adm. Code 725 |
3) | The closure requirements of 35 Ill. Adm. Code 724.278. |
e) | Direct transfer equipment. Direct transfer equipment must meet the following requirements: |
1) | Secondary containment. Owners and operators |
A) | For all new direct transfer equipment, prior to their being put into service; and |
B) | For existing direct transfer equipment, by August 21, 1993. |
2) | Requirements prior to meeting secondary containment requirements. |
A) | For existing direct transfer equipment that does not have secondary containment, the owner or operator |
B) | This assessment must determine whether the direct transfer equipment is adequately designed and has sufficient structural strength and compatibility with the |
i) | Design |
ii) | Hazardous characteristics of the |
iii) | Existing corrosion protection measures; |
iv) | Documented age of the equipment, if available, (otherwise, an estimate of the age); and |
v) | Results of a leak test or other integrity examination such that the effects of temperature variations, vapor pockets, cracks, leaks, corrosion and erosion are accounted for. |
C) | If, as a result of the assessment specified above, the direct transfer equipment is found to be leaking or unfit for use, the owner or operator |
3) | Inspections and recordkeeping. |
A) | The owner or operator |
i) | Overfill/spill control equipment (e.g., waste-feed cutoff systems, bypass systems, and drainage systems) to ensure that it is in good working order; |
ii) | The above ground portions of the direct transfer equipment to detect corrosion, erosion, or releases of waste (e.g., wet spots, dead vegetation, etc.); and |
iii) | Data gathered from monitoring equipment and leak-detection equipment, (e.g., pressure and temperature gauges) to ensure that the direct transfer equipment is being operated according to its design. |
B) | The owner or operator |
C) | Records of inspections made under this subsection must be maintained in the operating record at the facility, and available for inspection for at least |
4) | Design and installation of new ancillary equipment. Owners and operators |
5) | Response to leaks or spills. Owners and operators |
6) | Closure. Owners and operators |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.212 | Regulation of Residues |
A residue derived from the burning or processing of hazardous waste in a BIF is not excluded from the definition of a hazardous waste under 35 Ill. Adm. Code 721.104(b)(4), (b)(7), or (b)(8), unless the device and the owner or operator meet the following requirements:
a) | The device meets the following criteria: |
1) | Boilers. Boilers must burn at least |
2) | Ore or mineral furnaces. Industrial furnaces subject to 35 Ill. Adm. Code 721.104(b)(7) must process at least |
3) | Cement kilns. Cement kilns must process at least |
b) | The owner or operator demonstrates that the hazardous waste does not significantly affect the residue by demonstrating conformance with either of the following criteria: |
1) | Comparison of waste-derived residue with normal residue. The waste-derived residue must not contain Appendix H to 35 Ill. Adm. Code 721 |
A) | Normal residue. Concentrations of toxic constituents of concern in normal residue must be determined based on analyses of a minimum of 10 samples representing a minimum of 10 days of operation. Composite samples may be used to develop a sample for analysis provided that the compositing period does not exceed 24 hours. The upper tolerance limit (at |
B) | Waste-derived residue. Waste derived residue must be sampled and analyzed as often as necessary to determine whether the residue generated during each 24-hour period has concentrations of toxic constituents that are higher than the concentrations established for the normal residue under subsection (b)(1)(A) of this Section. If so, hazardous waste burning has significantly affected the residue and the residue is not excluded from the definition of “hazardous waste.” |
2) | Comparison of waste-derived residue concentrations with health-based limits. |
A) | Nonmetal constituents. The concentration of each nonmetal toxic constituent of concern (specified in subsection (b)(1) of this Section) in the waste-derived residue must not exceed the health-based level specified in Appendix G of this Part, or the level of detection (using analytical procedures prescribed in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” |
BOARD NOTE: In a note to corresponding 40 CFR 266.112(b)(2)(i) (1999) (2002), as amended at 64 Fed. Reg. 53076 (Sept. 30, 1999), USEPA stated as follows:
The administrative stay, under the condition that the owner or operator complies with alternative levels defined as the land disposal restriction limits specified in 35 Ill. Adm. Code 728.143 for F039 nonwastewaters, remains in effect until further administrative action is taken and notice is published in the Federal Register and the Code of Federal Regulations.
Under Section 3006(b) and (g) of RCRA, 42 USC 6926(b) and (g), federal amendments do not go into effect in Illinois until the State of Illinois incorporates them into the State program. This applies unless the authority under which USEPA adopted the amendments is the Hazardous and Solid Waste Amendments of 1984 (HSWA), in which case the federal amendments become effective in Illinois on their federal effective date.
B) | Metal constituents. The concentration of metals in an extract obtained using the TCLP test must not exceed the levels specified in Appendix G of this Part; |
C) | Sampling and analysis. Wastewater-derived residue must be sampled and analyzed as often as necessary to determine whether the residue generated during each 24-hour period has concentrations of toxic constituents that are higher than the health-based levels. Concentrations of concern in the wastewater-derived residue must be determined based on analysis of one or more samples obtained over a 24-hour period. Multiple samples may be analyzed, and multiple samples may be taken to form a composite for analysis provided that the sampling period does not exceed 24 hours. If more than one sample is analyzed to characterize waste-derived residues generated over a 24-hour period, the concentration of each toxic constituent is the arithmetic mean of the concentrations of the samples. No results can be disregarded; and |
c) | Records sufficient to document compliance with the provisions of this Section must be retained until closure of the BIF unit. At a minimum, the following must be recorded: |
1) | Levels of constituents in Appendix H to 35 Ill. Adm. Code 721 |
2) | If the waste-derived residue is compared with normal residue under subsection (b)(1) of this Section: |
A) | The levels of constituents in Appendix H to 35 Ill. Adm. Code 721 |
B) | Data and information, including analyses of samples as necessary, obtained to determine if changes in raw materials or fuels would reduce the concentration of toxic constituents of concern in the normal residue. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.219 | Extensions of Time |
The owner or operator may request a case-by-case extension of time to extend any time limit provided by Section 726.203(c). The operator shall must file a petition for a RCRA variance pursuant to 35 Ill. Adm. Code 104. The Board will grant the variance if compliance with the time limit is not practicable for reasons beyond the control of the owner or operator.
a) | In granting an extension, the Board will apply conditions as the facts warrant to ensure timely compliance with the requirements of Section 726.203 and that the facility operates in a manner that does not pose a hazard to human health and the environment; |
b) | When an owner and operator requests an extension of time to enable the facility to comply with the alternative hydrocarbon provisions of Section 726.204(f) and obtain a RCRA permit because the facility cannot meet the HC limit of Section 726.204(c): |
1) | The Board will do the following, in considering whether to grant the extension: |
A) | Determine whether the owner and operator have submitted in a timely manner a complete Part B permit application that includes information required under 35 Ill. Adm. Code 703.208(b); and |
B) | Consider whether the owner and operator have made a good faith effort to certify compliance with all other emission controls, including the controls on dioxins and furans of Section 726.204(e) and the controls on PM, metals and HCl/chlorine gas. |
2) | If an extension is granted, the Board will, as a condition of the extension, require the facility to operate under flue gas concentration limits on CO and HC that, based on available information, including information in the Part B permit application, are baseline CO and HC levels as defined by Section 726.204(f)(1). |
BOARD NOTE: Derived from 40 CFR 266.103(c)(7)(ii), adopted at 56 Fed. Reg. 7206, February 21, 1991; 56 Fed. Reg. 32688, July 17, 1991; and 57 Fed. Reg. 38566, August 25, 1992 (2002).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART M: MILITARY MUNITIONS
Section 726.300 | Applicability |
a) | The regulations in this Subpart M identify when military munitions become a solid waste, and, if these wastes are also hazardous under this Subpart M or 35 Ill. Adm. Code 721, the management standards that apply to these wastes. |
b) | Unless otherwise specified in this Subpart M, all applicable requirements in 35 Ill. Adm. Code 702, 703, 705, 720 through 726, and 728 apply to waste military munitions. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.301 | Definitions |
In addition to the definitions in 35 Ill. Adm. Code 720.110, the following definitions apply to this Subpart M:
“Active range” means a military range that is currently in service and is being regularly used for range activities.
“Chemical agents” and “chemical munitions” are defined as in the Department of Defense Authorization Act of 1986, 50 U.S.C. USC 1521(j)(1) (1997), incorporated by reference in 35 Ill. Adm. Code 720.111.
“Director” is as defined in 35 Ill. Adm. Code 702.110.
“Explosives or munitions emergency response specialist” is as defined in 35 Ill. Adm. Code 720.110.
“Explosives or munitions emergency” is as defined in 35 Ill. Adm. Code 720.110.
“Explosives or munitions emergency response” is as defined in 35 Ill. Adm. Code 720.110.
“Inactive range” means a military range that is not currently being used but which is still under military control and considered by the military to be a potential range area and which has not been put to a new use that is incompatible with range activities.
“Military” means the United States (U.S.) Department of Defense (DOD), the Armed Services, Coast Guard, National Guard, Department of Energy (DOE) or other parties under contract or acting as an agent for the foregoing who handle military munitions.
“Military munitions” is as defined in 35 Ill. Adm. Code 720.110.
“Military range” means designated land and water areas that are set aside; managed; and used to conduct research on, develop, test, and evaluate military munitions and explosives, other ordnance, or weapon systems or areas that are set aside, managed, and used to train military personnel in their use and handling. Ranges include firing lines and positions, maneuver areas, firing lanes, test pads, detonation pads, impact areas, and buffer zones with restricted access and exclusionary areas.
“Unexploded ordnance” or “UXO” means military munitions that have been primed, fused, armed, or otherwise prepared for action and that have been fired, dropped, launched, projected, or placed in such a manner as to constitute a hazard to operations, installation, personnel, or material and remain unexploded either by malfunction, design, or any other cause.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.302 | Definition of Solid Waste |
a) | A military munition is not a solid waste when any of the following situations describes the munition: |
1) | It is used for its intended purpose, including any of the following uses: |
A) | Use in training military personnel or explosives and munitions emergency response specialists (including training in proper destruction of unused propellant or other munitions); |
B) | Use in research, development, testing, and evaluation of military munitions, weapons, or weapon systems; or |
C) | Recovery, collection, and on-range destruction of unexploded ordnance and munitions fragments during range clearance activities at active or inactive ranges. However, “use for intended purpose” does not include the on-range disposal or burial of unexploded ordnance and contaminants when the burial is not a result of product use. |
2) | It is an unused munition, or component thereof, it is being repaired, reused, recycled, reclaimed, disassembled, reconfigured, or otherwise subjected to materials recovery activities, unless such activities involve use constituting disposal, as defined in 35 Ill. Adm. Code 721.102(c)(1), or it is burned for energy recovery, as defined in 35 Ill. Adm. Code 721.102(c)(2). |
b) | An unused military munition is a solid waste when any of the following occurs: |
1) | The munition is abandoned by being disposed of, burned, detonated (except during intended use as specified in subsection (a) of this Section), incinerated, or treated prior to disposal; |
2) | The munition is removed from storage in a military magazine or other storage area for the purpose of being disposed of, burned, incinerated, or treated prior to disposal; |
3) | The munition is deteriorated or damaged (e.g., the integrity of the munition is compromised by cracks, leaks, or other damage) to the point that it cannot be put into serviceable condition, and cannot reasonably be recycled or used for other purposes; or |
4) | The munition has been declared a solid waste by an authorized military official. |
c) | A used or fired military munition is a solid waste when either of the following |
1) | The munition is transported off-range or from the site of use (where the site of use is not a range) for the purpose of storage, reclamation, treatment, disposal, or treatment prior to disposal; or |
2) | The munition is recovered, collected, and then disposed of by burial or landfilling either on or off a range. |
d) | For purposes of RCRA section 1004(27) (42 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.303 | Standards Applicable to the Transportation of Solid Waste Military Munitions |
a) | Criteria for hazardous waste regulation of waste non-chemical military munitions in transportation. |
1) | Waste military munitions that are being transported and which exhibit a hazardous waste characteristic or which are listed as hazardous waste under 35 Ill. Adm. Code 721 are subject to regulation under 35 Ill. Adm. Code 702, 703, 705, 720 through 726, and 728, unless the munitions meet all the following conditions: |
A) | The waste military munitions are not chemical agents or chemical munitions; |
B) | The waste military munitions are transported in accordance with the Department of Defense shipping controls applicable to the transport of military munitions; |
C) | The waste military munitions are transported from a military-owned or -operated installation to a military-owned or -operated treatment, storage, or disposal facility; and |
D) | The transporter of the waste |
2) | If any waste military munitions shipped under subsection (a)(1) of this Section are not received by the receiving facility within 45 days |
3) | The conditional exemption from regulation as hazardous waste in subsection (a)(1) of this Section |
4) | The conditional exemption in subsection (a)(1) of this Section applies only so long as all of the conditions in subsection (a)(1) of this Section are met. |
b) | Reinstatement of conditional exemption. |
1) | If any waste military munition loses its conditional exemption under subsection (a)(1) of this Section, the transporter may file with the Agency an application for reinstatement of the conditional exemption from hazardous waste transportation regulation with respect to such munition as soon as the munition is returned to compliance with the conditions of subsection (a)(1) of this Section. |
2) | If the Agency finds that reinstatement of the conditional exemption is appropriate, it |
3) | The Agency may terminate a conditional exemption reinstated by default under the preceding sentence in writing if it finds that reinstatement is inappropriate based on its consideration of the factors set forth in subsection (b)(2) of this Section. If the Agency terminates a reinstated exemption, it |
4) | The applicant under this subsection (b) may appeal the |
c) | Amendments to DOD shipping controls. The Department of Defense shipping controls applicable to the transport of military munitions referenced in subsection (a)(1)(B) of this Section are Government Bill of Lading (GBL) (GSA Standard Form 1109), Requisition Tracking Form (DD Form 1348), the Signature and Talley Record (DD Form 1907), Special Instructions for Motor Vehicle Drivers (DD Form 836), and the Motor Vehicle Inspection Report (DD Form 626) in effect on November 8, 1995, incorporated by reference in 35 Ill. Adm. Code 720.111. |
BOARD NOTE: Corresponding federal provision 40 CFR 266.203(c), as added at 62 Fed. Reg. 6655 (Feb. 12, 1997), further provides as follows: “Any amendments to the Department of Defense shipping controls shall must become effective for purposes of paragraph (a)(1) of this section on the date the Department of Defense publishes notice in the Federal Register that the shipping controls referenced in paragraph (a)(1)(ii) of this section have been amended.” (40 CFR 266.203(a)(1)(ii) corresponds with 35 Ill. Adm. Code 726.303(a)(1)(B).) Section 5-75 of the Illinois Administrative Procedure Act [5 ILCS 100/5-75] prohibits the incorporation of later amendments and editions by reference. For this reason, interested members of the regulated community will need to notify the Board of any amendments of these references before those amendments can become effective under Illinois law.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.304 | Standards Applicable to Emergency Responses |
Explosives and munitions emergencies involving military munitions or explosives are subject to 35 Ill. Adm. Code 722.110(i), 723.110(e), 724.101(g)(8), 725.101(c)(11), and 703.121(c)(3), or, alternatively, to 35 Ill. Adm. Code 703.221.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.305 | Standards Applicable to the Storage of Solid Waste Military Munitions |
a) | Criteria for hazardous waste regulation of waste non-chemical military munitions in storage. |
1) | Waste military munitions in storage that exhibit a hazardous waste characteristic or are listed as hazardous waste under 35 Ill. Adm. Code 721 are listed or identified as a hazardous waste (and thus are subject to regulation under 35 Ill. Adm. Code 702, 703, 705, 720 through 726, 728, 733, and 739), unless all the following conditions are met: |
A) | The waste military munitions are not chemical agents or chemical munitions; |
B) | The waste military munitions must be subject to the jurisdiction of the Department of Defense Explosives Safety Board (DDESB); |
C) | The waste military munitions must be stored in accordance with the DDESB storage standards applicable to waste military munitions; |
D) | Within 90 days of when a storage unit is first used to store waste military munitions, the owner or operator |
E) | The owner or operator |
F) | The owner or operator |
G) | Access to the stored waste military munitions must be limited to appropriately trained and authorized personnel. |
2) | The conditional exemption in subsection (a)(1) of this Section from regulation as hazardous waste |
3) | The conditional exemption in subsection (a)(1) of this Section applies only so long as all of the conditions in subsection (a)(1) of this Section are met. |
b) | Notice of termination of waste storage. The owner or operator |
c) | Reinstatement of conditional exemption. |
1) | If any waste military munition loses its conditional exemption under subsection (a)(1) of this Section, an application may be filed with the Agency for reinstatement of the conditional exemption from hazardous waste storage regulation with respect to such munition as soon as the munition is returned to compliance with the conditions of subsection (a)(1) of this Section. |
2) | If the Agency finds that reinstatement of the conditional exemption is appropriate, it |
3) | The Agency may terminate a conditional exemption reinstated by default under the preceding sentence in writing if it finds that reinstatement is inappropriate based on its consideration of the factors set forth in subsection (c)(2) of this Section. If the Agency terminates a reinstated exemption, it |
4) | The applicant under this subsection (c) may appeal the |
d) | Waste chemical munitions. |
1) | Waste military munitions that are chemical agents or chemical munitions and |
2) | Waste military munitions that are chemical agents or chemical munitions and that exhibit a hazardous waste characteristic or are listed as hazardous waste under 35 Ill. Adm. Code 721, are not subject to the storage prohibition in RCRA section 3004(j), codified at 35 Ill. Adm. Code 728.150. |
e) | Amendments to DDESB storage standards. The DDESB storage standards applicable to waste military munitions, referenced in subsection (a)(1)(C) of this Section, are DOD 6055.9-STD (“DOD Ammunition and Explosive Safety Standards”), in effect on November 8, 1995, incorporated by reference in 35 Ill. Adm. Code 720.111. |
BOARD NOTE: Corresponding federal provision 40 CFR 266.205(e), as added at 62 Fed. Reg. 6656 (Feb. 12, 1997), further provides as follows: “Any amendments to the DDESB storage standards shall must become effective for purposes of paragraph (a)(1) of this section on the date the Department of Defense publishes notice in the Federal Register that the DDESB standards referenced in paragraph (a)(1) of this section have been amended.” Section 5-75 of the Illinois Administrative Procedure Act [5 ILCS 100/5-75] prohibits the incorporation of later amendments and editions by reference. For this reason, interested members of the regulated community will need to notify the Board of any amendments of these references before those amendments can become effective under Illinois law.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART N: CONDITIONAL EXEMPTION FOR LOW-LEVEL MIXED WASTE STORAGE, TREATMENT, TRANSPORTATION AND DISPOSAL
Section 726.310 | Definitions |
Terms are defined as follows for the purposes of this Subpart N:
“CERCLA reportable quantity” means that quantity of a particular substance designated by USEPA in 40 CFR 302.4 pursuant to the Comprehensive Environmental Response, Compensation and Liability Act of 1980 (42 USC 9601 et seq.) for which notification is required upon a release to the environment.
“Certified delivery” means certified mail with return receipt requested, equivalent courier service, or other means that provides the sender with a receipt confirming delivery.
“Director” is as defined in 35 Ill. Adm. Code 702.110.
“DNS” means the Department of Nuclear Safety, the State of Illinois agency charged with regulating source, by-product, and special nuclear material in Illinois in accordance with an agreement between the State and the federal Nuclear Regulatory Commission (NRC) under section 274(b) of the federal Atomic Energy Act of 1954, as amended (42 USC 2021(b)).
BOARD NOTE: In addition to the materials regulated under this Part, the DNS regulates radioactive materials under the Radiation Protection Act of 1990 [420 ILCS 40] that are not licensed by the federal NRC. For the purposes of notices to the DNS required under this Subpart N, the address is as follows:
Illinois Department of Nuclear Safety
1035 Outer Park Drive
Springfield, Illinois 62704
“Eligible naturally occurring or accelerator-produced radioactive material” means naturally occurring or accelerator-produced radioactive material (NARM) that is eligible for a transportation and disposal conditional exemption. It is a NARM waste that contains RCRA hazardous waste, meets the waste acceptance criteria of, and is allowed by State NARM regulations to be disposed of at a low-level radioactive waste disposal facility (LLRWDF) licensed in accordance with 10 CFR 61, DNS regulations, or the equivalent regulations of a licensing agency in another state.
BOARD NOTE: The Illinois DNS regulations are codified at 32 Ill. Adm. Code: Chapter II, Subchapter Subchapters b and d.
“Exempted waste” means a waste that meets the eligibility criteria in Section 726.325 and all of the conditions in Section 726.330 or a waste that meets the eligibility criteria in Section 726.410 and which complies with all the conditions in Section 726.415. Such waste is conditionally exempted from the regulatory definition of hazardous waste in 35 Ill. Adm. Code 721.103.
“Hazardous waste” means hazardous waste as defined in 35 Ill. Adm. Code 721.103.
“Land disposal restriction treatment standards” or “LDR treatment standards” means treatment standards, under 35 Ill. Adm. Code 728, that a RCRA hazardous waste must meet before it can be disposed of in a RCRA hazardous waste land disposal unit.
“License” means a license issued by the federal NRC or the Illinois DNS to a user that manages radionuclides regulated by the federal NRC or the Illinois DNS under authority of the Atomic Energy Act of 1954, as amended (42 USC 2014 et seq.) or the Radiation Protection Act of 1990 [420 ILCS 40].
“Low-level mixed waste” or “LLMW” is a waste that contains both low-level radioactive waste and RCRA hazardous waste.
“Low-level radioactive waste” or “LLRW” is a radioactive waste that contains source, by-product, or special nuclear material and which is not classified as high-level radioactive waste, transuranic waste, spent nuclear fuel, or by-product material, as defined in section 11(e)(2) of the Atomic Energy Act of 1954 (42 USC 2014(e)(2)). (See also the NRC definition of waste at 10 CFR 61.2.)
BOARD NOTE: This definition differs from the similar definitions of low-level radioactive waste in the Illinois Low-Level Radioactive Waste Management Act [420 ILCS 20/3(k)], the Central Midwest Interstate Low-Level Radioactive Waste Compact Act [45 ILCS 140/1, Article II(k)], and 32 Ill. Adm. Code 606.20(g) of the DNS regulations. Those basically define low-level radioactive waste as radioactive waste that is not (1) high-level radioactive waste, (2) transuranic waste, (3) spent nuclear fuel, or (4) by-product material, as such are defined in section 11 of the federal Atomic Energy Act of 1954 (42 USC 2014).
“Mixed waste” means a waste that contains both RCRA hazardous waste and source, by-product, or special nuclear material subject to the Atomic Energy Act of 1954, as amended (42 USC 2014 et seq.).
BOARD NOTE: This definition differs from the similar definitions of mixed waste in the Illinois Low-Level Radioactive Waste Management Act [420 ILCS 20/3(l)] and 32 Ill. Adm. Code 606.20(h) of the DNS regulations. Those basically define mixed waste as containing both RCRA hazardous waste and low-level radioactive waste, as such is defined under Section 3(k) of the Illinois Low-Level Radioactive Waste Management Act [420 ILCS 20/3(k)].
“Naturally occurring or accelerator-produced radioactive material” or “NARM” means a radioactive material that fulfills one of the following conditions:
It is naturally occurring and it is not a source, by-product, or special nuclear material, as defined by the federal Atomic Energy Act (42 USC 2014 et seq.), or
It is produced by an accelerator.
BOARD NOTE: NARM is regulated by the State, under the Radiation Protection Act of 1990 [420 ILCS 40] and 32 Ill. Adm. Code: Chapter II, Subchapter Subchapters b and d, or by the federal Department of Energy (DOE), as authorized by the federal Atomic Energy Act (42 USC 2014 et seq.), under DOE regulations and orders.
“NRC” means the United States Nuclear Regulatory Commission.
BOARD NOTE: For the purposes of notices to the NRC required under this Subpart N, the address is as follows:
U.S. Nuclear Regulatory Commission, Region III
801 Warrenville Road
Lisle, Illinois 60532-4351
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.340 | Loss of a Storage and Treatment Conditional Exemption and Required Action |
a) | A generator’s LLMW will automatically lose the storage and treatment conditional exemption if the generator fails to meet any of the conditions specified in Section 726.330. When a generator’s LLMW loses the exemption, the generator must immediately manage that waste which failed the condition as RCRA hazardous waste, and the storage unit storing the LLMW immediately becomes subject to RCRA hazardous waste container or tank storage requirements. |
1) | If a generator fails to meet any of the conditions specified in Section 726.330, the generator must report to the Agency, the Illinois DNS, and the NRC in writing by certified delivery within 30 days after learning of the failure. The generator’s report must be signed by the generator’s authorized representative certifying that the information provided is true, accurate, and complete. This report must include the following: |
A) | The specific conditions that the generator failed to meet; |
B) | A description of the LLMW (including the waste name, hazardous waste codes and quantity) and storage location at the facility; and |
C) | The dates on which the generator failed to meet the conditions. |
2) | If the failure to meet any of the conditions may endanger human health or the environment, the generator must also immediately notify the Agency orally within 24 hours and follow up with a written notification within five days. A failure that may endanger human health or the environment may include, but is not limited to, discharge of a CERCLA reportable quantity or other leaking or exploding tanks or containers, or detection of radionuclides above background or hazardous constituents in the leachate collection system of a storage area. If the failure may endanger human health or the environment, the generator must follow the provisions of its emergency plan. |
b) | The Board may, by an order issued in an enforcement proceeding against the generator, terminate the generator’s conditional exemption for its LLMW, or require the generator to meet additional conditions to claim a conditional exemption, for serious or repeated noncompliance with any requirements of this Subpart N. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.345 | Reclaiming a Lost Storage and Treatment Conditional Exemption |
a) | A generator may reclaim a lost storage and treatment conditional exemption for its LLMW if the following conditions are fulfilled: |
1) | The generator again meets the conditions specified in Section 726.330; and |
2) | The generator sends the Agency a notice by certified delivery that the generator is reclaiming the exemption for its LLMW. The generator’s notice must be signed by its authorized representative certifying that the information contained in the generator’s notice is true, complete, and accurate. In its notice, the generator must do the following: |
A) | Explain the circumstances of each failure. |
B) | Certify that the generator has corrected each failure that caused it to lose the exemption for its LLMW and that the generator again meets all the conditions as of the date that the generator specifies. |
C) | Describe plans that the generator has implemented, listing specific steps that it has taken, to ensure that the conditions will be met in the future. |
D) | Include any other information that the generator wants the Agency to consider when it reviews the generator’s notice reclaiming the exemption. |
b) | The Agency may terminate a reclaimed conditional exemption if it determines, in writing, pursuant to Section 39 of the Act [415 ILCS 5/39], that the generator’s claim is inappropriate based on factors including, but not limited to, the following: the generator has failed to correct the problem; the generator explained the circumstances of the failure unsatisfactorily; or the generator failed to implement a plan with steps to prevent another failure to meet the conditions of Section 726.330. In reviewing a reclaimed conditional exemption under this Section, the Agency may add conditions to the exemption to ensure that waste management during storage and treatment of the LLMW will protect human health and the environment. Any Agency determination made pursuant to this subsection (b) is subject to review by the Board pursuant to Section 40 of the Act [415 ILCS 5/40]. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.360 | Applicability of Closure Requirements to Storage Units |
An interim status and permitted storage unit that has been used to store only LLMW prior to April 22, 2002 and which, after that date, stores only LLMW that becomes exempt under this subpart Subpart N, is not subject to the closure requirements of 35 Ill. Adm. Code 724 and 725. A storage unit (or portions of units) that has been used to store both LLMW and non-mixed hazardous waste prior to April 22, 2002 or which is used to store both after that date remain subject to closure requirements with respect to the non-mixed hazardous waste.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.420 | Treatment Standards for Eligible Waste |
A generator’s LLMW or eligible NARM waste must meet the applicable LDR treatment standards specified in Subpart D of 35 Ill. Adm. Code 728.Subpart D.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.455 | Loss of a Transportation and Disposal Conditional Exemption and Required Action |
a) | Any waste will automatically lose the transportation and disposal exemption if the generator fails to manage it in accordance with all of the conditions specified in Section 726.415. |
1) | When the generator fails to meet any of the conditions specified in Section 726.415 for any of its wastes, the generator must report to the Agency and the Illinois DNS, in writing by certified delivery, within 30 days after learning of the failure. The generator’s report must be signed by its authorized representative certifying that the information provided is true, accurate, and complete. This report must include the following: |
A) | The specific conditions that the generator failed to meet for the waste; |
B) | A description of the waste (including the waste name, hazardous waste codes and quantity) that lost the exemption; and |
C) | The dates on which the generator failed to meet the conditions for the waste. |
2) | If the failure to meet any of the conditions may endanger human health or the environment, the generator must also immediately notify the Agency orally within 24 hours and follow up with a written notification within |
b) | The Board may, by an order issued in an enforcement proceeding against the generator, terminate the generator’s ability to claim a conditional exemption for its waste, or require the generator to meet additional conditions to claim a conditional exemption, for serious or repeated noncompliance with any requirements of this Subpart N. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.460 | Reclaiming a Lost Transportation and Disposal Conditional Exemption |
a) | A generator may reclaim a lost transportation and disposal conditional exemption for a waste after the generator has received a return receipt confirming that the Agency and the Illinois DNS have received the generator’s notification of the loss of the exemption specified in Section 726.455(a) and if the following conditions are fulfilled: |
1) | The generator again meets the conditions specified in Section 726.415 for the waste; and |
2) | The generator sends a notice, by certified delivery, to the Agency that the generator is reclaiming the exemption for the waste. A generator’s notice must be signed by the generator’s authorized representative certifying that the information provided is true, accurate, and complete. The notice must include all of the following: |
A) | An explanation of the circumstances of each failure; |
B) | A certification that each failure that caused the generator to lose the exemption for the waste has been corrected and that the generator again meets all conditions for the waste as of the date the generator specifies; |
C) | A description of plans that the generator has implemented, listing the specific steps that the generator has taken, to ensure that conditions will be met in the future; and |
D) | Any other information that the generator wants the Agency to consider when the Agency reviews the generator’s notice reclaiming the exemption. |
b) | The Agency may terminate a reclaimed conditional exemption if it determines, in writing, pursuant to Section 39 of the Act [415 ILCS 5/39], that the generator’s claim is inappropriate based on factors including, but not limited to, the following: the generator has failed to correct the problem; the generator explained the circumstances of the failure unsatisfactorily; or the generator has failed to implement a plan with steps to prevent another failure to meet the conditions of Section 726.415. In reviewing a reclaimed conditional exemption under this Section, the Agency may add conditions to the exemption to ensure that transportation and disposal activities will protect human health and the environment. Any Agency determination made pursuant to this subsection (b) is subject to review by the Board pursuant to Section 40 of the Act [415 ILCS 5/40]. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.Appendix A | |
Tier I and Tier II Feed Rate and Emissions Screening Limits for Metals | |
I-A
Tier I and Tier II Feed Rate and Emissions Screening Limits for Noncarcinogenic Metals for Facilities in Noncomplex Terrain [Values for urban areas]
TESH (m) |
Antimony (g/hr) |
Barium (g/hr) |
Lead (g/hr) |
Mercury (g/hr) |
Silver (g/hr) |
Thallium (g/hr) |
4 |
60. |
10000. |
18. |
60. |
600. |
60. |
6 |
68. |
11000. |
20. |
68. |
680. |
68. |
8 |
76. |
13000. |
23. |
76. |
760. |
76. |
10 |
86. |
14000. |
26. |
86. |
860. |
86. |
12 |
96. |
17000. |
30. |
96. |
960. |
96. |
14 |
110. |
18000. |
34. |
110. |
1100. |
110. |
16 |
130. |
21000. |
36. |
130. |
1300. |
130. |
18 |
140. |
24000. |
43. |
140. |
1400. |
140. |
20 |
160. |
27000. |
46. |
160. |
1600. |
160. |
22 |
180. |
30000. |
54. |
180. |
1800. |
180. |
24 |
200. |
34000. |
60. |
200. |
2000. |
200. |
26 |
230. |
39000. |
68. |
230. |
2300. |
230. |
28 |
260. |
43000. |
78. |
260. |
2600. |
260. |
30 |
300. |
50000. |
90. |
300. |
3000. |
300. |
35 |
400. |
66000. |
110. |
400. |
4000. |
400. |
40 |
460. |
78000. |
140. |
460. |
4600. |
460. |
45 |
600. |
100000. |
180. |
600. |
6000. |
600. |
50 |
780. |
130000. |
230. |
780. |
7800. |
780. |
55 |
960. |
170000. |
300. |
960. |
9600. |
960. |
60 |
1200. |
200000. |
360. |
1200. |
12000. |
1200. |
65 |
1500. |
250000. |
430. |
1500. |
15000. |
1500. |
70 |
1700. |
280000. |
500. |
1700. |
17000. |
1700. |
75 |
1900. |
320000. |
580. |
1900. |
19000. |
1900. |
80 |
2200. |
360000. |
640. |
2200. |
22000. |
2200. |
85 |
2500. |
400000. |
760. |
2500. |
25000. |
2500. |
90 |
2800. |
460000. |
820. |
2800. |
28000. |
2800. |
95 |
3200. |
540000. |
960. |
3200. |
32000. |
3200. |
100 |
3600. |
600000. |
1100. |
3600. |
36000. |
3600. |
105 |
4000. |
680000. |
1200. |
4000. |
40000. |
4000. |
110 |
4600. |
780000. |
1400. |
4600. |
46000. |
4600. |
115 |
5400. |
860000. |
1600. |
5400. |
54000. |
5400. |
120 |
6000. |
1000000. |
1800. |
6000. |
60000. |
6000. |
I-B
Tier I and Tier II Feed Rate and Emissions Screening Limits for Noncarcinogenic Metals for Facilities in Noncomplex Terrain [Values for rural areas]
TESH (m) |
Antimony (g/hr) |
Barium (g/hr) |
Lead (g/hr) |
Mercury (g/hr) |
Silver (g/hr) |
Thallium (g/hr) |
4 |
31. |
5200. |
9.4 |
31. |
310. |
31. |
6 |
36. |
6000. |
11. |
36. |
360. |
36. |
8 |
40. |
6800. |
12. |
40. |
400. |
40. |
10 |
46. |
7800. |
14. |
46. |
460. |
46. |
12 |
58. |
9600. |
17. |
58. |
580. |
58. |
14 |
68. |
11000. |
21. |
68. |
680. |
68. |
16 |
86. |
14000. |
26. |
86. |
860. |
86. |
18 |
110. |
18000. |
32. |
110. |
1100. |
110. |
20 |
130. |
22000. |
40. |
130. |
1300. |
130. |
22 |
170. |
28000. |
50. |
170. |
1700. |
170. |
24 |
220. |
36000. |
64. |
220. |
2200. |
220. |
26 |
280. |
46000. |
82. |
280. |
2800. |
280. |
28 |
350. |
58000. |
100. |
350. |
3500. |
350. |
30 |
430. |
76000. |
130. |
430. |
4300. |
430. |
35 |
720. |
120000. |
210. |
720. |
7200. |
720. |
40 |
1100. |
180000. |
320. |
1100. |
11000. |
1100. |
45 |
1500. |
250000. |
460. |
1500. |
15000. |
1500. |
50 |
2000. |
330000. |
600. |
2000. |
20000. |
2000. |
55 |
2600. |
440000. |
780. |
2600. |
26000. |
2600. |
60 |
3400. |
580000. |
1000. |
3400. |
34000. |
3400. |
65 |
4600. |
760000. |
1400. |
4600. |
46000. |
4600. |
70 |
5400. |
900000. |
1600. |
5400. |
54000. |
5400. |
75 |
6400. |
1100000. |
1900. |
6400. |
64000. |
6400. |
80 |
7600. |
1300000. |
2300. |
7600. |
76000. |
7600. |
85 |
9400. |
1500000. |
2800. |
9400. |
94000. |
9400. |
90 |
11000. |
1800000. |
3300. |
11000. |
110000. |
11000. |
95 |
13000. |
2200000. |
3900. |
13000. |
130000. |
13000. |
100 |
15000. |
2600000. |
4600. |
15000. |
150000. |
15000. |
105 |
18000. |
3000000. |
5400. |
18000. |
180000. |
18000. |
110 |
22000. |
3600000. |
6600. |
22000. |
220000. |
22000. |
115 |
26000. |
4400000. |
7800. |
26000. |
260000. |
26000. |
120 |
31000. |
5000000. |
9200. |
31000. |
310000. |
31000. |
I-C
Tier I and Tier II Feed Rate and Emissions Screening Limits for Noncarcinogenic Metals for Facilities in Complex Terrain
Values for urban and rural areas
TESH (m) |
Antimony (g/hr) |
Barium (g/hr) |
Lead (g/hr) |
Mercury (g/hr) |
Silver (g/hr) |
Thallium (g/hr) |
4 |
14. |
2400. |
4.3 |
14. |
140. |
14. |
6 |
21. |
3500. |
6.2 |
21. |
210. |
21. |
8 |
30. |
5000. |
9.2 |
30. |
300. |
30. |
10 |
43. |
7600. |
13. |
43. |
430. |
43. |
12 |
54. |
9000. |
17. |
54. |
540. |
54. |
14 |
68. |
11000. |
20. |
68. |
680. |
68. |
16 |
78. |
13000. |
24. |
78. |
780. |
78. |
18 |
86. |
14000. |
26. |
86. |
860. |
86. |
20 |
96. |
16000. |
29. |
96. |
960. |
96. |
22 |
100. |
18000. |
32. |
100. |
1000. |
100. |
24 |
120. |
19000. |
35. |
120. |
1200. |
120. |
26 |
130. |
22000. |
36. |
130. |
1300. |
130. |
28 |
140. |
24000. |
43. |
140. |
1400. |
140. |
30 |
160. |
27000. |
46. |
160. |
1600. |
160. |
35 |
200. |
33000. |
58. |
200. |
2000. |
200. |
40 |
240. |
40000. |
72. |
240. |
2400. |
240. |
45 |
300. |
50000. |
90. |
300. |
3000. |
300. |
50 |
360. |
60000. |
110. |
360. |
3600. |
360. |
55 |
460. |
76000. |
140. |
460. |
4600. |
460. |
60 |
580. |
94000. |
170. |
580. |
5800. |
580. |
65 |
680. |
110000. |
210. |
680. |
6800. |
680. |
70 |
780. |
130000. |
240. |
780. |
7800. |
780. |
75 |
860. |
140000. |
260. |
860. |
8600. |
860. |
80 |
960. |
160000. |
290. |
960. |
9600. |
960. |
85 |
1100. |
180000. |
330. |
1100. |
11000. |
1100. |
90 |
1200. |
200000. |
360. |
1200. |
12000. |
1200. |
95 |
1400. |
230000. |
400. |
1400. |
14000. |
1400. |
100 |
1500. |
260000. |
460. |
1500. |
15000. |
1500. |
105 |
1700. |
280000. |
500. |
1700. |
17000. |
1700. |
110 |
1900. |
320000. |
580. |
1900. |
19000. |
1900. |
115 |
2100. |
360000. |
640. |
2100. |
21000. |
2100. |
120 |
2400. |
400000. |
720. |
2400. |
24000. |
2400. |
I-D
Tier I and Tier II Feed Rate and Emissions Screening Limits for Carcinogenic Metals for Facilities in Noncomplex Terrain
Values for use in urban areas Values for use in rural areas
Values for use in urban areas |
Values for use in rural areas |
TESH (m) |
Arsenic (g/hr) |
Cadmium (g/hr) |
Chromium (g/hr) |
Beryllium (g/hr) |
Arsenic (g/hr) |
Cadmium (g/hr) |
Chromium (g/hr) |
Beryllium (g/hr) |
4 |
0.46 |
1.1 |
0.17 |
0.82 |
0.24 |
0.58 |
0.086 |
0.43 |
6 |
0.54 |
1.3 |
0.19 |
0.94 |
0.28 |
0.66 |
0.10 |
0.50 |
8 |
0.60 |
1.4 |
0.22 |
1.1 |
0.32 |
0.76 |
0.11 |
0.56 |
10 |
0.68 |
1.6 |
0.24 |
1.2 |
0.36 |
0.86 |
0.13 |
0.64 |
12 |
0.76 |
1.8 |
0.27 |
1.4 |
0.43 |
1.1 |
0.16 |
0.78 |
14 |
0.86 |
2.1 |
0.31 |
1.5 |
0.54 |
1.3 |
0.20 |
0.96 |
16 |
0.96 |
2.3 |
0.35 |
1.7 |
0.68 |
1.6 |
0.24 |
1.2 |
18 |
1.1 |
2.6 |
0.40 |
2.0 |
0.82 |
2.0 |
0.30 |
1.5 |
20 |
1.2 |
3.0 |
0.44 |
2.2 |
1.0 |
2.5 |
0.37 |
1.9 |
22 |
1.4 |
3.4 |
0.50 |
2.5 |
1.3 |
3.2 |
0.48 |
2.4 |
24 |
1.6 |
3.9 |
0.58 |
2.8 |
1.7 |
4.0 |
0.60 |
3.0 |
26 |
1.8 |
4.3 |
0.64 |
3.2 |
2.1 |
5.0 |
0.76 |
3.9 |
28 |
2.0 |
4.8 |
0.72 |
3.6 |
2.7 |
6.4 |
0.98 |
5.0 |
30 |
2.3 |
5.4 |
0.82 |
4.0 |
3.5 |
8.2 |
1.2 |
6.2 |
35 |
3.0 |
6.8 |
1.0 |
5.4 |
5.4 |
13. |
1.9 |
9.6 |
40 |
3.6 |
9.0 |
1.3 |
6.8 |
8.2 |
20. |
3.0 |
15. |
45 |
4.6 |
11. |
1.7 |
8.6 |
11. |
28. |
4.2 |
21. |
50 |
6.0 |
14. |
2.2 |
11. |
15. |
37. |
5.4 |
28. |
55 |
7.6 |
18. |
2.7 |
14. |
20. |
50. |
7.2 |
36. |
60 |
9.4 |
22. |
3.4 |
17. |
27. |
64. |
9.6 |
48. |
65 |
11. |
28. |
4.2 |
21. |
36. |
86. |
13. |
64. |
70 |
13. |
31. |
4.6 |
24. |
43. |
100. |
15. |
76. |
75 |
15. |
36. |
5.4 |
27. |
50. |
120. |
18. |
90. |
80 |
17. |
40. |
6.0 |
30. |
60. |
140. |
22. |
110. |
85 |
19. |
46. |
6.8 |
34. |
72. |
170. |
26. |
130. |
90 |
22. |
50. |
7.8 |
39. |
86. |
200. |
30. |
150. |
95 |
25. |
58. |
9.0 |
44. |
100. |
240. |
36. |
180. |
100 |
28. |
68. |
10. |
50. |
120. |
290. |
43. |
220. |
105 |
32. |
76. |
11. |
56. |
140. |
340. |
50. |
260. |
110 |
36. |
86. |
13. |
64. |
170. |
400. |
60. |
300. |
115 |
40. |
96. |
15. |
72. |
200. |
480. |
72. |
360. |
120 |
46. |
110. |
17. |
82. |
240. |
580. |
86. |
430. |
I-E
Tier I and Tier II Feed Rate and Emissions Screening Limits for Carcinogenic Metals for Facilities in Complex Terrain
Values for use in urban and rural areas
TESH (m) |
Arsenic (g/hr) |
Cadmium (g/hr) |
Chromium (g/hr) |
Beryllium (g/hr) |
4 |
0.11 |
0.26 |
0.040 |
0.20 |
6 |
0.16 |
0.39 |
0.058 |
0.29 |
8 |
0.24 |
0.58 |
0.086 |
0.43 |
10 |
0.35 |
0.82 |
0.13 |
0.62 |
12 |
0.43 |
1.0 |
0.15 |
0.76 |
14 |
0.50 |
1.3 |
0.19 |
0.94 |
16 |
0.60 |
1.4 |
0.22 |
1.1 |
18 |
0.68 |
1.6 |
0.24 |
1.2 |
20 |
0.76 |
1.8 |
0.27 |
1.3 |
22 |
0.82 |
1.9 |
0.30 |
1.5 |
24 |
0.90 |
2.1 |
0.33 |
1.6 |
26 |
1.0 |
2.4 |
0.36 |
1.8 |
28 |
1.1 |
2.7 |
0.40 |
2.0 |
30 |
1.2 |
3.0 |
0.44 |
2.2 |
35 |
1.5 |
3.7 |
0.54 |
2.7 |
40 |
1.9 |
4.6 |
0.68 |
3.4 |
45 |
2.4 |
5.4 |
0.84 |
4.2 |
50 |
2.9 |
6.8 |
1.0 |
5.0 |
55 |
3.5 |
8.4 |
1.3 |
6.4 |
60 |
4.3 |
10. |
1.5 |
7.8 |
65 |
5.4 |
13. |
1.9 |
9.6 |
70 |
6.0 |
14. |
2.2 |
11. |
75 |
6.8 |
16. |
2.4 |
12. |
80 |
7.6 |
18. |
2.7 |
13. |
85 |
8.2 |
20. |
3.0 |
15. |
90 |
9.4 |
23. |
3.4 |
17. |
95 |
10. |
25. |
4.0 |
19. |
100 |
12. |
28. |
4.3 |
21. |
105 |
13. |
32. |
4.8 |
24. |
110 |
15. |
35. |
5.4 |
27. |
115 |
17. |
40. |
6.0 |
30. |
120 |
19. |
44. |
6.4 |
33. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.Appendix D | |
Reference Air Concentrations | |
BOARD NOTE: The RAC for other Appendix H to 35 Ill. Adm. Code 721.Appendix H constituents not listed below or in Appendix E is 0.1 ug/cu mm3.
Constituent |
CAS No. |
RAC (ug/ |
Acetaldehyde |
75-07-0 |
10 |
Acetonitrile |
75-05-8 |
10 |
Acetophenone |
98-86-2 |
100 |
Acrolein |
107-02-8 |
20 |
Aldicarb |
116-06-3 |
1 |
Aluminum Phosphide |
20859-73-8 |
0.3 |
Allyl Alcohol |
107-18-6 |
5 |
Antimony |
7440-36-0 |
0.3 |
Barium |
7440-39-3 |
50 |
Barium Cyanide |
542-62-1 |
50 |
Bromomethane |
74-83-9 |
0.8 |
Calcium Cyanide |
592-01-8 |
30 |
Carbon Disulfide |
75-15-0 |
200 |
Chloral |
75-87-6 |
2 |
Chlorine (free) |
0.4 |
|
2-Chloro-1,3-butadiene |
126-99-8 |
3 |
Chromium III |
16065-83-1 |
1000 |
Copper Cyanide |
544-92-3 |
5 |
Cresols |
1319-77-3 |
50 |
Cumene |
98-82-8 |
1 |
Cyanide (free) |
57-12-15 |
20 |
Cyanogen |
460-19-5 |
30 |
Cyanogen Bromide |
506-68-3 |
80 |
Di-n-butyl Phthalate |
84-74-2 |
100 |
o-Dichlorobenzene |
95-50-1 |
10 |
p-Dichlorobenzene |
106-46-7 |
10 |
Dichlorodifluoromethane |
75-71-8 |
200 |
2,4-Dichlorophenol |
120-83-2 |
3 |
Diethyl Phthalate |
84-66-2 |
800 |
Dimethoate |
60-51-5 |
0.8 |
2,4-Dinitrophenol |
51-28-5 |
2 |
Dinoseb |
88-85-7 |
0.9 |
Diphenylamine |
122-39-4 |
20 |
Endosulfan |
115-29-1 |
0.05 |
Endrin |
72-20-8 |
0.3 |
Fluorine |
7782-41-4 |
50 |
Formic Acid |
64-18-6 |
2000 |
Glycidylaldehyde |
765-34-4 |
0.3 |
Hexachlorocyclopentadiene |
77-47-4 |
5 |
Hexachlorophene |
70-30-4 |
0.3 |
Hydrocyanic Acid |
74-90-8 |
20 |
Hydrogen Chloride |
7647-01-1 |
7 |
Hydrogen Sulfide |
7783-06-4 |
3 |
Isobutyl Alcohol |
78-83-1 |
300 |
Lead |
7439-92-1 |
0.09 |
Maleic Anhydride |
108-31-6 |
100 |
Mercury |
7439-97-6 |
0.3 |
Methacrylonitrile |
126-98-7 |
0.1 |
Methomyl |
16752-77-5 |
20 |
Methoxychlor |
72-43-5 |
50 |
Methyl Chlorocarbonate |
79-22-1 |
1000 |
Methyl Ethyl Ketone |
78-93-3 |
80 |
Methyl Parathion |
298-00-0 |
0.3 |
Nickel Cyanide |
557-19-7 |
20 |
Nitric Oxide |
10102-43-9 |
100 |
Nitrobenzene |
98-95-3 |
0.8 |
Pentachlorobenzene |
608-93-5 |
0.8 |
Pentachlorophenol |
87-86-5 |
30 |
Phenol |
108-95-2 |
30 |
M-Phenylenediamine |
108-45-2 |
5 |
Phenylmercuric Acetate |
62-38-4 |
0.075 |
Phosphine |
7803-51-2 |
0.3 |
Phthalic Anhydride |
85-44-9 |
2000 |
Potassium Cyanide |
151-50-8 |
50 |
Potassium Silver Cyanide |
506-61-6 |
200 |
Pyridine |
110-86-1 |
1 |
Selenious Acid |
7783-60-8 |
3 |
Selenourea |
630-10-4 |
5 |
Silver |
7440-22-4 |
3 |
Silver Cyanide |
506-64-9 |
100 |
Sodium Cyanide |
143-33-9 |
30 |
Strychnine |
57-24-9 |
0.3 |
1,2,4,5-Tetrachlorobenzene |
95-94-3 |
0.3 |
2,3,4,6-Tetrachlorophenol |
58-90-2 |
30 |
Tetraethyl Lead |
78-00-2 |
0.0001 |
Tetrahydrofuran |
109-99-9 |
10 |
Thallic Oxide |
1314-32-5 |
0.3 |
Thallium |
7440-28-0 |
0.5 |
Thallium (I) Acetate |
563-68-8 |
0.5 |
Thallium (I) Carbonate |
6533-73-9 |
0.3 |
Thallium (I) Chloride |
7791-12-0 |
0.3 |
Thallium (I) Nitrate |
10102-45-1 |
0.5 |
Thallium Selenite |
12039-52-0 |
0.5 |
Thallium (I) Sulfate |
7446-18-6 |
0.075 |
Thiram |
137-26-8 |
5 |
Toluene |
108-88-3 |
300 |
1,2,4-Trichlorobenzene |
120-82-1 |
20 |
Trichloromonofluoromethane |
75-69-4 |
300 |
2.4.5-Trichlorophenol |
95-95-4 |
100 |
Vanadium Pentoxide |
1314-62-1 |
20 |
Warfarin |
81-81-2 |
0.3 |
Xylenes |
1330-20-7 |
80 |
Zinc Cyanide |
557-21-1 |
50 |
Zinc Phosphide |
1314-84-7 |
0.3 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.Appendix E | |
BOARD NOTE: These are risk specific doses (RSDs) based on a risk of 1 in 10,000 (1´10-5).
Constituent |
CAS No. |
Unit risk (m3/mg) |
RSD (mg/m3) |
Acrylamide |
79-06-1 |
0.0013 |
0.0077 |
Acrylonitrile |
107-13-1 |
0.000068 |
0.15 |
Aldrin |
309-00-2 |
0.0049 |
0.0020 |
Aniline |
62-53-3 |
0.0000074 |
1.4 |
Arsenic |
7440-38-2 |
0.0043 |
0.0023 |
Benz(a)anthracene |
56-55-3 |
0.00089 |
0.011 |
Benzene |
71-43-2 |
0.0000083 |
1.2 |
Benzidine |
92-87-5 |
0.067 |
0.00015 |
Benzo(a)pyrene |
50-32-8 |
0.0033 |
0.0030 |
Beryllium |
7440-41-7 |
0.0024 |
0.0042 |
Bis(2-chloroethyl)ether |
111-44-4 |
0.00033 |
0.030 |
Bis(chloromethyl)ether |
542-88-1 |
0.062 |
0.00016 |
Bis(2-ethylhexyl)-phthalate |
117-81-7 |
0.00000024 |
42. |
1,3-Butadiene |
106-99-0 |
0.00028 |
0.036 |
Cadmium |
7440-43-9 |
0.0018 |
0.0056 |
Carbon Tetrachloride |
56-23-5 |
0.000015 |
0.67 |
Chlordane |
57-74-9 |
0.00037 |
0.027 |
Chloroform |
67-66-3 |
0.000023 |
0.43 |
Chloromethane |
74-87-3 |
0.0000036 |
2.8 |
Chromium VI |
7440-47-3 |
0.012 |
0.00083 |
DDT |
50-29-3 |
0.000097 |
0.10 |
Dibenz(a,h)anthracene |
53-70-3 |
0.014 |
0.00071 |
1,2-Dibromo-3-chloropropane |
96-12-8 |
0.0063 |
0.0016 |
1,2-Dibromoethane |
106-93-4 |
0.00022 |
0.045 |
1,1-Dichloroethane |
75-34-3 |
0.000026 |
0.38 |
1,2-Dichloroethane |
107-06-2 |
0.000026 |
0.38 |
1,1-Dichloroethylene |
75-35-4 |
0.000050 |
0.20 |
1,3-Dichloropropene |
542-75-6 |
0.35 |
0.000029 |
Dieldrin |
60-57-1 |
0.0046 |
0.0022 |
Diethylstilbestrol |
56-53-1 |
0.14 |
0.000071 |
Dimethylnitrosamine |
62-75-9 |
0.014 |
0.00071 |
2,4-Dinitrotoluene |
121-14-2 |
0.000088 |
0.11 |
1,2-Diphenylhydrazine |
122-66-7 |
0.00022 |
0.045 |
1,4-Dioxane |
123-91-1 |
0.0000014 |
7.1 |
Epichlorohydrin |
106-89-8 |
0.0000012 |
8.3 |
Ethylene Oxide |
75-21-8 |
0.00010 |
0.10 |
Ethylene Dibromide |
106-93-4 |
0.00022 |
0.045 |
Formaldehyde |
50-00-0 |
0.000013 |
0.77 |
Heptachlor |
76-44-8 |
0.0013 |
0.0077 |
Heptachlor Epoxide |
1024-57-3 |
0.0026 |
0.0038 |
Hexachlorobenzene |
118-74-1 |
0.00049 |
0.020 |
Hexachlorobutadiene |
87-68-3 |
0.000020 |
0.50 |
Alpha-hexachlorocyclohexane |
319-84-6 |
0.0018 |
0.0056 |
Beta-hexachlorocyclohexane |
319-85-7 |
0.00053 |
0.019 |
Gamma-hexachlorocyclohexane |
58-89-9 |
0.00038 |
0.026 |
Hexachlorocyclohexane, Technical |
0.00051 |
0.020 |
|
Hexachlorodibenzo-p-dioxin(1,2 Mixture) |
1.3 |
0.0000077 |
|
Hexachloroethane |
67-72-1 |
0.0000040 |
2.5 |
Hydrazine |
302-01-2 |
0.0029 |
0.0034 |
Hydrazine Sulfate |
302-01-2 |
0.0029 |
0.0034 |
3-Methylcholanthrene |
56-49-5 |
0.0027 |
0.0037 |
Methyl Hydrazine |
60-34-4 |
0.00031 |
0.032 |
Methylene Chloride |
75-09-2 |
0.0000041 |
2.4 |
4,4'-Methylene-bis-2-chloroaniline |
101-14-4 |
0.000047 |
0.21 |
Nickel |
7440-02-0 |
0.00024 |
0.042 |
Nickel Refinery Dust |
7440-02-0 |
0.00024 |
0.042 |
Nickel Subsulfide |
12035-72-2 |
0.00048 |
0.021 |
2-Nitropropane |
79-46-9 |
0.027 |
0.00037 |
N-Nitroso-n-butylamine |
924-16-3 |
0.0016 |
0.0063 |
N-Nitroso-n-methylurea |
684-93-5 |
0.086 |
0.00012 |
N-Nitrosodiethylamine |
55-18-5 |
0.043 |
0.00023 |
N-Nitrosopyrrolidine |
930-55-2 |
0.00061 |
0.016 |
Pentachloronitrobenzene |
82-68-8 |
0.000073 |
0.14 |
PCBs |
1336-36-3 |
0.0012 |
0.0083 |
Pronamide |
23950-58-5 |
0.0000046 |
2.2 |
Reserpine |
50-55-5 |
0.0030 |
0.0033 |
2,3,7,8-Tetrachlorodibenzo-p-dioxin |
1746-01-6 |
45. |
0.00000022 |
1,1,2,2-Tetrachloroethane |
79-34-5 |
0.000058 |
0.17 |
Tetrachloroethylene |
127-18-4 |
0.00000048 |
21. |
Thiourea |
62-56-6 |
0.00055 |
0.018 |
1,1,2-Trichloroethane |
79-00-5 |
0.000016 |
0.63 |
Trichloroethylene |
79-01-6 |
0.0000013 |
7.7 |
2,4,6-Trichlorophenol |
88-06-2 |
0.0000057 |
1.8 |
Toxaphene |
8001-35-2 |
0.00032 |
0.031 |
Vinyl Chloride |
75-01-4 |
0.0000071 |
1.4 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.Appendix F | |
Stack Plume Rise | |
Estimated Plume Rise (in Meters)
Based on Stack Exit Flow Rate and Gas Temperature
Exhaust Temperature (K°)
Flow rate
( |
<325 |
325-349 |
350-399 |
400-449 |
450-499 |
500-599 |
600-699 |
700-799 |
800-999 |
1000-1499 |
>1499 |
<0.5 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0.5-0.9 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
1 |
1.0-1.9 |
0 |
0 |
0 |
0 |
1 |
1 |
2 |
3 |
3 |
3 |
4 |
2.0-2.9 |
0 |
0 |
1 |
3 |
4 |
4 |
6 |
6 |
7 |
8 |
9 |
3.0-3.9 |
0 |
1 |
2 |
5 |
6 |
7 |
9 |
10 |
11 |
12 |
13 |
4.0-4.9 |
1 |
2 |
4 |
6 |
8 |
10 |
12 |
13 |
14 |
15 |
17 |
5.0-7.4 |
2 |
3 |
5 |
8 |
10 |
12 |
14 |
16 |
17 |
19 |
21 |
7.5-9.9 |
3 |
5 |
8 |
12 |
15 |
17 |
20 |
22 |
22 |
23 |
24 |
10.0-12.4 |
4 |
6 |
10 |
15 |
19 |
21 |
23 |
24 |
25 |
26 |
27 |
12.5-14.9 |
4 |
7 |
12 |
18 |
22 |
23 |
25 |
26 |
27 |
28 |
29 |
15.0-19.9 |
5 |
8 |
13 |
20 |
23 |
24 |
26 |
27 |
28 |
29 |
31 |
20.0-24.9 |
6 |
10 |
17 |
23 |
25 |
27 |
29 |
30 |
31 |
32 |
34 |
25.0-29.9 |
7 |
12 |
20 |
25 |
27 |
29 |
31 |
32 |
33 |
35 |
36 |
30.0-34.9 |
8 |
14 |
22 |
26 |
29 |
31 |
33 |
35 |
36 |
37 |
39 |
35.0-39.9 |
9 |
16 |
23 |
28 |
30 |
32 |
35 |
36 |
37 |
39 |
41 |
40.0-49.9 |
10 |
17 |
24 |
29 |
32 |
34 |
36 |
38 |
39 |
41 |
42 |
50.0-59.9 |
12 |
21 |
26 |
31 |
34 |
36 |
39 |
41 |
42 |
44 |
46 |
60.0-69.9 |
14 |
22 |
27 |
33 |
36 |
39 |
42 |
43 |
45 |
47 |
49 |
70.0-79.9 |
16 |
23 |
29 |
35 |
38 |
41 |
44 |
46 |
47 |
49 |
51 |
80.0-89.9 |
17 |
25 |
30 |
36 |
40 |
42 |
46 |
48 |
49 |
51 |
54 |
90.0-99.9 |
19 |
26 |
31 |
38 |
42 |
44 |
48 |
50 |
51 |
53 |
56 |
100.0-119.9 |
21 |
26 |
32 |
39 |
43 |
46 |
49 |
52 |
53 |
55 |
58 |
120.0-139.9 |
22 |
28 |
35 |
42 |
46 |
49 |
52 |
55 |
56 |
59 |
61 |
140.0-159.9 |
23 |
30 |
36 |
44 |
48 |
51 |
55 |
58 |
59 |
62 |
65 |
160.0-179.9 |
25 |
31 |
38 |
46 |
50 |
54 |
58 |
60 |
62 |
65 |
67 |
180.0-199.9 |
26 |
32 |
40 |
48 |
52 |
56 |
60 |
63 |
65 |
67 |
70 |
>199.9 |
26 |
33 |
41 |
49 |
54 |
58 |
62 |
65 |
67 |
69 |
73 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.Appendix G | |
Health-Based Limits for Exclusion of Waste-Derived Residues | |
NOTE 1: Under Section 726.212(b)(2)(A), the health-based concentration limits for Appendix H to 35 Ill. Adm. Code 721.Appendix H constituents for which a health-based concentration is not provided below is 0.002 2
´
10-6 mg/kg (0.000002 mg/kg or 0.002 µg/kg).
NOTE 2: The levels specified in this Section and the default level of 0.002 µg/kg (0.000002 mg/kg) or the level of detection for constituents, as identified in Note 1, are administratively stayed under the condition, for those constituents specified in Section 726.212(b)(1), that the owner or operator complies with alternative levels defined as the land disposal restriction limits specified in 35 Ill. Adm. Code 728.143 and Table B to 35 Ill. Adm. Code 728.Table B for F039 nonwastewaters. See Section 726.212(b)(2)(A).
Metals-TCLP Extract Concentration Limits
Constituent |
CAS No. |
Concentration limits (mg/L) |
Antimony |
7440-36-0 |
1. |
Arsenic |
7440-38-2 |
5. |
Barium |
7440-39-3 |
100. |
Beryllium |
7440-41-7 |
0.007 |
Cadmium |
7440-43-9 |
1. |
Chromium |
7440-47-3 |
5. |
Lead |
7439-92-1 |
5. |
Mercury |
7439-97-6 |
0.2 |
Nickel |
7440-02-0 |
70. |
Selenium |
7782-49-2 |
1. |
Silver |
7440-22-4 |
5. |
Thallium |
7440-28-0 |
7. |
Nonmetals-Residue Concentration Limits
Constituent |
CAS No. |
Concentration limits for residues (mg/kg) |
Acetonitrile |
75-05-8 |
0.2 |
Acetophenone |
98-86-2 |
4. |
Acrolein |
107-02-8 |
0.5 |
Acrylamide |
79-06-1 |
0.0002 |
Acrylonitrile |
107-13-1 |
0.0007 |
Aldrin |
309-00-2 |
0.00002 |
Allyl alcohol |
107-18-6 |
0.2 |
Aluminum phosphide |
20859-73-8 |
0.01 |
Aniline |
62-53-3 |
0.06 |
Barium cyanide |
542-62-1 |
1. |
Benz(a)anthracene |
56-55-3 |
0.0001 |
Benzene |
71-43-2 |
0.005 |
Benzidine |
92-87-5 |
0.000001 |
Bis(2-chloroethyl) ether |
111-44-4 |
0.0003 |
Bis(chloromethyl) ether |
542-88-1 |
0.000002 |
Bis(2-ethylhexyl) phthalate |
117-81-7 |
30. |
Bromoform |
75-25-2 |
0.7 |
Calcium cyanide |
592-01-8 |
0.000001 |
Carbon disulfide |
75-15-0 |
4. |
Carbon tetrachloride |
56-23-5 |
0.005 |
Chlordane |
57-74-9 |
0.0003 |
Chlorobenzene |
108-90-7 |
1. |
Chloroform |
67-66-3 |
0.06 |
Copper cyanide |
544-92-3 |
0.2 |
Cresols (Cresylic acid) |
1319-77-3 |
2. |
Cyanogen |
460-19-5 |
1. |
DDT |
50-29-3 |
0.001 |
Dibenz(a, h)-anthracene |
53-70-3 |
0.000007 |
1,2-Dibromo-3-chloropropane |
96-12-8 |
0.00002 |
p-Dichlorobenzene |
106-46-7 |
0.07.5 |
Dichlorodifluoromethane |
75-71-8 |
7. |
1,1-Dichloroethylene |
75-35-4 |
0.005 |
2,4-Dichlorophenol |
120-83-2 |
0.1 |
1,3-Dichloropropene |
542-75-6 |
0.001 |
Dieldrin |
60-57-1 |
0.00002 |
Diethyl phthalate |
84-66-2 |
30. |
Diethylstilbestrol |
56-53-1 |
0.0000001 |
Dimethoate |
60-51-5 |
0.03 |
2,4-Dinitrotoluene |
121-14-2 |
0.0005 |
Diphenylamine |
122-39-4 |
0.9 |
1,2-Diphenylhydrazine |
122-66-7 |
0.0005 |
Endosulfan |
115-29-7 |
0.002 |
Endrin |
72-20-8 |
0.0002 |
Epichlorohydrin |
106-89-8 |
0.04 |
Ethylene dibromide |
106-93-4 |
0.0000001 |
Ethylene oxide |
75-21-8 |
0.0003 |
Fluorine |
7782-41-4 |
4. |
Formic acid |
64-18-6 |
70. |
Heptachlor |
76-44-8 |
0.00008 |
Heptachlor epoxide |
1024-57-3 |
0.00004 |
Hexachlorobenzene |
118-74-1 |
0.0002 |
Hexachlorobutadiene |
87-68-3 |
0.005 |
Hexachlorocyclopentadiene |
77-47-4 |
0.2 |
Hexachlorodibenzo-p-dioxins |
19408-74-3 |
0.0000001 |
Hexachloroethane |
67-72-1 |
0.03 |
Hydrazine |
302-01-1 |
0.0001 |
Hydrogen cyanide |
74-90-8 |
0.00007 |
Hydrogen sulfide |
7783-06-4 |
0.000001 |
Isobutyl alcohol |
78-83-1 |
10. |
Methomyl |
16752-77-5 |
1. |
Methoxychlor |
72-43-5 |
0.1 |
3-Methylcholanthrene |
56-49-5 |
0.00004 |
4,4'-Methylenebis (2-chloroaniline) |
101-14-4 |
0.002 |
Methylene chloride |
75-09-2 |
0.05 |
Methyl ethyl ketone (MEK) |
78-93-3 |
2. |
Methyl hydrazine |
60-34-4 |
0.0003 |
Methyl parathion |
298-00-0 |
0.02 |
Naphthalene |
91-20-3 |
10. |
Nickel cyanide |
557-19-7 |
0.7 |
Nitric oxide |
10102-43-9 |
4. |
Nitrobenzene |
98-95-3 |
0.02 |
N-Nitrosodi-n-butylamine |
924-16-3 |
0.00006 |
N-Nitrosodiethylamine |
55-18-5 |
0.000002 |
N-Nitroso-N-methylurea |
684-93-5 |
0.0000001 |
N-Nitrosopyrrolidine |
930-55-2 |
0.0002 |
Pentachlorobenzene |
608-93-5 |
0.03 |
Pentachloronitrobenzene (PCNB) |
82-68-8 |
0.1 |
Pentachlorophenol |
87-86-5 |
1. |
Phenol |
108-95-2 |
1. |
Phenylmercury acetate |
62-38-4 |
0.003 |
Phosphine |
7803-51-2 |
0.01 |
Polychlorinated biphenyls, N.O.S |
1336-36-3 |
0.00005 |
Potassium cyanide |
151-50-8 |
2. |
Potassium silver cyanide |
506-61-6 |
7. |
Pronamide |
23950-58-5 |
3. |
Pyridine |
110-86-1 |
0.04 |
Reserpine |
50-55-5 |
0.00003 |
Selenourea |
630-10-4 |
0.2 |
Silver cyanide |
506-64-9 |
4. |
Sodium cyanide |
143-33-9 |
1. |
Strychnine |
57-24-9 |
0.01 |
1,2,4,5-Tetrachlorobenzene |
95-94-3 |
0.01 |
1,1,2,2-tetrachloroethane |
79-34-5 |
0.002 |
Tetrachloroethylene |
127-18-4 |
0.7 |
2,3,4,6-Tetrachlorophenol |
58-90-2 |
0.01 |
Tetraethyl lead |
78-00-2 |
0.000004 |
Thiourea |
62-56-6 |
0.0002 |
Toluene |
108-88-3 |
10. |
Toxaphene |
8001-35-2 |
0.005 |
1,1,2-Trichloroethane |
79-00-5 |
0.006 |
Trichloroethylene |
79-01-6 |
0.005 |
Trichloromonofluoromethane |
75-69-4 |
10. |
2,4,5-Trichlorophenol |
95-95-4 |
4. |
2,4,6-Trichlorophenol |
88-06-2 |
4. |
Vanadium pentoxide |
1314-62-1 |
0.7 |
Vinyl chloride |
75-01-4 |
0.002 |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.Appendix I | |
Methods Manual for Compliance with BIF Regulations | |
See “Methods Manual for Compliance with BIF Regulations.”. This document is available from two sources. It is available through NTIS, incorporated by reference in 35 Ill. Adm. Code 720.111. It is also available as 40 CFR 266, Appendix IX (1997), incorporated by reference in 35 Ill. Adm. Code 720.111.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.Appendix J | |
Guideline on Air Quality Models | |
See “Guideline on Air Quality Models (Revised).”. This document is available from two sources. It is available through NTIS, incorporated by reference in 35 Ill. Adm. Code 720.111. It is also available as 40 CFR 266, Appendix X, adopted at 56 Fed. Reg. 32688, July 17, 1991 and amended at 56 Fed. Reg. 42511, August 27, 1991, which is incorporated by reference in 35 Ill. Adm. Code 720.111. This incorporation includes no future editions or amendments.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.Appendix K | |
Lead-Bearing Materials | |
a) | Exempt |
BOARD NOTE: Lead-associated industries are lead smelters, lead-acid battery manufacturing and lead chemical manufacturing (e.g., manufacturing of lead oxide or other lead compounds).
Acid dump/fill solids
Sump mud
Materials from laboratory analyses
Acid filters
Baghouse bags
Clothing (e.g., coveralls, aprons, shoes, hats,, gloves)
Sweepings
Air filter bags and cartridges
Respiratory cartridge filters
Shop abrasive
Stacking boards
Waste shipping containers (e.g., cartons, bags, drums, cardboard)
Paper hand towels
Wiping rags and sponges
Contaminated pallets
Water treatment sludges, filter cakes, residues, and solids
Emission control dusts, sludges, filter cakes, residues, and solids from lead-associated industries (e.g., K069 and D008 wastes)
Spent grinds, posts and separators
Spend batteries
Lead oxide and lead oxide residues
Lead plates and groups
Spent battery cases, covers, and vents
Pasting belts
Water filter media
Cheesecloth from pasting rollers
Pasting additive bags
Asphalt paving materials
b) | Exempt |
Charging jumpers and clips
Platen abrasive
Fluff from lead wire and cable casings
Lead-based pigments and compounding pigment dust
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.Appendix L | |
Nickel or Chromium-Bearing Materials that | |
a) | Exempt |
Baghouse bags
Raney nickel catalyst
Floor sweepings
Air filters
Electroplating bath filters
Wastewater filter media
Wood Pallets
Disposable clothing (coveralls, aprons, hats, and gloves)
Laboratory samples and spent chemicals
Shipping containers and plastic liners from containers or vehicles used to transport nickel or chromium-containing wastes
Respirator cartridge filters
Paper hand towels
b) | Exempt |
Electroplating wastewater treatment sludges (F006)
Nickel and/or chromium-containing solutions
Nickel and/or chromium-containing catalysts
Nickel-cadmium and nickel-iron batteries
Filter cake from wet scrubber system water treatment plants in the specialty steel industry
Filter cake from nickel-chromium alloy pickling operations
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 726.Appendix M | |
Mercury-Bearing Wastes | |
The following materials are exempt mercury-bearing materials containing less than 500 ppm of Appendix H to 35 Ill. Adm. Code 721.Appendix H organic constituents, when generated by manufacturers or users of mercury or mercury products:
Activated carbon | |
Decomposer graphite | |
Wood | |
Paper | |
Protective clothing | |
Sweepings | |
Respiratory cartridge filters | |
Cleanup articles | |
Plastic bags and other contaminated containers | |
Laboratory and process control samples | |
K106 and other wastewater treatment plant sludge and filter cake | |
Mercury cell sump and tank sludge | |
Mercury cell process solids | |
Recoverable levels of mercury contained in soil | |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 728
LAND DISPOSAL RESTRICTIONS
SUBPART A: GENERAL
Section
728.101 | Purpose, Scope, and Applicability |
728.102 | Definitions |
728.103 | Dilution Prohibited as a Substitute for Treatment |
728.104 | Treatment Surface Impoundment Exemption |
728.105 | Procedures for |
728.106 | Petitions to Allow Land Disposal of a Waste Prohibited under Subpart C |
728.107 | Testing, Tracking, and Recordkeeping Requirements for Generators, Treaters, and Disposal Facilities |
728.108 | Landfill and Surface Impoundment Disposal Restrictions (Repealed) |
728.109 | Special Rules for Characteristic Wastes |
SUBPART B: SCHEDULE FOR LAND DISPOSAL PROHIBITION AND ESTABLISHMENT OF TREATMENT STANDARDS
Section
728.110 | First Third (Repealed) |
728.111 | Second Third (Repealed) |
728.112 | Third Third (Repealed) |
728.113 | Newly Listed Wastes |
728.114 | Surface Impoundment |
SUBPART C: PROHIBITION ON LAND DISPOSAL
Section
728.130 | |
728.131 | |
728.132 | |
728.133 | Waste-Specific Prohibitions: |
728.134 | Waste-Specific Prohibitions: |
728.135 | |
728.136 | |
728.137 | |
728.138 | Waste-Specific Prohibitions: Newly-Identified Organic Toxicity Characteristic Wastes and Newly-Listed Coke By-Product and Chlorotoluene Production Wastes |
728.139 | Waste-Specific Prohibitions: Spent Aluminum Potliners and Carbamate Wastes |
SUBPART D: TREATMENT STANDARDS
Section
728.140 | Applicability of Treatment Standards |
728.141 | Treatment Standards Expressed as Concentrations in Waste Extract |
728.142 | Treatment Standards Expressed as Specified Technologies |
728.143 | Treatment Standards Expressed as Waste Concentrations |
728.144 | Adjustment of Treatment Standard |
728.145 | Treatment Standards for Hazardous Debris |
728.146 | Alternative Treatment Standards Based on HTMR |
728.148 | Universal Treatment Standards |
728.149 Alternative LDR Treatment Standards for Contaminated Soil
SUBPART E: PROHIBITIONS ON STORAGE
Section
728.150 | Prohibitions on Storage of Restricted Wastes |
Toxicity Characteristic Leaching Procedure (TCLP) (Repealed) | |
Treatment Standards (As concentrations in the Treatment Residual Extract) (Repealed) | |
List of Halogenated Organic Compounds Regulated under Section 728.132 | |
Wastes Excluded from Lab Packs | |
Organic Lab Packs (Repealed) | |
Technologies to Achieve Deactivation of Characteristics | |
Federal Effective Dates | |
National Capacity LDR Variances for UIC Wastes | |
EP Toxicity Test Method and Structural Integrity Test | |
Recordkeeping, Notification, and Certification Requirements (Repealed) | |
Constituent Concentrations in Waste Extract (CCWE) | |
Constituent Concentrations in Wastes (CCW) | |
Technology Codes and Description of Technology-Based Standards | |
Technology-Based Standards by RCRA Waste Code | |
Standards for Radioactive Mixed Waste | |
Alternative Treatment Standards for Hazardous Debris | |
Alternative Treatment Standards Based on HTMR | |
Wastes Excluded from CCW Treatment Standards | |
Generator Paperwork Requirements | |
Treatment Standards for Hazardous Wastes | |
Universal Treatment Standards (UTS) | |
AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].
SOURCE: Adopted in R87-5 at 11 Ill. Reg. 19354, effective November 12, 1987; amended in R87-39 at 12 Ill. Reg. 13046, effective July 29, 1988; amended in R89-1 at 13 Ill. Reg. 18403, effective November 13, 1989; amended in R89-9 at 14 Ill. Reg. 6232, effective April 16, 1990; amended in R90-2 at 14 Ill. Reg. 14470, effective August 22, 1990; amended in R90-10 at 14 Ill. Reg. 16508, effective September 25, 1990; amended in R90-11 at 15 Ill. Reg. 9462, effective June 17, 1991; amended in R90-11 at 15 Ill. Reg. 11937, effective August 12, 1991; amendment withdrawn at 15 Ill. Reg. 14716, October 11, 1991; amended in R91-13 at 16 Ill. Reg. 9619, effective June 9, 1992; amended in R92-10 at 17 Ill. Reg. 5727, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20692, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6799, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12203, effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17563, effective November 23, 1994; amended in R95-6 at 19 Ill. Reg. 9660, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 11100, effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 783, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7685, effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17706, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1964, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9204, effective July 26, 1999; amended in R00-13 at 24 Ill. Reg. 9623, effective June 20, 2000; amended in R01-3 at 25 Ill. Reg. 1296, effective January 11, 2001; amended in R01-21/R01-23 at 25 Ill. Reg. 9181, effective July 9, 2001; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. 6687, effective April 22, 2002; amended in R03-18 at 27 Ill. Reg. ________, effective ______________________.
SUBPART A: GENERAL
Section 728.101 | Purpose, Scope, and Applicability |
a) | This Part identifies hazardous wastes that are restricted from land disposal and defines those limited circumstances under which an otherwise prohibited waste may continue to be land disposed. |
b) | Except as specifically provided otherwise in this Part or 35 Ill. Adm. Code 721, the requirements of this Part apply to persons that generate or transport hazardous waste and to owners and operators of hazardous waste treatment, storage, and disposal facilities. |
c) | Restricted wastes may continue to be land disposed as follows: |
1) | Where |
2) | Where |
3) | A waste that is hazardous only because it exhibits a characteristic of hazardous waste and |
A) | |
B) | |
4) | A waste that is hazardous only because it exhibits a characteristic of hazardous waste and which is otherwise prohibited under this Part is not prohibited if the waste meets any of the following criteria, unless the waste is subject to a specified method of treatment other than DEACT in Section 728.140 or is D003 reactive cyanide: |
A) | Any of the following is true of either treatment or management of the waste: |
i) | The waste is managed in a treatment system |
ii) | The waste is treated for purposes of the pretreatment requirements of 35 Ill. Adm. Code 307 and 310; or |
iii) | The waste is managed in a zero discharge system engaged in Clean Water Act (CWA)-equivalent treatment, as defined in Section 728.137(a); and |
B) | The waste no longer exhibits a prohibited characteristic of hazardous waste at the point of land disposal (i.e., placement in a surface impoundment). |
d) | This Part does not affect the availability of a waiver under Section 121(d)(4) of the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (CERCLA) (42 USC |
e) | The following hazardous wastes are not subject to any provision of this Part: |
1) | Waste generated by small quantity generators of less than 100 kg of non-acute hazardous waste or less than 1 kg of acute hazardous waste per month, as defined in 35 Ill. Adm. Code 721.105; |
2) | Waste pesticide that a farmer disposes of pursuant to 35 Ill. Adm. Code 722.170; |
3) | Waste identified or listed as hazardous after November 8, 1984, for which USEPA has not promulgated a land disposal prohibition or treatment standard; |
4) | De minimis losses of waste that exhibits a characteristic of hazardous waste to wastewaters are not considered to be prohibited waste and are defined as losses from normal material handling operations (e.g., spills from the unloading or transfer of materials from bins or other containers or leaks from pipes, valves, or other devices used to transfer materials); minor leaks of process equipment, storage tanks, or containers; leaks from well-maintained pump packings and seals; sample purgings; relief device discharges; discharges from safety showers and rinsing and cleaning of personal safety equipment; rinsate from empty containers or from containers that are rendered empty by that rinsing; and laboratory waste that does not exceed one percent of the total flow of wastewater into the facility’s headworks on an annual basis, or with a combined annualized average concentration not exceeding one part per million (ppm) in the headworks of the facility’s wastewater treatment or pretreatment facility; or |
5) | Land disposal prohibitions for hazardous characteristic wastes do not apply to laboratory wastes displaying the characteristic of ignitability (D001), corrosivity (D002), or organic toxicity (D012 through D043) that are mixed with other plant wastewaters at facilities whose ultimate discharge is subject to regulation under the CWA (including wastewaters at facilities that have eliminated the discharge of wastewater), provided that the annualized flow of laboratory wastewater into the facility’s headworks does not exceed one percent or that the laboratory wastes’ combined annualized average concentration does not exceed one part per million in the facility’s headworks. |
f) | A universal waste handler or universal waste transporter (as defined in 35 Ill. Adm. Code 720.110) is exempt from Sections 728.107 and 728.150 for the hazardous wastes listed below. Such a handler or transporter is subject to regulation under 35 Ill. Adm. Code 733. |
1) | Batteries, as described in 35 Ill. Adm. Code 733.102; |
2) | Pesticides, as described in 35 Ill. Adm. Code 733.103; |
3) | Thermostats, as described in 35 Ill. Adm. Code 733.104; and |
4) | Lamps, as described in 35 Ill. Adm. Code 733.105. |
g) | This Part is cumulative with the land disposal restrictions of 35 Ill. Adm. Code 729. The Environmental Protection Agency (Agency) |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.102 | Definitions |
When used in this Part, the following terms have the meanings given below. All other terms have the meanings given under 35 Ill. Adm. Code 702.110, 720.110, or 721.102 through 721.104.
“Agency” means the Illinois Environmental Protection Agency.
“Board” means the Illinois Pollution Control Board.
“CERCLA” means the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (42 USC 9601 et seq.)
“Debris” means solid material exceeding a 60 mm particle size that is intended for disposal and that is: a manufactured object; plant or animal matter; or natural geologic material. However, the following materials are not debris: any material for which a specific treatment standard is provided in Subpart D of this Part, namely lead acid batteries, cadmium batteries, and radioactive lead solids; process residuals, such as smelter slag and residues from the treatment of waste, wastewater, sludges, or air emission residues; and intact containers of hazardous waste that are not ruptured and that retain at least 75 percent of their original volume. A mixture of debris that has not been treated to the standards provided by Section 728.145 of this Part and other material is subject to regulation as debris if the mixture is comprised primarily of debris, by volume, based on visual inspection.
“End-of-pipe” refers to the point where effluent is discharged to the environment.
“Halogenated organic compounds” or “HOCs” means those compounds having a carbon-halogen bond that are listed under Appendix C of this Part.
“Hazardous constituent or constituents” means those constituents listed in Appendix H to 35 Ill. Adm. Code 721.Appendix H.
“Hazardous debris” means debris that contains a hazardous waste listed in Subpart D of 35 Ill. Adm. Code 721.Subpart D or that exhibits a characteristic of hazardous waste identified in Subpart C of 35 Ill. Adm. Code 721.Subpart C. Any deliberate mixing of prohibited waste with debris that changes its treatment classification (i.e., from waste to hazardous debris) is not allowed under the dilution prohibition in Section 728.103.
“Inorganic metal-bearing waste” is one for which USEPA has established treatment standards for metal hazardous constituents that does not otherwise contain significant organic or cyanide content, as described in Section 728.103(b)(1), and which is specifically listed in Appendix K of this Part.
“Land disposal” means placement in or on the land, except in a corrective action management unit or staging pile, and “land disposal” includes, but is not limited to, placement in a landfill, surface impoundment, waste pile, injection well, land treatment facility, salt dome formation, salt bed formation, underground mine or cave, or placement in a concrete vault or bunker intended for disposal purposes.
“Nonwastewaters” are wastes that do not meet the criteria for “wastewaters” in this Section.
“Polychlorinated biphenyls” or “PCBs” are halogenated organic compounds defined in accordance with 40 CFR 761.3, incorporated by reference in 35 Ill. Adm. Code 720.111.
“ppm” means parts per million.
“RCRA corrective action” means corrective action taken under 35 Ill. Adm. Code 724.200 or 725.193, 40 CFR 264.100 or 265.93 (1996), or similar regulations in other states with RCRA programs authorized by USEPA pursuant to 40 CFR 271 (1996).
“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 United States Natural Resources Conservation Service, or a mixture of such materials with liquids, sludges, or solids that is inseparable by simple mechanical removal processes and which is made up primarily of soil by volume based on visual inspection. Any deliberate mixing of prohibited waste with debris that changes its treatment classification (i.e., from waste to hazardous debris) is not allowed under the dilution prohibition in Section 728.103.
“Stormwater impoundments” are surface impoundments that receive wet weather flow and which receive process waste only during wet weather events.
“Underlying hazardous constituent” means any constituent listed in Table U of this Part, “Universal Treatment Standards (UTS),”, except fluoride, selenium, sulfides, vanadium, and zinc, that can reasonably be expected to be present at the point of generation of the hazardous waste at a concentration above the constituent-specific UTS treatment standard.
“USEPA” or “U.S. EPA” means the United States Environmental Protection Agency.
“Wastewaters” are wastes that contain less than 1 one percent by weight total organic carbon (TOC) and less than 1 one percent by weight total suspended solids (TSS).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.103 | Dilution Prohibited as a Substitute for Treatment |
a) | Except as provided in subsection (b) of this Section, no generator, transporter, handler, or owner or operator of a treatment, storage, or disposal facility |
b) | Dilution of waste that is hazardous only because it exhibits a characteristic of hazardous waste in a treatment system that treats wastes subsequently discharged to a water of the State pursuant to an NPDES permit issued under 35 Ill. Adm. Code 309, that treats wastes in a CWA-equivalent treatment system, or that treats wastes for purposes of pretreatment requirements under 35 Ill. Adm. Code 310 is not impermissible dilution for purposes of this Section, unless a method other than DEACT has been specified in Section 728.140 as the treatment standard or unless the waste is a D003 reactive cyanide wastewater or nonwastewater. |
c) | Combustion of waste designated by any of the USEPA hazardous waste codes listed in |
1) | The waste contains hazardous organic constituents or cyanide at levels exceeding the constituent-specific treatment standard found in Section 728.148; |
2) | The waste consists of organic, debris-like materials (e.g., wood, paper, plastic, or cloth) contaminated with an inorganic metal-bearing hazardous waste; |
3) | The waste has reasonable heating value, such as greater than or equal to 5000 Btu per pound, at the point of generation; |
4) | The waste is co-generated with wastes for which combustion is a required method of treatment; |
5) | The waste is subject to any federal or state requirements necessitating reduction of organics (including biological agents); or |
6) | The waste contains greater than one percent Total Organic Carbon (TOC). |
d) | It is a form of impermissible dilution, and therefore prohibited, to add iron filings or other metallic forms of iron to lead-containing hazardous wastes in order to achieve any land disposal restriction treatment standard for lead. Lead-containing wastes include D008 wastes (wastes exhibiting a characteristic due to the presence of lead), all characteristic wastes containing lead as an underlying hazardous constituent, listed wastes containing lead as a regulated |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.104 | Treatment Surface Impoundment Exemption |
a) | Wastes |
1) | Treatment of such wastes occurs in the impoundments; |
2) | The following conditions are met: |
A) | Sampling and testing. For wastes with treatment standards in Subpart D or prohibition levels in Subpart C, the residues from treatment are analyzed, as specified in Section 728.107 or 728.132, to determine if they meet the applicable treatment standards or, where no treatment standards have been established for the waste, the applicable prohibition levels. The sampling method, specified in the waste analysis plan under 35 Ill. Adm. Code 724.113 or 725.113, must be designed such that representative samples of the sludge and the supernatant are tested separately rather than mixed to form homogeneous samples. |
B) | Removal. The following treatment residues (including any liquid waste) must be removed at least annually: residues |
C) | Subsequent management. Treatment residues must not be placed in any other surface impoundment for subsequent management. |
D) | Recordkeeping. Sampling, testing, and recordkeeping provisions of 35 Ill. Adm. Code 724.113 or 725.113 apply; |
3) | The impoundment meets the design requirements of 35 Ill. Adm. Code 724.321(c) or 725.321(a) even though the unit may not be new, expanded or a replacement, and must be in compliance with applicable groundwater monitoring requirements of Subpart F of 35 Ill. Adm. Code 724 |
A) | The impoundment is exempted pursuant to 35 Ill. Adm. Code 724.321(d) or (e), or to 35 Ill. Adm. Code 725.321(c) or (d); |
B) | Upon application by the owner or operator, the Agency has by permit provided that the requirements of this Part do not apply on the basis that the surface impoundment fulfills all of the following conditions: |
i) | The impoundment has at least one liner, for which there is no evidence that such liner is leaking; |
ii) | The impoundment is located more than one-quarter mile from an underground source of drinking water; and |
iii) | The impoundment is in compliance with generally applicable groundwater monitoring requirements for facilities with permits; or |
C) | Upon application by the owner or operator, the Board has, pursuant to Subpart D of 35 Ill. Adm. Code |
4) | The owner or operator submits to the Agency a written certification that the requirements of subsection (a)(3) of this Section have been met. The following certification is required: |
I certify under penalty of law that the requirements of 35 Ill. Adm. Code 728.104(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 a treatment for purposes of an exemption under this Section. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.105 | Procedures for |
a) | The Board incorporates by reference 40 CFR 268.5 |
b) | Persons may apply to USEPA for extensions of effective dates pursuant to 40 CFR 268.5. Extensions |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.106 | Petitions to Allow Land Disposal of a Waste Prohibited under Subpart C |
a) | Any person seeking an exemption from a prohibition under Subpart C for the disposal of a restricted hazardous waste in a particular unit or units |
1) | An identification of the specific waste and the specific unit for which the demonstration will be made; |
2) | A waste analysis to describe fully the chemical and physical characteristics of the subject waste; |
3) | A comprehensive characterization of the disposal unit site including an analysis of background air, soil, and water quality; |
4) | A monitoring plan |
5) | Sufficient information to assure the Agency that the owner or operator of a land disposal unit receiving restricted wastes will comply with other applicable federal, state, and local laws; |
6) | Whether the facility is in interim status, or, if a RCRA permit has been issued, the term of the permit. |
b) | The demonstration referred to in subsection (a) of this Section must meet the following criteria: |
1) | All waste and environmental sampling, test and analysis data must be accurate and reproducible to the extent that state-of-the-art techniques allow; |
2) | All sampling, testing and estimation techniques for chemical and physical properties of the waste and all environmental parameters must conform with “Test Methods for Evaluating Solid Waste” and with “Generic Quality Assurance Project Plan for Land Disposal Restrictions Program,” incorporated by reference in 35 Ill. Adm. Code 720.111. |
3) | Simulation models must be calibrated for the specific waste and site conditions, and verified for accuracy by comparison with actual measurements; |
4) | A quality assurance and quality control plan that addresses all aspects of the demonstration and conforms with “Test Methods for Evaluating Solid Waste” and with “Generic Quality Assurance Project Plan for Land Disposal Restrictions Program,” incorporated by reference in 35 Ill. Adm. Code 720.111 |
5) | An analysis must be performed to identify and quantify any aspects of the demonstration that contribute significantly to uncertainty. This analysis must include an evaluation of the consequences of predictable future events, including, but not limited to, earthquakes, floods, severe storm events, droughts, or other natural phenomena. |
c) | Each petition referred to in subsection (a) of this Section must include the following: |
1) | A monitoring plan that describes the monitoring program installed at or around the unit to verify continued compliance with the conditions of the adjusted standard. This monitoring plan must provide information on the monitoring of the unit or the environment around the unit. The following specific information must be included in the plan: |
A) | The media monitored in the cases where monitoring of the environment around the unit is required; |
B) | The type of monitoring conducted at the unit, in the cases where monitoring of the unit is required; |
C) | The location of the monitoring stations; |
D) | The monitoring interval (frequency of monitoring at each station); |
E) | The specific hazardous constituents to be monitored; |
F) | The implementation schedule for the monitoring program; |
G) | The equipment used at the monitoring stations; |
H) | The sampling and analytical techniques employed; and |
I) | The data recording and reporting procedures. |
2) | Where applicable, the monitoring program described in subsection (c)(1) of this Section must be in place for a period of time specified by the Board, as part of its approval of the petition, prior to receipt of prohibited waste at the unit. |
3) | The monitoring data collected according to the monitoring plan specified under subsection (c)(1) of this Section must be sent to the Agency according to a format and schedule specified and approved in the monitoring plan |
4) | A copy of the monitoring data collected under the monitoring plan specified under subsection (c)(1) of this Section must be kept on-site at the facility in the operating record. |
5) | The monitoring program specified under subsection (c)(1) of this Section must meet the following criteria: |
A) | All sampling, testing, and analytical data must be approved by the Board and must provide data that is accurate and reproducible |
B) | All estimation and monitoring techniques must be approved by the Board |
C) | A quality assurance and quality control plan addressing all aspects of the monitoring program must be provided to and approved by the Board. |
d) | Each petition must be submitted to the Board as provided in Subpart D of 35 Ill. Adm. Code |
e) | After a petition has been approved, the owner or operator |
1) | If the owner or operator plans to make changes to the unit design, construction, or operation, the owner or operator |
A) | File a petition for modification of or a new petition to amend an adjusted standard with the Board reflecting the changes; or |
B) | Demonstrate to the Agency that the change can be made consistent with the conditions of the existing adjusted standard. |
2) | If the owner or operator discovers that a condition at the site |
f) | If there is migration of hazardous |
1) | Immediately suspend receipt of prohibited waste at the unit, and |
2) | Notify the Agency, in writing, within 10 days |
3) | Following receipt of the notification, the Agency shall, within 60 days |
A) | Determine whether the owner or operator can continue to receive prohibited waste in the unit under the conditions of the adjusted standard. |
B) | If modification or vacation of the adjusted standard is necessary, file a motion to modify or vacate the adjusted standard with the Board. |
C) | Determine whether further examination of any migration is required under the applicable provisions of 35 Ill. Adm. Code 724 or 725. |
g) | Each petition must include the following statement signed by the petitioner or an authorized representative: |
I certify under penalty of law that I have personally examined and am familiar with the information submitted in this petition and all attached documents, and that, based on my inquiry of those individuals immediately responsible for obtaining the information. I believe that submitted information is true, accurate, and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment.
h) | After receiving a petition, the Board may request any additional information that may be required to evaluate the demonstration. |
i) | If approved, the petition will apply to land disposal of the specific restricted waste at the individual disposal unit described in the demonstration and will not apply to any other restricted waste at that disposal unit, or to that specific restricted waste at any other disposal unit. |
j) | The Board will give public notice and provide an opportunity for public comment, as provided in Subpart D of 35 Ill. Adm. Code |
k) | The term of a petition granted under this Section will be no longer than the term of the RCRA permit if the disposal unit is operating under a RCRA permit, or up to a maximum of 10 years from the date of approval provided under subsection (g) of this Section if the unit is operating under interim status. In either case, the term of the granted petition expires upon the termination or denial of a RCRA permit, or upon the termination of interim status or when the volume limit of waste to be land disposed during the term of petition is reached. |
l) | Prior to the Board’s decision, the applicant |
m) | The petition granted by the Board does not relieve the petitioner of responsibilities in the management of hazardous waste under 35 Ill. Adm. Code 702, 703, and 720 through 726. |
n) | Liquid hazardous wastes containing PCBs at concentrations greater than or equal to 500 ppm are not eligible for an adjusted standard under this Section. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.107 | Testing, Tracking, and Recordkeeping Requirements for Generators, Treaters, and Disposal Facilities |
a) | Requirements for generators |
1) | A generator of a hazardous waste |
2) | If the waste or contaminated soil does not meet the treatment standard, the generator |
A) | For contaminated soil, the following certification statement should be included, signed by an authorized representative: |
I certify under penalty of law that I personally have examined this contaminated soil and it (does/does not) contain listed hazardous waste and (does/does not) exhibit a characteristic of hazardous waste and requires treatment to meet the soil treatment standards as provided by 35 Ill. Adm. Code 728.149(c).
B) | This subsection (a)(2)(B) corresponds with 40 CFR 268.7(a)(2)(ii), which is marked “reserved” by USEPA. This statement maintains structural consistency with USEPA rules. |
3) | If the waste or contaminated soil meets the treatment standard at the original point of generation, the waste generator must do the following: |
A) | With the initial shipment of waste to each treatment, storage, or disposal facility, the generator |
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 35 Ill. Adm. Code 728.Subpart D of 35 Ill. Adm. Code 728. 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.
B) | For contaminated soil, with the initial shipment of wastes to each treatment, storage, or disposal facility, the generator must send a one-time written notice to each facility receiving the waste and place a copy in the file. The notice must include the information in the column headed “(a)(3)” in Table I of this Part. |
C) | If the waste changes, the generator |
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 Section 728.105, disposal in a no-migration unit under Section 728.106, 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 |
5) | If a generator is managing and treating prohibited waste or contaminated soil in tanks, containers, or containment buildings regulated under 35 Ill. Adm. Code 722.134 to meet applicable LDR treatment standards found at Section 728.140, the generator |
A) | The waste analysis plan must be based on a detailed chemical and physical analysis of a representative sample of the prohibited wastes being treated, and contain all information necessary to treat the wastes in accordance with the requirements of this Part, including the selected testing frequency; |
B) | Such plan must be kept in the facility’s on-site files and made available to inspectors; and |
C) | Wastes shipped off-site pursuant to this subsection (a)(5) of this Section must comply with the notification requirements of subsection (a)(3) of this Section. |
6) | If a generator determines that the waste or contaminated soil is restricted based solely on its knowledge of the waste, all supporting data used to make this determination must be retained on-site in the generator’s files. If a generator determines that the waste is restricted based on testing this waste or an extract developed using SW-846 Method 1311 (the Toxicity Characteristic Leaching Procedure), incorporated by reference in 35 Ill. Adm. Code 720.111, all waste analysis data must be retained on-site in the generator’s files. |
7) | If a generator determines that it is managing a prohibited waste |
8) | A generator |
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 Section 728.142(c), the generator |
A) | With the initial shipment of waste to a treatment facility, the generator |
I certify under penalty of law that I personally have examined and am familiar with the waste and that the lab pack contains only wastes that have not been excluded under Appendix D to 35 Ill. Adm. Code 728.Appendix D and that this lab pack will be sent to a combustion facility in compliance with the alternative treatment standards for lab packs at 35 Ill. Adm. Code 728.142(c). I am aware that there are significant penalties for submitting a false certification, including the possibility of fine or imprisonment.
B) | No further notification is necessary until such time as 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. |
C) | If the lab pack contains characteristic hazardous wastes (D001-D043), underlying hazardous constituents (as defined in Section 728.102(i)) need not be determined. |
D) | The generator |
10) | Small quantity generators with tolling agreements pursuant to 35 Ill. Adm. Code 722.120(e) |
b) | The owner or operator of a treatment facility |
1) | For wastes or contaminated soil with treatment standards expressed in the waste extract (TCLP), the owner or operator of the treatment facility |
2) | For wastes or contaminated soil with treatment standards expressed as concentrations in the waste, the owner or operator of the treatment facility |
3) | A one-time notice must be sent with the initial shipment of waste or contaminated soil to the land disposal facility. A copy of the notice must be placed in the treatment facility’s file. |
A) | No further notification is necessary until such time that the waste or receiving facility changes, in which case a new notice must be sent and a copy placed in the treatment facility’s file. |
B) | The one-time notice must include the following requirements |
Treatment Facility Paperwork Requirements Table
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i) | USEPA hazardous waste number and manifest number of first shipment; |
ii) | The waste is subject to the LDRs. The constituents of concern for F001 through F005 and F039 waste 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; |
iii) | The notice must include the applicable wastewater/ nonwastewater category (see Section 728.102(d) and (f)) and subdivisions made within a waste code based on waste-specific criteria (such as D003 reactive cyanide); |
iv) | Waste analysis data (when available); |
v) | For contaminated soil subject to LDRs as provided in Section 728.149(a), the constituents subject to treatment as described in Section 728.149(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 Section 728.149(c)”; and |
vi) | A certification is needed (see applicable Section for exact wording). |
4) | The owner or operator of a treatment facility |
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 35 Ill. Adm. Code 728.140 without impermissible dilution of the prohibited waste. I am aware there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.
A certification is also necessary for contaminated soil and it must state as follows:
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 35 Ill. Adm. Code 728.149 without impermissible dilution of the prohibited wastes. I am aware there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.
A) | A copy of the certification must be placed in the treatment facility’s on-site files. If the waste or treatment residue changes, or the receiving facility changes, a new certification must be sent to the receiving facility, and a copy placed in the treatment facility’s file. |
B) | Debris excluded from the definition of hazardous waste under 35 Ill. Adm. Code 721.103(e) (i.e., debris treated by an extraction or destruction technology listed in Table F of this Part and debris that the Agency has determined does not contain hazardous waste) is subject to the notification and certification requirements of subsection (d) of this Section rather than the certification requirements of this subsection (b)(4). |
C) | For wastes with organic constituents having treatment standards expressed as concentration levels, if compliance with the treatment standards is based in part or in whole on the analytical detection limit alternative specified in Section 728.140(d), the certification must be signed by an authorized representative and must state |
I certify under penalty of law that I have personally examined and am familiar with the treatment technology and operation of the treatment process used to support this certification. Based on my inquiry of those individuals immediately responsible for obtaining this information, I believe that the nonwastewater organic constituents have been treated by combustion units as specified in Table C to 35 Ill. Adm. Code 728.Table C. I have been unable to detect the nonwastewater organic constituents, despite having used best good faith efforts to analyze for such constituents. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.
D) | For characteristic wastes that are subject to the treatment standards in Section 728.140 and Table T of this Part (other than those expressed as a required method of treatment) or Section 728.149 and which contain underlying hazardous constituents, as defined in |
I certify under penalty of law that the waste has been treated in accordance with the requirements of 35 Ill. Adm. Code 728.140 and Table T of Section 728.149 of that Part to remove the hazardous characteristic. This decharacterized waste contains underlying hazardous constituents that require further treatment to meet treatment standards. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.
E) | For characteristic wastes that contain underlying hazardous constituents, as defined in Section 728.102(i), that are treated on-site to remove the hazardous characteristic and to treat underlying hazardous constituents to levels in Section 728.148 and Table U of this Part universal treatment standards, the certification must state |
I certify under penalty of law that the waste has been treated in accordance with the requirements of 35 Ill. Adm. Code 728.140 and Table T of that Part to remove the hazardous characteristic and that underlying hazardous constituents, as defined in 35 Ill. Adm. Code 728.102(i), have been treated on-site to meet the universal treatment standards of 35 Ill. Adm. Code 728.148 and Table U of that Part. I am aware that there are significant penalties for submitting a false certification, including the possibility of fine and imprisonment.
5) | If the waste or treatment residue will be further managed at a different treatment, storage, or disposal facility, the treatment, storage, or disposal facility |
6) | Where the wastes are recyclable materials used in a manner constituting disposal subject to the provisions of 35 Ill. Adm. Code 726.120(b), regarding treatment standards and prohibition levels, the owner or operator of a treatment facility (i.e., the recycler) is not required to notify the receiving facility pursuant to subsection (b)(3) of this Section. With each shipment of such wastes the owner or operator of the recycling facility |
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 35 Ill. Adm. Code 726.120(b), the owner or operator of any land disposal facility disposing any waste subject to restrictions under this Part shall do the following: |
1) | Maintain in its files copies of the notice and certifications specified in subsection (a) or (b) of this Section. |
2) | Test the waste or an extract of the waste or treatment residue developed using SW-846 Method 1311 (the Toxicity Characteristic Leaching Procedure), incorporated by reference in 35 Ill. Adm. Code 720.111, to assure that the waste or treatment residue is in compliance with the applicable treatment standards set forth in Subpart D of this Part. Such testing must be performed according to the frequency specified in the facility’s waste analysis plan as required by 35 Ill. Adm. Code 724.113 or 35 Ill. Adm. Code 725.113. |
3) | Where the owner or operator is disposing of any waste that is subject to the prohibitions under Section 728.133(f) but not subject to the prohibitions set forth in Section 728.132, the owner or operator |
4) | Where the owner or operator is disposing of any waste that is a recyclable material used in a manner constituting disposal subject to the provisions of 35 Ill. Adm. Code 726.120(b), the owner or operator is not subject to subsections (c)(1) through (c)(3) of this Section with respect to such waste. |
d) | A generator or treater that first claims that hazardous debris is excluded from the definition of hazardous waste under 35 Ill. Adm. Code 721.103(e) (i.e., debris treated by an extraction or destruction technology provided by Table F of this Part, and debris that has been delisted) is subject to the following notification and certification requirements: |
1) | A one-time notification must be submitted to the Agency including the following information: |
A) | The name and address of the RCRA Subtitle D (municipal solid waste landfill) facility receiving the treated debris; |
B) | A description of the hazardous debris as initially generated, including the applicable USEPA hazardous waste numbers; and |
C) | For debris excluded under 35 Ill. Adm. Code 721.103(e)(1), the technology from Table F of this Part used to treat the debris. |
2) | The notification must be updated if the debris is shipped to a different facility and, for debris excluded under 35 Ill. Adm. Code 721.102(e)(1), if a different type of debris is treated or if a different technology is used to treat the debris. |
3) | For debris excluded under 35 Ill. Adm. Code 721.103(e)(1), the owner or operator of the treatment facility |
A) | Records must be kept of all inspections, evaluations, and analyses of treated debris that are made to determine compliance with the treatment standards; |
B) | Records must be kept of any data or information the treater obtains during treatment of the debris that identifies key operating parameters of the treatment unit; and |
C) | For each shipment of treated debris, a certification of compliance with the treatment standards must be signed by an authorized representative and placed in the facility’s files. The certification must state |
I certify under penalty of law that the debris has been treated in accordance with the requirements of 35 Ill. Adm. Code 728.145. I am aware that there are significant penalties for making a false certification, including the possibility of fine and imprisonment.
e) | A generator or treater that first receives a determination from USEPA or the Agency that a given contaminated soil subject to LDRs, as provided in Section 728.149(a), no longer contains a listed hazardous waste and |
1) | Prepare a one-time only documentation of these determinations including all supporting information; and |
2) | Maintain that information in the facility files and other records for a minimum of three years. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.109 | Special Rules for Characteristic Wastes |
a) | The initial generator of a solid waste |
b) | Where a prohibited waste is both listed under Subpart D of 35 Ill. Adm. Code 721 |
c) | In addition to any applicable standards determined from the initial point of generation, no prohibited waste that exhibits a characteristic under Subpart C of 35 Ill. Adm. Code 721 |
d) | A waste that exhibits a characteristic of hazardous waste under Subpart C of 35 Ill. Adm. Code 721 is also subject to Section 728.107 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 files and sent to the Agency, except for those facilities described in subsection (f) of this Section. The notification and certification that is placed in the generator’s or treater’s files must be updated if the process or operation generating the waste changes or if the RCRA Subtitle D (municipal solid waste landfill) facility receiving the waste changes. However, the generator or treater need only notify the Agency on an annual basis if such changes occur. Such notification and certification should be sent to the Agency by the end of the year, but no later than December 31. |
1) | The notification must include the following information: |
A) | The name and address of the RCRA Subtitle D (municipal solid waste landfill) facility receiving the waste shipment; and |
B) | A description of the waste as initially generated, including the applicable USEPA hazardous waste numbers, the treatability groups, and the underlying hazardous constituents (as defined in Section 728.102(i)), unless the waste will be treated and monitored for all underlying hazardous constituents. If all underlying hazardous constituents will be treated and monitored, there is no requirement to list any of the underlying hazardous constituents on the notice. |
2) | The certification must be signed by an authorized representative and must state the language found in Section 728.107(b)(4). If treatment removes the characteristic but does not meet standards applicable to underlying hazardous constituents, then the certification found in Section 728.107(b)(4)(D) applies. |
3) | For a characteristic waste whose ultimate disposal will be into a Class I nonhazardous waste injection well, and for which compliance with the treatment standards set forth in |
A) | A description of the pollution prevention mechanism and when it was implemented, if already complete; |
B) | The mass of each underlying hazardous constituent before pollution prevention; |
C) | The mass of each underlying hazardous constituent that must be removed, adjusted to reflect variations in mass due to normal operating conditions; and |
D) | The mass reduction of each underlying hazardous constituent that is achieved. |
e) | For a decharacterized waste managed on-site in a wastewater treatment system subject to the federal Clean Water Act (CWA) or zero-dischargers engaged in CWA-equivalent treatment, compliance with the treatment standards set forth in Sections 728.148 and |
f) | For a decharacterized waste managed on-site in a wastewater treatment system subject to the federal Clean Water Act (CWA) for which all underlying hazardous constituents (as defined in Section 728.102) are addressed by a CWA permit, this compliance must be documented and this documentation must be kept in on-site files. |
g) | For a characteristic waste whose ultimate disposal will be into a Class I nonhazardous waste injection well that qualifies for the de minimis exclusion described in Section 728.101, information supporting that qualification must be kept in on-site files. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART B: SCHEDULE FOR LAND DISPOSAL PROHIBITION AND ESTABLISHMENT OF TREATMENT STANDARDS
Section 728.113 | Newly Listed Wastes |
The Board incorporates by reference 40 CFR 268.13 (1991). This Section incorporates no later editions or amendments.
In corresponding 40 CFR 268.13, USEPA stated that it would make a land disposal prohibition determination for any hazardous waste identified or listed after November 8, 1984 within six months after the date of identification or listing. This statement maintains structural consistency with the corresponding federal regulations.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.114 | Surface Impoundment |
a) | This Section defines additional circumstances under which an otherwise prohibited waste may continue to be placed in a surface impoundment. |
b) | Wastes |
c) | Wastes |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART C: PROHIBITION ON LAND DISPOSAL
Section 728.130 | |
a) | The following wastes are prohibited from land disposal: the wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous waste numbers F032, F034, and F035. |
b) | |
c) | |
d) | The requirements of subsections (a) and (b) of this Section do not apply if any of the following conditions is fulfilled: |
1) | The wastes meet the applicable treatment standards specified in Subpart D of this Part; |
2) | |
3) | The wastes meet the applicable alternate treatment standards established pursuant to a petition granted under Section 728.144; or |
4) | |
e) | To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards specified in |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.131 | |
a) | The dioxin-containing wastes specified in 35 Ill. Adm. Code 721.131 as USEPA Hazardous Waste Numbers F020, F021, F022, F023, F026, F027, and F028 are prohibited from land disposal, unless the following condition applies: |
b) | |
c) | |
d) | The requirements of subsections (a) and (b) of this Section do not apply if any of the following conditions is fulfilled: |
1) | The wastes meet the standards of Subpart D of this Part; or |
2) | |
3) | |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.132 | |
a) | The following wastes are prohibited from land disposal: any volumes of soil exhibiting the toxicity characteristic solely because of the presence of metals (USEPA hazardous waste numbers D004 through D011) and containing PCBs. |
b) | The requirements of subsection (a) of this Section do not apply if any of the following conditions is fulfilled: |
1) | Low-halogenated organics waste meeting |
A) | The wastes contain halogenated organic compounds in total concentration less than 1,000 mg/kg; and |
B) | The wastes meet the treatment standards specified in Subpart D of this |
2) | Low-halogenated organics waste meeting alternative treatment standards for contaminated soil: |
A) | The wastes contain halogenated organic compounds in total concentration less than 1,000 mg/kg; and |
B) | The wastes meet the alternative treatment standards specified in Section 728.149 for contaminated soil; or |
3) | |
4) | The wastes meet applicable alternative treatment standards established pursuant to a petition granted under Section 728.144. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.133 | Waste-Specific Prohibitions: |
a) | The wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous wastes numbers K174 and K175, soil and debris contaminated with these wastes, radioactive wastes mixed with these wastes, and soil and debris contaminated with radioactive wastes mixed with these wastes are prohibited from land disposal. |
b) | The requirements of subsection (a) of this Section do not apply if any of the following conditions is fulfilled: |
1) | The wastes meet the applicable treatment standards specified in Subpart D of this Part; |
2) | |
3) | The wastes meet the applicable treatment standards established pursuant to a petition granted under Section 728.144; |
4) | Hazardous debris has met the treatment standards in Section 728.140 or the alternative treatment standards in Section 728.145; or |
5) | |
c) | To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards specified in Section 728.140, the initial generator must test a sample of the waste extract or the entire waste, depending on whether the treatment standards are expressed as concentrations in the waste extract or the waste, or the generator may use knowledge of the waste. If the waste contains regulated constituents in excess of the applicable levels of Subpart D of this Part, the waste is prohibited from land disposal, and all requirements of this Part 728 are applicable, except as otherwise specified. |
d) | Disposal of USEPA hazardous waste number K175 wastes that have complied with all applicable Section 728.140 treatment standards must also be macroencapsulated in accordance with Table F of this Part, unless the waste is placed in one of the following: |
1) | A RCRA Subtitle C monofill containing only K175 wastes that meet all applicable Section 728.140 treatment standards; or |
2) | A dedicated RCRA Subtitle C landfill cell in which all other wastes being co-disposed are at pH£ 6.0. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.134 | Waste-Specific Prohibitions: |
a) | The following wastes are prohibited from land disposal: the wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous waste numbers D004 through D011 that are newly identified (i.e., wastes, soil, or debris identified as hazardous by the Toxic Characteristic Leaching Procedure but not the Extraction Procedure), and waste, soil, or debris from mineral processing operations that is identified as hazardous by the specifications at 35 Ill. Adm. Code 721. |
b) | The following waste is prohibited from land disposal: slag from secondary lead smelting that exhibits the characteristic of toxicity due to the presence of one or more metals. |
c) | The following wastes are prohibited from land disposal: newly identified characteristic wastes from elemental phosphorus processing; radioactive wastes mixed with USEPA hazardous waste numbers D004 through D011 wastes that are newly identified (i.e., wastes, soil, or debris identified as hazardous by the Toxic Characteristic Leaching Procedure but not the Extraction Procedure); or mixed with newly identified characteristic mineral processing wastes, soil, or debris. |
d) | This |
e) | The requirements of subsections (a) and (b) of this Section do not apply if any of the following applies to the waste: |
1) | The wastes meet the applicable treatment standards specified in Subpart D of this Part; |
2) | The Board has granted an exemption from a prohibition pursuant to a petition under Section 728.106, with respect to those wastes and units covered by the petition; |
3) | The wastes meet the applicable alternate treatment standards established pursuant to a petition granted under Section 728.144; or |
4) | USEPA has granted an extension to the effective date of a prohibition pursuant to 40 CFR 268.5, with respect to those wastes covered by the extension. |
f) | To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards specified in Section 728.140 and Table T of this Part, 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 Section 728.148 and Table U of this Part, the waste is prohibited from land disposal, and all requirements of this Part are applicable, except as otherwise specified. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.135 | |
a) | |
b) | The requirements of subsection (a) of this Section do not apply |
1) | The wastes meet the applicable treatment standards specified in Subpart D of this Part; |
2) | The Board has granted an adjusted standard that exempts waste from a prohibition pursuant to Section 728.106, with respect to those wastes and units covered by the adjusted standard; |
3) | The wastes meet an adjusted standard from an applicable treatment standard granted under Section 728.144; |
4) | The waste is hazardous debris that has met the treatment standards set forth in Section 728.140 and Table T of this Part or the alternative treatment standards in Section 728.145; or |
5) | USEPA has granted an extension to the effective date of a prohibition pursuant to 40 CFR 268.5, with respect to these wastes covered by the extension. |
c) | To determine whether a hazardous waste identified in this |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.136 | |
a) | |
b) | The requirements of subsection (a) of this Section do not apply if any of the following |
1) | The wastes meet the applicable treatment standards specified in Subpart D of this Part; |
2) | |
3) | The wastes meet the applicable treatment standards established pursuant to a petition granted under Section 728.144; |
4) | Hazardous debris has met the treatment standards in |
5) | |
c) | To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards specified in |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.137 | |
a) | The wastes specified in 35 Ill. Adm. Code 721.121 as D001 (and is not in the High TOC Ignitable Liquids Subcategory), and specified in 35 Ill. Adm. Code 721.122 as D002, that are managed in systems other than those whose discharge is regulated under the Clean Water Act (CWA), or that inject in Class I deep wells regulated under the Safe Drinking Water Act (SDWA), or that are zero dischargers that engage in CWA-equivalent treatment before ultimate land disposal, are prohibited from land disposal. CWA-equivalent treatment means biological treatment for organics, alkaline chlorination or ferrous sulfate precipitation for cyanide, precipitation/sedimentation for metals, reduction of hexavalent chromium, or other treatment technology that can be demonstrated to perform equally or greater than these technologies. |
b) | The wastes specified in 35 Ill. Adm. Code 721.121 as D001 (and is not in the High TOC Ignitable Liquids Subcategory), and specified in 35 Ill. Adm. Code 721.122 as D002, that are managed in systems defined in 35 Ill. Adm. Code 704 and 730 as Class V injection wells, that do not engage in CWA-equivalent treatment before injection, are prohibited from land disposal. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.138 | Waste-Specific Prohibitions: Newly-Identified Organic Toxicity Characteristic Wastes and Newly-Listed Coke By-Product and Chlorotoluene Production Wastes |
a) | The wastes specified in 35 Ill. Adm. Code 721.132 as |
b) | |
c) | |
d) | The requirements of subsections (a), (b), and (c) |
1) | The wastes meet the applicable treatment standards specified in |
2) | |
3) | The wastes meet the applicable alternate treatment standards established pursuant to a petition granted under Section 728.144; |
4) | |
e) | To determine whether a hazardous waste identified in this |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.139 | Waste-Specific Prohibitions: Spent Aluminum Potliners and Carbamate Wastes |
a) | The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA Hazardous Waste numbers K156-K159 and K161; and in 35 Ill. Adm. Code 721.133 as USEPA hazardous waste numbers P127, P128, P185, P188 through P192, P194, P196 through P199, P201 through P205, U271, U278 through U280, U364, U367, U372, U373, U387, U389, U394, U395, U404, and U409 through U411 are prohibited from land disposal. In addition, soil and debris contaminated with these wastes are prohibited from land disposal. |
b) | The wastes identified in 35 Ill. Adm. Code 721.123 as USEPA hazardous waste number D003 are prohibited from land disposal, other than those that are managed in a system whose discharge is regulated under 35 Ill. Adm. Code:Subtitle C, one that injects hazardous waste in Class I waste injection well regulated under 35 Ill. Adm. Code 702, 704, and 730, or one that is a zero discharger that engages in federal Clean Water Act (CWA)-equivalent treatment before ultimate land disposal. This prohibition does not apply to unexploded ordnance and other explosive devices that have been the subject of an emergency response. (Such D003 wastes are prohibited unless they meet the treatment standard of DEACT before land disposal (see Section 728.140)). |
c) | The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste number K088 are prohibited from land disposal. In addition, soil and debris contaminated with these wastes are prohibited from land disposal. |
d) | Radioactive wastes mixed with waste designated by any of USEPA hazardous waste numbers K088, K156 through K159, K161, P127, P128, P185, P188 through P192, P194, P196 through P199, P201 through P205, U271, U278 through U280, U364, U367, U372, U373, U387, U389, U394, U395, U404, and U409 through U411 are prohibited from land disposal. In addition, soil and debris contaminated with these radioactive mixed wastes are prohibited from land disposal. |
e) | This subsection corresponds with 40 CFR 268.39(e), which expired by its own terms after April 8, 1998. This statement maintains structural |
f) | The requirements of subsections (a), (b), (c), and (d) of this Section do not apply if any of the following applies to the waste: |
1) | The wastes meet the applicable treatment standards specified in Subpart D of this Part; |
2) | The person conducting the disposal has been granted an exemption from a prohibition under a petition pursuant to Section 728.106, with respect to those wastes and units covered by the petition; |
3) | The wastes meet the applicable alternative treatment standards established pursuant to a petition granted under Section 728.144; or |
4) | The person conducting the disposal has been granted an extension to the effective date of a prohibition pursuant to Section 728.105, with respect to those wastes covered by the extension. |
g) | To determine whether a hazardous waste identified in this Section exceeds the applicable treatment standards set forth in Section 728.140, the initial generator |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART D: TREATMENT STANDARDS
Section 728.140 | Applicability of Treatment Standards |
a) | A prohibited waste identified in Table T of this Part, “Treatment Standards for Hazardous Wastes,” |
1) | All hazardous constituents in the waste or in the treatment residue must be at or below the values found in Table T of this Part for that waste (total waste standards); |
2) | The hazardous constituents in the extract of the waste or in the extract of the treatment residue must be at or below the values found in Table T of this Part (waste extract standards); or |
3) | The waste must be treated using the technology specified in Table T of this Part (technology standard), which is described in detail in Table C of this Part, “Technology Codes and Description of Technology-Based Standards.” |
b) | For wastewaters, compliance with concentration level standards is based on maximums for any one day, except for D004 through D011 wastes for which the previously promulgated treatment standards based on grab samples remain in effect. For all nonwastewaters, compliance with concentration level standards is based on grab sampling. For wastes covered by the waste extract standards, the test Method 1311, the Toxicity Characteristic Leaching Procedure, found in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” |
c) | When wastes with differing treatment standards for a constituent of concern are combined for purposes of treatment, the treatment residue must meet the lowest treatment standard for the constituent of concern. |
d) | Notwithstanding the prohibitions specified in subsection (a) of this Section, treatment and disposal facilities may demonstrate (and certify pursuant to |
1) | The treatment standards for the organic constituents were established based on incineration in units operated in accordance with the technical requirements of Subpart O of 35 Ill. Adm. Code 724 |
2) | The treatment or disposal facility has used the methods referenced in subsection (d)(1) of this Section to treat the organic constituents; and |
3) | The treatment or disposal facility may demonstrate compliance with organic constituents if good-faith analytical efforts achieve detection limits for the regulated organic constituents that do not exceed the treatment standards specified in this Section and Table T of this Part by an order of magnitude. |
e) | For a characteristic waste (USEPA hazardous waste number D001 through D043) that is subject to treatment standards set forth in Table T of this Part, “Treatment Standards for Hazardous Wastes,” |
f) | The treatment standards for USEPA hazardous waste numbers F001 through F005 nonwastewater constituents carbon disulfide, cyclohexanone, or methanol apply to wastes that contain only one, two, or three of these constituents. Compliance is measured for these constituents in the waste extract from test Method 1311, the Toxicity Characteristic Leaching Procedure found in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,” |
g) | This subsection (g) corresponds with 40 CFR 268.40(g), |
h) | Prohibited USEPA hazardous waste numbers D004 through D011, mixed radioactive wastes, and mixed radioactive listed wastes containing metal constituents that were previously treated by stabilization to the treatment standards in effect at that time and then put into storage do not have to be re-treated to meet treatment standards in this Section prior to land disposal. |
i) | |
BOARD NOTE: USEPA added 40 CFR 268.40(i) at 63 Fed. Reg. 46331 (Aug. 31, 1998) to stay the Phase IV land disposal restrictions (LDRs) as they apply to zinc-containing fertilizers while it develops a more comprehensive set of regulations applicable to use of hazardous waste in making fertilizers. To effect the stay, USEPA applied the 1990 LDR standards to the affected materials.
j) | The treatment standards for the wastes specified in 35 Ill. Adm. Code 721.133 as USEPA hazardous waste numbers P185, P191, P192, P197, U364, U394, and U395 may be satisfied by either meeting the constituent concentrations presented in Table T of this Part, “Treatment Standards for Hazardous Wastes,” or by treating the waste by the following technologies: combustion, as defined by the technology code CMBST at Table C, for nonwastewaters; 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 Table C, for wastewaters. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.141 | Treatment Standards Expressed as Concentrations in Waste Extract |
For the requirements previously found in this Section and for treatment standards in Section 728.Table A to this Part, “Table CCWE-Constituent Concentrations in Waste Extracts,”, refer to Section 728.140 and 728.Table T to this Part, “Treatment Standards for Hazardous Wastes.”.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.142 | Treatment Standards Expressed as Specified Technologies |
a) | The following wastes listed in Table T of this Part, “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 Table C of this Part. |
1) | Liquid hazardous wastes containing PCBs at concentrations greater than or equal to 50 ppm but less than 500 ppm must be incinerated in accordance with the technical requirements of 40 CFR 761.70, incorporated by reference in 35 Ill. Adm. Code 720.111, or burned in high efficiency boilers in accordance with the technical requirements of 40 CFR 761.60. Liquid hazardous wastes containing PCBs at concentrations greater than or equal to 500 ppm must be incinerated in accordance with the technical requirements of 40 CFR 761.70. Thermal treatment in accordance with this Section must be in compliance with applicable regulations in 35 Ill. Adm. Code 724, 725, and 726. |
2) | Nonliquid hazardous wastes containing halogenated organic compounds (HOCs) in total concentrations greater than or equal to 1000 mg/kg and liquid HOC-containing wastes that are prohibited under Section 728.132(e)(1) must be incinerated in accordance with the requirements of Subpart O of 35 Ill. Adm. Code 724 |
3) | A mixture consisting of wastewater, the discharge of which is subject to regulation under 35 Ill. Adm. Code 309 or 310, and de minimis losses of materials from manufacturing operations in which these materials are used as raw materials or are produced as products in the manufacturing process that meet the criteria of the D001 ignitable liquids containing greater than 10 percent total organic constituents (TOC) subcategory are subject to the DEACT treatment standard described in Table C of this Part. For purposes of this subsection (a)(3), “de minimis losses” include the following: |
A) | Those from normal material handling operations (e.g., spills from the unloading or transfer of materials from bins or other containers, or leaks from pipes, valves, or other devices used to transfer materials); |
B) | Minor leaks from process equipment, storage tanks, or containers; |
C) | Leaks from well-maintained pump packings and seals; |
D) | Sample purgings; and |
E) | Relief device discharges. |
b) | Any person may submit an application to the Agency demonstrating that an alternative treatment method can achieve a level of performance equivalent to that achievable by methods specified in subsections (a), (c), and (d) of this Section for wastes or specified in Table F of this Part for hazardous debris. The applicant |
c) | As an alternative to the otherwise applicable treatment standards of Subpart D of this Part, lab packs are eligible for land disposal provided the following requirements are met: |
1) | The lab packs comply with the applicable provisions of 35 Ill. Adm. Code 724.416 and 725.416; |
BOARD NOTE: 35 Ill. Adm. Code 729.301 and 729.312 include additional restrictions on the use of lab packs.
2) | The lab pack does not contain any of the wastes listed in Appendix D of this Part; |
3) | The lab packs are incinerated in accordance with the requirements of Subpart O of 35 Ill. Adm. Code 724 |
4) | Any incinerator residues from lab packs containing D004, D005, D006, D007, D008, D010, and D011 are treated in compliance with the applicable treatment standards specified for such wastes in Subpart D of this Part. |
d) | Radioactive hazardous mixed wastes are subject to the treatment standards in Section 728.140 and Table T of this Part. Where treatment standards are specified for radioactive mixed wastes in Table T of this Part, “Table of Treatment Standards,” |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.143 | Treatment Standards Expressed as Waste Concentrations |
For the requirements previously found in this Section and for treatment standards in Section 728.Table A to this Part, “CCW-Constituent Concentrations in Wastes,”, refer to Section 728.140 and 728.Table T to this Part, “Treatment Standards for Hazardous Wastes.”.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.144 | Adjustment of Treatment Standard |
a) | Based on a petition filed by a generator or treater of hazardous waste, the Board will grant an adjusted standard from an applicable treatment standard if the petitioner can demonstrate that either of the following applies to treatment of the waste: |
1) | It is not physically possible to treat the waste to the level specified in the treatment standard, or by the method specified as the treatment standard. To show that this is the case, the petitioner must demonstrate that because the physical or chemical properties of the waste differ significantly from waste analyzed in developing the treatment standard, the waste cannot be treated to the specified level or by the specified method; or |
2) | It is inappropriate to require the waste to be treated to the level specified in the treatment standard or by the method specified as the treatment standard, even though such treatment is technically possible. To show that this is the case, the petitioner must demonstrate that either of the following applies to treatment of the waste: |
A) | Treatment to the specified level or by the specified method is technically inappropriate (for example, resulting in combustion of large amounts of mildly contaminated environmental media); or |
B) | For remediation waste only, treatment to the specified level or by the specified method is environmentally inappropriate because it would likely discourage aggressive remediation. |
BOARD NOTE: 40 CFR 268.44 refers to these as “treatability variances.”. The Board has not used this term in its rules to avoid confusion with the Board variances under Title IX of the Environmental Protection Act. The equivalent Board procedures are an “adjusted standard from a treatment standard” pursuant to subsections (a) through (l) (m) of this Section, or a “treatability exception” adopted pursuant to subsections (m) et seq. subsection (p) of this Section. While the latter is adopted by “identical in substance” rulemaking following a USEPA action, the former is an original Board action which that will be the only mechanism following authorization to the State of this component of the RCRA program.
b) | Each petition must be submitted in accordance with the procedures in Subpart D of 35 Ill. Adm. Code |
c) | Each petition must include the following statement signed by the petitioner or an authorized representative: |
I certify under penalty of law that I have personally examined and am familiar with the information submitted in this petition and all attached documents, and that, based on my inquiry of those individuals immediately responsible for obtaining the information, I believe that the submitted information is true, accurate and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment.
d) | After receiving a petition for an adjusted treatment standard, the Board may request any additional information or samples |
e) | The Board will give public notice and provide an opportunity for public comment, as provided in Subpart D of 35 Ill. Adm. Code |
f) | A generator, treatment facility or disposal facility that is managing a waste covered by an adjusted treatment standard |
g) | During the petition review process, the applicant is required to comply with all restrictions on land disposal under this Part once the effective date for the waste has been reached. |
h) | Based on a petition filed by a generator or treater of hazardous waste, the Board will grant an |
1) | It is not physically possible to treat the waste to the level specified in the treatment standard, or by the method specified as the treatment standard. To show that this is the case, the petitioner must demonstrate that because the physical or chemical properties of the waste differ significantly from waste analyzed in developing the treatment standard, the waste cannot be treated to the specified level or by the specified method; or |
2) | It is inappropriate to require the waste to be treated to the level specified in the treatment standard or by the method specified as the treatment standard, even though such treatment is technically possible. To show that this is the case, the petitioner must demonstrate that either of the following applies to treatment of the waste: |
A) | Treatment to the specified level or by the specified method is technically inappropriate (for example, resulting in combustion of large amounts of mildly contaminated environmental media where the treatment standard is not based on combustion of such media); or |
B) | For remediation waste only, treatment to the specified level or by the specified method is environmentally inappropriate because it would likely discourage aggressive remediation. |
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. An adjusted standard from a treatment standard granted under this subsection (h)(3) will include the following features: |
A) | At a minimum, the adjusted standard from the treatment standard will impose an alternative land disposal restriction treatment standard that will achieve the following, using a reasonable maximum exposure scenario: |
i) | For carcinogens, it will achieve constituent concentrations that result in the total excess risk to an individual exposed over a lifetime, generally falling within a range from 10-4 to 10-6; and |
ii) | For constituents with non-carcinogenic effects, it will achieve constituent concentrations that an individual could be exposed to on a daily basis without appreciable risk of deleterious effect during a lifetime. |
B) | The treatment adjusted standard will not consider post-land-disposal controls. |
4) | For contaminated soil only, treatment to the level or by the method specified in the soil treatment standards would result in concentrations of hazardous constituents that are below (i.e., lower than) natural background concentrations at the site where the contaminated soil will be land disposed. |
5) | The Board will follow the procedures of Section 28.1 of the Act and Subpart D of 35 Ill. Adm. Code |
i) | Each petition for a site-specific adjusted treatment standard must include the information in 35 Ill. Adm. Code 720.120(b)(1) through (b)(4). |
j) | After receiving a petition for a site-specific adjusted treatment standard, the Board may request any additional information or samples |
k) | A generator, treatment facility or disposal facility |
l) | During the petition review process, the petitioner for a site-specific adjusted treatment standard |
m) | For any adjusted standard from a treatment standard, the petitioner must also demonstrate that compliance with the requested adjusted standard is sufficient to minimize threats to human health and the environment posed by land disposal of the waste. In evaluating this demonstration, the Board will take into account whether the adjusted standard should be granted if the subject waste is to be used in a manner constituting disposal pursuant to Sections 728.120 through 728.123. |
n) | This subsection (n) corresponds with 40 CFR 264.1030(n), marked “reserved” by USEPA. This statement maintains structural consistency with |
o) | The facilities listed in Table H of this Part are excluded from the treatment standards under |
p) | If USEPA grants a treatability exception by regulatory action pursuant to 40 CFR 268.44 |
BOARD NOTE: The Board will adopt the treatability exception during a RCRA update Docket if a timely demonstration is made. Otherwise, the Board will assign the matter to a separate Docket.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.145 | Treatment Standards for Hazardous Debris |
a) | Treatment standards. Hazardous debris must be treated prior to land disposal as follows, unless the |
1) | General. Hazardous debris must be treated for each “contaminant subject to treatment,” |
2) | Characteristic debris. Hazardous debris that exhibits the characteristic of ignitability, corrosivity, or reactivity identified under 35 Ill. Adm. Code 721.121, 721.122, or 721.123, respectively, must be deactivated by treatment using one of the technologies identified in Table F of this Part. |
3) | Mixtures of debris types. The treatment standards of Table F of this Part must be achieved for each type of debris contained in a mixture of debris types. If an immobilization technology is used in a treatment train, it must be the last treatment technology used. |
4) | Mixtures of contaminant types. Debris that is contaminated with two or more contaminants subject to treatment identified under subsection (b) of this Section must be treated for each contaminant using one or more treatment technologies identified in Table F of this Part. If an immobilization technology is used in a treatment train, it must be the last treatment technology used. |
5) | Waste PCBs. Hazardous debris that is also a waste PCB under 40 CFR 761 is subject to the requirements of either 40 CFR 761 or the requirements of this Section, whichever are more stringent. |
b) | Contaminants subject to treatment. Hazardous debris must be treated for each “contaminant subject to treatment.” |
1) | Toxicity characteristic debris. The contaminants subject to treatment for debris that exhibits the Toxicity Characteristic (TC) by 35 Ill. Adm. Code 721.124 are those EP constituents for which the debris exhibits the TC toxicity characteristic. |
2) | Debris contaminated with listed waste. The contaminants subject to treatment for debris that is contaminated with a prohibited listed hazardous waste are those constituents or wastes for which treatment standards are established for the waste under Section 728.140 and Table T of this Part. |
3) | Cyanide reactive debris. Hazardous debris that is reactive because of cyanide must be treated for cyanide. |
c) | Conditioned exclusion of treated debris. Hazardous debris that has been treated using one of the specified extraction or destruction technologies in Table F of this Part and that does not exhibit a characteristic of hazardous waste identified under Subpart C of 35 Ill. Adm. Code 721 |
d) | Treatment residuals. |
1) | General requirements. Except as provided by subsections (d)(2) and (d)(4) of this Section: |
A) | Residue from the treatment of hazardous debris must be separated from the treated debris using simple physical or mechanical means; and |
B) | Residue from the treatment of hazardous debris is subject to the waste-specific treatment standards provided by Subpart D of this Part for the waste contaminating the debris. |
2) | Nontoxic debris. Residue from the deactivation of ignitable, corrosive, or reactive characteristic hazardous debris (other than cyanide-reactive) that is not contaminated with a contaminant subject to treatment defined by subsection (b) of this Section, must be deactivated prior to land disposal and is not subject to the waste-specific treatment standards of Subpart D of this Part. |
3) | Cyanide-reactive debris. Residue from the treatment of debris that is reactive because of cyanide must meet the standards for USEPA hazardous waste number D003 under Section 728.140 and Table T of this Part. |
4) | Ignitable nonwastewater residue. Ignitable nonwastewater residue containing equal to or greater than 10 percent total organic carbon is subject to the technology specified in the treatment standard for USEPA hazardous waste number D001: Ignitable Liquids. |
5) | Residue from spalling. Layers of debris removed by spalling are hazardous debris that |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.146 | Alternative Treatment Standards Based on HTMR |
For the treatment standards previously found in Section 728.Table G to this Part, as formerly referenced in this Section, refer to Sections Section 728.140 and 728.Table T to this Part, “Treatment Standards for Hazardous Wastes.”.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.148 | Universal Treatment Standards |
Section 728.Table U to this Part, “Universal Treatment Standards (UTS),”, identifies the hazardous constituents, along with the nonwastewater and wastewater treatment standard levels, that are used to regulate most prohibited hazardous wastes with numerical limits. For determining compliance with treatment standards for underlying hazardous constituents, as defined in Section 728.102(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 Section 728.Table U to this Part.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.149 | Alternative LDR Treatment Standards for Contaminated Soil |
a) | Applicability. An owner or operator must comply with LDRs prior to placing soil that exhibits a characteristic of hazardous waste or which exhibited a characteristic of hazardous waste at the time it was generated into a land disposal unit. The following chart describes whether an owner or operator must comply with LDRs prior to placing soil contaminated by listed hazardous waste into a land disposal unit: |
If the LDRs |
And if the LDRs |
And if |
Then the owner or operator |
Applied to the listed waste when it contaminated the soil*. |
Apply to the listed waste now. |
— |
Must comply with LDRs. |
Did not 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. |
Did not 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. |
Needs not comply with LDRs. |
Did not apply to the listed waste when it contaminated the soil*. |
Do not apply to the listed waste now. |
— |
Needs not comply with LDRs. |
* For dates of LDR applicability, see Appendix G of this Part. To determine the date any given listed hazardous waste contaminated any given volume of soil, use the last date any given listed hazardous waste was placed into any given land disposal unit or, in the case of an accidental spill, the date of the spill. | |
b) | Prior to land disposal, contaminated soil identified by subsection (a) of this Section as needing to comply with LDRs must be treated according to the applicable treatment standards specified in subsection (c) of this Section or according to the universal treatment standards specified in Section 728.148 and Table U of this Part applicable to the contaminating listed hazardous waste or the applicable characteristic of hazardous waste if the soil is characteristic. The treatment standards specified in subsection (c) of this Section and the universal treatment standards may be modified through a treatment variance approved in accordance with Section 728.144. |
c) | Treatment standards for contaminated soils. Prior to land disposal, contaminated soil identified by subsection (a) of this Section as needing to comply with LDRs must be treated according to all the standards specified in this subsection (c) or according to the universal treatment standards specified in Section 728.148 and Table U of this Part. |
1) | All soils. Prior to land disposal, all constituents subject to treatment must be treated as follows: |
A) | For non-metals except carbon disulfide, cyclohexanone, and methanol, treatment must achieve 90 percent reduction in total constituent concentrations, except as provided by subsection (c)(1)(C) of this Section. |
B) | For metals and carbon disulfide, cyclohexanone, and methanol, treatment must achieve 90 percent reduction in constituent concentrations as measured in leachate from the treated media (tested according to the TCLP) or 90 percent reduction in total constituent concentrations (when a metal removal treatment technology is used), except as provided by subsection (c)(1)(C) of this Section. |
C) | When treatment of any constituent subject to treatment to a 90 percent reduction standard would result in a concentration less than 10 times the universal treatment standard for that constituent, treatment to achieve constituent concentrations less than 10 times the universal treatment standard is not required. The universal treatment standards are identified in Table U of this Part. |
2) | Soils that exhibit the characteristic of ignitability, corrosivity or reactivity. In addition to the treatment required by subsection (c)(1) of this Section, prior to land disposal, soils that exhibit the characteristic of ignitability, corrosivity, or reactivity must be treated to eliminate these characteristics. |
3) | Soils that contain nonanalyzable constituents. In addition to the treatment requirements of subsections (c)(1) and (c)(2) of this Section, prior to land disposal, the following treatment is required for soils that contain nonanalyzable constituents: |
A) | For soil that contains only analyzable and nonanalyzable organic constituents, treatment of the analyzable organic constituents to the levels specified in subsections (c)(1) and (c)(2) of this Section; or |
B) | For soil that contains only nonanalyzable constituents, treatment by the methods specified in Section 728.142 for the waste contained in the soil. |
d) | Constituents subject to treatment. When applying the soil treatment standards in subsection (c) of this Section, constituents subject to treatment are any constituents listed in Table U of this Part, entitled “Universal Treatment Standards,” that are reasonably expected to be present in any given volume of contaminated soil, except fluoride, selenium, sulfides, vanadium, zinc, and that are present at concentrations greater than ten times the universal treatment standard. PCBs are not constituents subject to treatment in any given volume of soil that exhibits the toxicity characteristic solely because of the presence of metals. |
e) | Management of treatment residuals. Treatment residuals from treating contaminated soil identified by subsection (a) of this Section as needing to comply with LDRs must be managed as follows: |
1) | Soil residuals are subject to the treatment standards of this Section; |
2) | Non-soil residuals are subject to the following requirements: |
A) | For soils contaminated by listed hazardous waste, the RCRA Subtitle C standards applicable to the listed hazardous waste; and |
B) | For soils that exhibit a characteristic of hazardous waste, if the non-soil residual also exhibits a characteristic of hazardous waste, the treatment standards applicable to the characteristic hazardous waste. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
SUBPART E: PROHIBITIONS ON STORAGE
Section 728.150 | Prohibitions on Storage of Restricted Wastes |
a) | Except as provided in this Section, the storage of hazardous wastes restricted from land disposal under Subpart C of this Part is prohibited, unless the following conditions are met: |
1) | A generator stores such wastes in tanks, containers, or containment buildings on-site solely for the purpose of the accumulation of such quantities of hazardous waste as necessary to facilitate proper recovery, treatment, or disposal and the generator complies with the requirements in 35 Ill. Adm. Code 722.134 and 35 Ill. Adm. Code 724 and 725. (A generator that is in existence on the effective date of a regulation under this Part and which must store hazardous wastes for longer than 90 days due to the regulations under this Part becomes an owner or operator of a storage facility and |
2) | An owner or operator of a hazardous waste treatment, storage, or disposal facility stores such wastes in tanks, containers, or containment buildings solely for the purpose of the accumulation of such quantities of hazardous waste as necessary to facilitate proper recovery, treatment, or disposal and each of the following conditions are fulfilled: |
A) | Each container is clearly marked to identify its contents and the date each period of accumulation begins; and |
B) | Each tank is clearly marked with a description of its contents, the quantity of each hazardous waste received and the date each period of accumulation begins, or such information is recorded and maintained in the operating record at the facility. Regardless of whether the tank itself is marked, the owner and operator |
3) | A transporter stores manifested shipments of such wastes at a transfer facility for 10 days or less. |
b) | An owner or operator of a treatment, storage, or disposal facility may store such wastes for up to one year unless the Agency can demonstrate that such storage was not solely for the purpose of accumulation of such quantities of hazardous waste as are necessary to facilitate proper recovery, treatment, or disposal. |
c) | An owner or operator of a treatment, storage, or disposal facility may store wastes beyond one year; however, the owner or operator bears the burden of proving that such storage was solely for the purpose of accumulation of such quantities of hazardous waste as are necessary to facilitate proper recovery, treatment, or disposal. |
d) | If a generator’s waste is exempt from a prohibition on the type of land disposal utilized for the waste (for example, because of an approved case-by-case extension under 40 CFR 268.5, incorporated by reference in Section 728.105, an approved Section 728.106 petition or a national capacity variance under 40 CFR 268, Subpart C), the prohibition in subsection (a) does not apply during the period of such exemption. |
e) | The prohibition in subsection (a) of this Section does not apply to hazardous wastes that meet the treatment standards specified under Sections 728.141, 728.142, and 728.143 or the adjusted treatment standards specified under Section 728.144, or, where treatment standards have not been specified, the waste is in compliance with the applicable prohibitions specified in Section 728.132 or 728.139. |
f) | Liquid hazardous wastes containing PCBs at concentrations greater than or equal to 50 ppm must be stored at a facility that meets the requirements of 40 CFR 761.65(b), incorporated by reference in 35 Ill. Adm. Code 720.111, and must be removed from storage and treated or disposed as required by the Part within one year of the date when such wastes are first placed into storage. The provisions of subsection (c) of this Section do not apply to such PCB wastes prohibited under Section 728.132. |
g) | The prohibition and requirements in this Section do not apply to hazardous remediation wastes stored in a staging pile approved pursuant to 35 Ill. Adm. Code 724.654. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Appendix C | |
List of Halogenated Organic Compounds Regulated under Section 728.132 | |
In determining the concentration of halogenated organic compounds (HOCs) in a hazardous waste for purposes of the Section 728.132 land disposal prohibition, USEPA has defined the HOCs that must be included in a calculation as any compounds having a carbon-halogen bond which that are listed in this Appendix (see Section 728.102). This Appendix C to Part 728 consists of the following compounds:
I. Volatiles
1. | Bromodichloromethane |
2. | Bromomethane |
3. | Carbon Tetrachloride |
4. | Chlorobenzene |
5. | 2-Chloro-1,3-butadiene |
6. | Chlorodibromomethane |
7. | Chloroethane |
8. | 2-Chloroethyl vinyl ether |
9. | Chloroform |
10. | Chloromethane |
11. | 3-Chloropropene |
12. | 1,2-Dibromo-3-chloropropane |
13. | 1,2-Dibromomethane |
14. | Dibromomethane |
15. | Trans-1,4-Dichloro-2--butene |
16. | Dichlorodifluoromethane |
17. | 1,1-Dichloroethane |
18. | 1,2-Dichloroethane |
19. | 1,1-Dichloroethylene |
20. | Trans-1,2-Dichloroethene |
21. | 1,2-Dichloropropane |
22. | Trans-1,3-Dichloropropene |
23. | cis-1,3-Dichloropropene |
24. | Iodomethane |
25. | Methylene chloride |
26. | 1,1,1,2-Tetrachloroethane |
27. | 1,1,2,2-Tetrachloroethane |
28. | Tetrachloroethene |
29. | Tribromomethane |
30. | 1,1,1-Trichloroethane |
31. | 1,1,2-Trichloroethane |
32. | Trichloroethene |
33. | Trichloromonofluoromethane |
34. | 1,2,3-Thrichloropropane |
35. | Vinyl Chloride |
II. Semivolatiles
1. | Bis(2-chloroethoxy)ethane |
2. | Bis(2-chloroethyl)ether |
3. | Bis(2-chloroisopropyl)ether |
4. | p-Chloroaniline |
5. | Chlorobenzilate |
6. | p-Chloro-m-cresol |
7. | 2-Chloronaphthalene |
8. | 2-Chlorophenol |
9. | 3-Chloropropionitrile |
10. | m-Dichlorobenzene |
11. | o-Dichlorobenzene |
12. | p-Dichlorobenzene |
13. | 3.3'-Dichlorobenzidine |
14. | 2,4-Dichlorophenol |
15. | 2,6-Dichlorophenol |
16. | Hexachlorobenzene |
17. | Hexachlorobutadiene |
18. | Hexachlorocyclopentadiene |
19. | Hexachloroethane |
20. | Hexachlorophene |
21. | Hexachloropropene |
22. | 4,4'-Methylenebis(2-chloroanaline) |
23. | Pentachlorobenzene |
24. | Pentachloroethane |
25. | Pentachloronitrobenzene |
26. | Pentachlorophenol |
27. | Pronamide |
28. | 1,2,4,5-Tetrachlorobenzene |
29. | 2,3,4,6-Tetrachlorophenol |
30. | 1,2,4-Trichlorobenzene |
31. | 2,4,5-Trichlorophenol |
32. | 2,4,6-Trichlorophenol |
33. | Tris(2,3-dibromopropyl)phosphate |
III. Organochlorine Pesticides
1. | Aldrin |
2. | alpha-BHC |
3. | beta-BHC |
4. | delta-BHC |
5. | gamma-BHC |
6. | Chlorodane |
7. | DDD |
8. | DDE |
9. | DDT |
10. | Dieldrin |
11. | Endosulfan I |
12. | Endosulfan II |
13. | Endrin |
14. | Endrin aldehyde |
15. | Heptachlor |
16. | Heptachlor epoxide |
17. | Isodrin |
18. | Kepone |
19. | Methoxyclor |
20. | Toxaphene |
IV. Phenoxyacetic Acid Herbicides
1. | 2,4-Dichlorophenoxyacetic acid |
2. | Silvex |
3. | 2,4,5-T |
V. PCBs
1. | Aroclor 1016 |
2. | Aroclor 1221 |
3. | Aroclor 1232 |
4. | Aroclor 1242 |
5. | Aroclor 1248 |
6. | Aroclor 1254 |
7. | Aroclor 1260 |
8. | PCBs not otherwise specified |
VI. Dioxins and Furans
1. | Hexachlorodibenzo-p-dioxins |
2. | Hexachlorodibenzofuran |
3. | Pentachlorodibenzo-p-dioxins |
4. | Pentachlorodibenzofuran |
5. | Tetrachlorodibenzo-p-dioxins |
6. | Tetrachlorodibenzofuran |
7. | 2,3,7,8-Tetrachlorodibenzo-p-dioxin |
BOARD NOTE: Derived from 40 CFR 268, Appendix III, as added at 65 Fed. Reg. 81340 (December 26, 2000) (2002).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Appendix D | |
Wastes Excluded from Lab Packs | |
Hazardous waste with the following U.S. EPA USEPA hazardous waste codes may not be placed in lab packs under the alternative lab pack treatment standards of Section 728.142(c): D009, F019, K003, K004, K005, K006, K062, K071, K100, K106, P010, P011, P012, P076, P078, U134, and U151.
BOARD NOTE: 35 Ill. Adm. Code 729.301 and 729.312 include additional limitations on the use of lab packs.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Appendix F | |
Technologies to Achieve Deactivation of Characteristics | |
The treatment standard for many characteristic wastes is stated in the Section 728.Table T of this Part, entitled “Treatment Standards for Hazardous Wastes,” as “DEACT and meet Section 728.148 standards.” USEPA 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 CWA or in a CWA-equivalent facility, and that also contain underlying hazardous constituents (see Section 728.102(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. This appendix Appendix F presents a partial list of technologies, utilizing the five letter technology codes established in Table C of this Part, that may be useful in meeting the treatment standard. Use of these specific technologies is not mandatory and does not preclude direct reuse, recovery or the use of other pretreatment technologies, provided deactivation is achieved and underlying hazardous constituents are treated to achieve the UTS.
Waste code/subcategory |
Nonwastewaters |
Wastewaters |
D001 Ignitable Liquids based on 35 Ill. Adm. Code 721.121(a)(1)—Low TOC Nonwastewater Subcategory (containing one percent to <10 percent TOC) |
RORGS WETOX INCIN CHOXD BIODG |
n.a. |
D001 Ignitable Liquids based on 35 Ill. Adm. Code 721.121(a)(1)—Ignitable Wastewater Subcategory (containing < |
n.a. |
WETOX RORGS INCIN CHOXD BIODG |
D001 Compressed Gases based on 35 Ill. Adm. Code 721.121(a)(3) |
RCGAS FSUBS INCIN ADGAS fb. INCIN ADGAS fb. (CHOXD; or CHRED) |
n.a. |
D001 Ignitable Reactives based on 35 Ill. Adm. Code 721.121(a)(2) |
WTRRX CHOXD CHRED STABL INCIN |
n.a. |
D001 Ignitable Oxidizers based on 35 Ill. Adm. Code 721.121(a)(4) |
CHRED INCIN |
CHRED INCIN |
D002 Acid Subcategory based on 35 Ill. Adm. Code 721.122(a)(1) with pH less than or equal to |
RCORR NEUTR INCIN |
NEUTR INCIN |
D002 Alkaline Subcategory based on 35 Ill. Adm. Code 721.122(a)(1) with pH greater than or equal to 12.5 |
NEUTR INCIN |
NEUTR INCIN |
D002 Other Corrosives based on 35 Ill. Adm. Code 721.122(a)(2) |
CHOXD CHRED INCIN STABL |
CHOXD CHRED INCIN |
D003 Water Reactives based on 35 Ill. Adm. Code 721.123(a)(2), (a)(3), and (a)(4) |
INCIN WTRRX CHOXD CHRED |
n.a. |
D003 Reactive Sulfides based on 35 Ill. Adm. Code 721.123(a)(5) |
CHOXD CHRED INCIN STABL |
CHOXD CHRED BIODG INCIN |
D003 Explosives based on 35 Ill. Adm. Code 721.123(a) |
INCIN CHOXD CHRED |
INCIN CHOXD CHRED BIODG CARBN |
D003 Other Reactives based on 35 Ill. Adm. Code 721.123(a)(1) |
INCIN CHOXD CHRED |
INCIN CHOXD CHRED BIODG CARBN |
K044 Wastewater treatment sludges from the manufacturing and processing of explosives |
CHOXD CHRED INCIN |
CHOXD CHRED BIODG CARBN INCIN |
K045 Spent carbon from the treatment of wastewaters containing explosives |
CHOXD CHRED INCIN |
CHOXD CHRED BIODG CARBN INCIN |
K047 Pink/red water from TNT operations |
CHOXD CHRED INCIN |
CHOXD CHRED BIODG CARBN INCIN |
Note: “n.a.” stands for “not applicable.”.
“fb.” Stands for “followed by.”.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Appendix G | |
Federal Effective Dates | |
The following are the effective dates for the USEPA rules in 40 CFR 268. These generally became effective as Illinois rules at a later date.
TABLE 1
EFFECTIVE DATES OF SURFACE DISPOSED WASTES (NON-SOIL AND DEBRIS) REGULATED IN THE LDRSa—COMPREHENSIVE LIST
Waste code |
Waste category |
Effective date |
D001c |
All (except High TOC Ignitable Liquids) |
|
D001 |
High TOC Ignitable Liquids |
|
D002c |
All |
|
D003e |
Newly identified surface-disposed elemental phosphorus processing wastes |
May 26, 2000 |
D004 |
Newly identified D004 and mineral processing wastes |
|
D004 |
Mixed radioactive/newly identified D004 or mineral processing wastes |
May 26, 2000 |
D005 |
Newly identified D005 and mineral processing wastes |
|
D005 |
Mixed radioactive/newly identified D005 or mineral processing wastes |
May 26, 2000 |
D006 |
Newly identified D006 and mineral processing wastes |
|
D006 |
Mixed radioactive/newly identified D006 or mineral processing wastes |
May 26, 2000 |
D007 |
Newly identified D007 and mineral processing wastes |
|
D007 |
Mixed radioactive/newly identified D007or mineral processing wastes |
May 26, 2000 |
D008 |
Newly identified D008 and mineral processing waste |
|
D008 |
Mixed radioactive/newly identified D008 or mineral processing wastes |
May 26, 2000 |
D009 |
Newly identified D009 and mineral processing waste |
|
D009 |
Mixed radioactive/newly identified D009or mineral processing wastes |
May 26, 2000 |
D010 |
Newly identified D010 and mineral processing wastes |
|
D010 |
Mixed radioactive/newly identified D010 or mineral processing wastes |
May 26, 2000 |
D011 |
Newly identified D011 and mineral processing wastes |
|
D011 |
Mixed radioactive/newly identified D011or mineral processing wastes |
May 26, 2000 |
D012 (that exhibit the toxicity characteristic based on the TCLP)d |
All |
|
D013 (that exhibit the toxicity characteristic based on the TCLP)d |
All |
|
D014 (that exhibit the toxicity characteristic based on the TCLP)d |
All |
|
D015 (that exhibit the toxicity characteristic based on the TCLP)d |
All |
|
D016 (that exhibit the toxicity characteristic based on the TCLP)d |
All |
|
D017 (that exhibit the toxicity characteristic based on the TCLP)d |
All |
|
D018 |
Mixed with radioactive wastes |
|
D018 |
All others |
|
D019 |
Mixed with radioactive wastes |
|
D019 |
All others |
|
D020 |
Mixed with radioactive wastes |
|
D020 |
All others |
|
D021 |
Mixed with radioactive wastes |
|
D021 |
All others |
|
D022 |
Mixed with radioactive wastes |
|
D022 |
All others |
|
D023 |
Mixed with radioactive wastes |
|
D023 |
All others |
|
D024 |
Mixed with radioactive wastes |
|
D024 |
All others |
|
D025 |
Mixed with radioactive wastes |
|
D025 |
All others |
|
D026 |
Mixed with radioactive wastes |
|
D026 |
All others |
|
D027 |
Mixed with radioactive wastes |
|
D027 |
All others |
|
D028 |
Mixed with radioactive wastes |
|
D028 |
All others |
|
D029 |
Mixed with radioactive wastes |
|
D029 |
All others |
|
D030 |
Mixed with radioactive wastes |
|
D030 |
All others |
|
D031 |
Mixed with radioactive wastes |
|
D031 |
All others |
|
D032 |
Mixed with radioactive wastes |
|
D032 |
All others |
|
D033 |
Mixed with radioactive wastes |
|
D033 |
All others |
|
D034 |
Mixed with radioactive wastes |
|
D034 |
All others |
|
D035 |
Mixed with radioactive wastes |
|
D035 |
All others |
|
D036 |
Mixed with radioactive wastes |
|
D036 |
All others |
|
D037 |
Mixed with radioactive wastes |
|
D037 |
All others |
|
D038 |
Mixed with radioactive wastes |
|
D038 |
All others |
|
D039 |
Mixed with radioactive wastes |
|
D039 |
All others |
|
D040 |
Mixed with radioactive wastes |
|
D040 |
All others |
|
D041 |
Mixed with radioactive wastes |
|
D041 |
All others |
|
D042 |
Mixed with radioactive wastes |
|
D042 |
All others |
|
D043 |
Mixed with radioactive wastes |
|
D043 |
All others |
|
F001 |
Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids |
|
F001 |
All others |
|
F002 (1,1,2-trichloroethane) |
Wastewater and Nonwastewater |
|
F002 |
Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids |
|
F002 |
All others |
|
F003 |
Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids |
|
F003 |
All others |
|
F004 |
Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids |
|
F004 |
All others |
|
F005 (benzene, 2-ethoxy ethanol, 2-nitropropane) |
Wastewater and Nonwastewater |
|
F005 |
Small quantity generators, CERCLA response/RCRA corrective action, initial generator’s solvent-water mixtures, solvent-containing sludges and solids |
|
F005 |
All others |
|
F006 |
Wastewater |
|
F006 |
Nonwastewater |
|
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 |
|
F011 |
All others |
July 8, 1989 |
F012 (cyanides) |
Nonwastewater |
|
F012 |
All others |
July 8, 1989 |
F019 |
All |
|
F020 |
All |
|
F021 |
All |
|
F025 |
All |
|
F026 |
All |
|
F027 |
All |
|
F028 |
All |
|
F032 |
Mixed with radioactive wastes |
May 12, 1999 |
F032 |
All others |
|
F034 |
Mixed with radioactive wastes |
May 12, 1999 |
F034 |
All others |
|
F035 |
Mixed with radioactive wastes |
May 12, 1999 |
F035 |
All others |
|
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 |
|
F039 |
Nonwastewater |
May 8, 1992 |
K001 (organics)b |
All |
|
K001 |
All others |
|
K002 |
All |
|
K003 |
All |
|
K004 |
Wastewater |
|
K004 |
Nonwastewater |
|
K005 |
Wastewater |
|
K005 |
Nonwastewater |
June 8, 1989 |
K006 |
All |
|
K007 |
Wastewater |
|
K007 |
Nonwastewater |
June 8, 1989 |
K008 |
Wastewater |
|
K008 |
Nonwastewater |
|
K009 |
All |
June 8, 1989 |
K010 |
All |
June 8, 1989 |
K011 |
Wastewater |
|
K011 |
Nonwastewater |
June 8, 1989 |
K013 |
Wastewater |
|
K013 |
Nonwastewater |
June 8, 1989 |
K014 |
Wastewater |
|
K014 |
Nonwastewater |
June 8, 1989 |
K015 |
Wastewater |
|
K015 |
Nonwastewater |
|
K016 |
All |
|
K017 |
All |
|
K018 |
All |
|
K019 |
All |
|
K020 |
All |
|
K021 |
Wastewater |
|
K021 |
Nonwastewater |
|
K022 |
Wastewater |
|
K022 |
Nonwastewater |
|
K023 |
All |
June 8, 1989 |
K024 |
All |
|
K025 |
Wastewater |
|
K025 |
Nonwastewater |
|
K026 |
All |
|
K027 |
All |
June 8, 1989 |
K028 (metals) |
Nonwastewater |
|
K028 |
All others |
June 8, 1989 |
K029 |
Wastewater |
|
K029 |
Nonwastewater |
June 8, 1989 |
K030 |
All |
|
K031 |
Wastewater |
|
K031 |
Nonwastewater |
May 8, 1992 |
K032 |
All |
|
K033 |
All |
|
K034 |
All |
|
K035 |
All |
|
K036 |
Wastewater |
June 8, 1989 |
K036 |
Nonwastewater |
|
K037b |
Wastewater |
|
K037 |
Nonwastewater |
|
K038 |
All |
June 8, 1989 |
K039 |
All |
June 8, 1989 |
K040 |
All |
June 8, 1989 |
K041 |
All |
|
K042 |
All |
|
K043 |
All |
June 8, 1989 |
K044 |
All |
|
K045 |
All |
|
K046 (Nonreactive) |
Nonwastewater |
|
K046 |
All others |
|
K047 |
All |
|
K048 |
Wastewater |
|
K048 |
Nonwastewater |
|
K049 |
Wastewater |
|
K049 |
Nonwastewater |
|
K050 |
Wastewater |
|
K050 |
Nonwastewater |
|
K051 |
Wastewater |
|
K051 |
Nonwastewater |
|
K052 |
Wastewater |
|
K052 |
Nonwastewater |
|
K060 |
Wastewater |
|
K060 |
Nonwastewater |
|
K061 |
Wastewater |
|
K061 |
Nonwastewater |
June 30, 1992 |
K062 |
All |
|
K069 |
Nonwastewater |
|
K069 |
All others |
|
K071 |
All |
|
K073 |
All |
|
K083 |
All |
|
K084 |
Wastewater |
|
K084 |
Nonwastewater |
May 8, 1992 |
K085 |
All |
|
K086 (organics)b |
All |
|
K086 |
All others |
|
K087 |
All |
|
K088 |
Mixed with radioactive wastes |
|
K088 |
All others |
|
K093 |
All |
June 8, 1989 |
K094 |
All |
June 8, 1989 |
K095 |
Wastewater |
|
K095 |
Nonwastewater |
June 8, 1989 |
K096 |
Wastewater |
|
K096 |
Nonwastewater |
June 8, 1989 |
K097 |
All |
|
K098 |
All |
|
K099 |
All |
|
K100 |
Wastewater |
|
K100 |
Nonwastewater |
|
K101 (organics) |
Wastewater |
|
K101 (metals) |
Wastewater |
|
K101 (organics) |
Nonwastewater |
|
K101 (metals) |
Nonwastewater |
May 8, 1992 |
K102 (organics) |
Wastewater |
|
K102 (metals) |
Wastewater |
|
K102 (organics) |
Nonwastewater |
|
K102 (metals) |
Nonwastewater |
May 8, 1992 |
K103 |
All |
|
K104 |
All |
|
K105 |
All |
|
K106 |
Wastewater |
|
K106 |
Nonwastewater |
May 8, 1992 |
K107 |
Mixed with radioactive wastes |
June 30, 1994 |
K107 |
All others |
|
K108 |
Mixed with radioactive wastes |
June 30, 1994 |
K108 |
All others |
|
K109 |
Mixed with radioactive wastes |
June 30, 1994 |
K109 |
All others |
|
K110 |
Mixed with radioactive wastes |
June 30, 1994 |
K110 |
All others |
|
K111 |
Mixed with radioactive wastes |
June 30, 1994 |
K111 |
All others |
|
K112 |
Mixed with radioactive wastes |
June 30, 1994 |
K112 |
All others |
|
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 |
|
K118 |
Mixed with radioactive wastes |
June 30, 1994 |
K118 |
All others |
|
K123 |
Mixed with radioactive wastes |
June 30, 1994 |
K123 |
All others |
|
K124 |
Mixed with radioactive wastes |
June 30, 1994 |
K124 |
All others |
|
K125 |
Mixed with radioactive wastes |
June 30, 1994 |
K125 |
All others |
|
K126 |
Mixed with radioactive wastes |
June 30, 1994 |
K126 |
All others |
|
K131 |
Mixed with radioactive wastes |
June 30, 1994 |
K131 |
All others |
|
K132 |
Mixed with radioactive wastes |
June 30, 1994 |
K132 |
All others |
|
K136 |
Mixed with radioactive wastes |
June 30, 1994 |
K136 |
All others |
|
K141 |
Mixed with radioactive wastes |
|
K141 |
All others |
|
K142 |
Mixed with radioactive wastes |
|
K142 |
All others |
|
K143 |
Mixed with radioactive wastes |
|
K143 |
All others |
|
K144 |
Mixed with radioactive wastes |
|
K144 |
All others |
|
K145 |
Mixed with radioactive wastes |
|
K145 |
All others |
|
K147 |
Mixed with radioactive wastes |
|
K147 |
All others |
|
K148 |
Mixed with radioactive wastes |
|
K148 |
All others |
|
K149 |
Mixed with radioactive wastes |
|
K149 |
All others |
|
K150 |
Mixed with radioactive wastes |
|
K150 |
All others |
|
K151 |
Mixed with radioactive wastes |
|
K151 |
All others |
|
K156 |
Mixed with radioactive wastes |
|
K156 |
All others |
July 8, 1996 |
K157 |
Mixed with radioactive wastes |
|
K157 |
All others |
July 8, 1996 |
K158 |
Mixed with radioactive wastes |
|
K158 |
All others |
July 8, 1996 |
K159 |
Mixed with radioactive wastes |
|
K159 |
All others |
July 8, 1996 |
K160 |
Mixed with radioactive wastes |
|
K160 |
All others |
July 8, 1996 |
K161 |
Mixed with radioactive wastes |
|
K161 |
All others |
July 8, 1996 |
P001 |
All |
|
P002 |
All |
|
P003 |
All |
|
P004 |
All |
|
P005 |
All |
|
P006 |
All |
|
P007 |
All |
|
P008 |
All |
|
P009 |
All |
|
P010 |
Wastewater |
|
P010 |
Nonwastewater |
May 8, 1992 |
P011 |
Wastewater |
|
P011 |
Nonwastewater |
May 8, 1992 |
P012 |
Wastewater |
|
P012 |
Nonwastewater |
May 8, 1992 |
P013 (barium) |
Nonwastewater |
|
P013 |
All others |
June 8, 1989 |
P014 |
All |
|
P015 |
All |
|
P016 |
All |
|
P017 |
All |
|
P018 |
All |
|
P020 |
All |
|
P021 |
All |
June 8, 1989 |
P022 |
All |
|
P023 |
All |
|
P024 |
All |
|
P026 |
All |
|
P027 |
All |
|
P028 |
All |
|
P029 |
All |
June 8, 1989 |
P030 |
All |
June 8, 1989 |
P031 |
All |
|
P033 |
All |
|
P034 |
All |
|
P036 |
Wastewater |
|
P036 |
Nonwastewater |
May 8, 1992 |
P037 |
All |
|
P038 |
Wastewater |
|
P038 |
Nonwastewater |
May 8, 1992 |
P039 |
All |
June 8, 1989 |
P040 |
All |
June 8, 1989 |
P041 |
All |
June 8, 1989 |
P042 |
All |
|
P043 |
All |
June 8, 1989 |
P044 |
All |
June 8, 1989 |
P045 |
All |
|
P046 |
All |
|
P047 |
All |
|
P048 |
All |
|
P049 |
All |
|
P050 |
All |
|
P051 |
All |
|
P054 |
All |
|
P056 |
All |
|
P057 |
All |
|
P058 |
All |
|
P059 |
All |
|
P060 |
All |
|
P062 |
All |
June 8, 1989 |
P063 |
All |
June 8, 1989 |
P064 |
All |
|
P065 |
Wastewater |
|
P065 |
Nonwastewater |
May 8, 1992 |
P066 |
All |
|
P067 |
All |
|
P068 |
All |
|
P069 |
All |
|
P070 |
All |
|
P071 |
All |
June 8, 1989 |
P072 |
All |
|
P073 |
All |
|
P074 |
All |
June 8, 1989 |
P075 |
All |
|
P076 |
All |
|
P077 |
All |
|
P078 |
All |
|
P081 |
All |
|
P082 |
All |
|
P084 |
All |
|
P085 |
All |
June 8, 1989 |
P087 |
All |
May 8, 1992 |
P088 |
All |
|
P089 |
All |
June 8, 1989 |
P092 |
Wastewater |
|
P092 |
Nonwastewater |
May 8, 1992 |
P093 |
All |
|
P094 |
All |
June 8, 1989 |
P095 |
All |
|
P096 |
All |
|
P097 |
All |
June 8, 1989 |
P098 |
All |
June 8, 1989 |
P099 (silver) |
Wastewater |
|
P099 |
All others |
June 8, 1989 |
P101 |
All |
|
P102 |
All |
|
P103 |
All |
|
P104 (silver) |
Wastewater |
|
P104 |
All others |
June 8, 1989 |
P105 |
All |
|
P106 |
All |
June 8, 1989 |
P108 |
All |
|
P109 |
All |
June 8, 1989 |
P110 |
All |
|
P111 |
All |
June 8, 1989 |
P112 |
All |
|
P113 |
All |
|
P114 |
All |
|
P115 |
All |
|
P116 |
All |
|
P118 |
All |
|
P119 |
All |
|
P120 |
All |
|
P121 |
All |
June 8, 1989 |
P122 |
All |
|
P123 |
All |
|
P127 |
Mixed with radioactive wastes |
|
P127 |
All others |
July 8, 1996 |
P128 |
Mixed with radioactive wastes |
|
P128 |
All others |
July 8, 1996 |
P185 |
Mixed with radioactive wastes |
|
P185 |
All others |
July 8, 1996 |
P188 |
Mixed with radioactive wastes |
|
P188 |
All others |
July 8, 1996 |
P189 |
Mixed with radioactive wastes |
|
P189 |
All others |
July 8, 1996 |
P190 |
Mixed with radioactive wastes |
|
P190 |
All others |
July 8, 1996 |
P191 |
Mixed with radioactive wastes |
|
P191 |
All others |
July 8, 1996 |
P192 |
Mixed with radioactive wastes |
|
P192 |
All others |
July 8, 1996 |
P194 |
Mixed with radioactive wastes |
|
P194 |
All others |
July 8, 1996 |
P196 |
Mixed with radioactive wastes |
|
P196 |
All others |
July 8, 1996 |
P197 |
Mixed with radioactive wastes |
|
P197 |
All others |
July 8, 1996 |
P198 |
Mixed with radioactive wastes |
|
P198 |
All others |
July 8, 1996 |
P199 |
Mixed with radioactive wastes |
|
P199 |
All others |
July 8, 1996 |
P201 |
Mixed with radioactive wastes |
|
P201 |
All others |
July 8, 1996 |
P202 |
Mixed with radioactive wastes |
|
P202 |
All others |
July 8, 1996 |
P203 |
Mixed with radioactive wastes |
|
P203 |
All others |
July 8, 1996 |
P204 |
Mixed with radioactive wastes |
|
P204 |
All others |
July 8, 1996 |
P205 |
Mixed with radioactive wastes |
|
P205 |
All others |
July 8, 1996 |
U001 |
All |
|
U002 |
All |
|
U003 |
All |
|
U004 |
All |
|
U005 |
All |
|
U006 |
All |
|
U007 |
All |
|
U008 |
All |
|
U009 |
All |
|
U010 |
All |
|
U011 |
All |
|
U012 |
All |
|
U014 |
All |
|
U015 |
All |
|
U016 |
All |
|
U017 |
All |
|
U018 |
All |
|
U019 |
All |
|
U020 |
All |
|
U021 |
All |
|
U022 |
All |
|
U023 |
All |
|
U024 |
All |
|
U025 |
All |
|
U026 |
All |
|
U027 |
All |
|
U028 |
All |
June 8, 1989 |
U029 |
All |
|
U030 |
All |
|
U031 |
All |
|
U032 |
All |
|
U033 |
All |
|
U034 |
All |
|
U035 |
All |
|
U036 |
All |
|
U037 |
All |
|
U038 |
All |
|
U039 |
All |
|
U041 |
All |
|
U042 |
All |
|
U043 |
All |
|
U044 |
All |
|
U045 |
All |
|
U046 |
All |
|
U047 |
All |
|
U048 |
All |
|
U049 |
All |
|
U050 |
All |
|
U051 |
All |
|
U052 |
All |
|
U053 |
All |
|
U055 |
All |
|
U056 |
All |
|
U057 |
All |
|
U058 |
All |
June 8, 1989 |
U059 |
All |
|
U060 |
All |
|
U061 |
All |
|
U062 |
All |
|
U063 |
All |
|
U064 |
All |
|
U066 |
All |
|
U067 |
All |
|
U068 |
All |
|
U069 |
All |
June 30, 1992 |
U070 |
All |
|
U071 |
All |
|
U072 |
All |
|
U073 |
All |
|
U074 |
All |
|
U075 |
All |
|
U076 |
All |
|
U077 |
All |
|
U078 |
All |
|
U079 |
All |
|
U080 |
All |
|
U081 |
All |
|
U082 |
All |
|
U083 |
All |
|
U084 |
All |
|
U085 |
All |
|
U086 |
All |
|
U087 |
All |
June 8, 1989 |
U088 |
All |
June 8, 1989 |
U089 |
All |
|
U090 |
All |
|
U091 |
All |
|
U092 |
All |
|
U093 |
All |
|
U094 |
All |
|
U095 |
All |
|
U096 |
All |
|
U097 |
All |
|
U098 |
All |
|
U099 |
All |
|
U101 |
All |
|
U102 |
All |
June 8, 1989 |
U103 |
All |
|
U105 |
All |
|
U106 |
All |
|
U107 |
All |
June 8, 1989 |
U108 |
All |
|
U109 |
All |
|
U110 |
All |
|
U111 |
All |
|
U112 |
All |
|
U113 |
All |
|
U114 |
All |
|
U115 |
All |
|
U116 |
All |
|
U117 |
All |
|
U118 |
All |
|
U119 |
All |
|
U120 |
All |
|
U121 |
All |
|
U122 |
All |
|
U123 |
All |
|
U124 |
All |
|
U125 |
All |
|
U126 |
All |
|
U127 |
All |
|
U128 |
All |
|
U129 |
All |
|
U130 |
All |
|
U131 |
All |
|
U132 |
All |
|
U133 |
All |
|
U134 |
All |
|
U135 |
All |
|
U136 |
Wastewater |
|
U136 |
Nonwastewater |
May 8, 1992 |
U137 |
All |
|
U138 |
All |
|
U140 |
All |
|
U141 |
All |
|
U142 |
All |
|
U143 |
All |
|
U144 |
All |
|
U145 |
All |
|
U146 |
All |
|
U147 |
All |
|
U148 |
All |
|
U149 |
All |
|
U150 |
All |
|
U151 |
Wastewater |
|
U151 |
Nonwastewater |
May 8, 1992 |
U152 |
All |
|
U153 |
All |
|
U154 |
All |
|
U155 |
All |
|
U156 |
All |
|
U157 |
All |
|
U158 |
All |
|
U159 |
All |
|
U160 |
All |
|
U161 |
All |
|
U162 |
All |
|
U163 |
All |
|
U164 |
All |
|
U165 |
All |
|
U166 |
All |
|
U167 |
All |
|
U168 |
All |
|
U169 |
All |
|
U170 |
All |
|
U171 |
All |
|
U172 |
All |
|
U173 |
All |
|
U174 |
All |
|
U176 |
All |
|
U177 |
All |
|
U178 |
All |
|
U179 |
All |
|
U180 |
All |
|
U181 |
All |
|
U182 |
All |
|
U183 |
All |
|
U184 |
All |
|
U185 |
All |
|
U186 |
All |
|
U187 |
All |
|
U188 |
All |
|
U189 |
All |
|
U190 |
All |
June 8, 1989 |
U191 |
All |
|
U192 |
All |
|
U193 |
All |
|
U194 |
All |
June 8, 1989 |
U196 |
All |
|
U197 |
All |
|
U200 |
All |
|
U201 |
All |
|
U202 |
All |
|
U203 |
All |
|
U204 |
All |
|
U205 |
All |
|
U206 |
All |
|
U207 |
All |
|
U208 |
All |
|
U209 |
All |
|
U210 |
All |
|
U211 |
All |
|
U213 |
All |
|
U214 |
All |
|
U215 |
All |
|
U216 |
All |
|
U217 |
All |
|
U218 |
All |
|
U219 |
All |
|
U220 |
All |
|
U221 |
All |
June 8, 1989 |
U222 |
All |
|
U223 |
All |
June 8, 1989 |
U225 |
All |
|
U226 |
All |
|
U227 |
All |
|
U228 |
All |
|
U234 |
All |
|
U235 |
All |
June 8, 1989 |
U236 |
All |
|
U237 |
All |
|
U238 |
All |
|
U239 |
All |
|
U240 |
All |
|
U243 |
All |
|
U244 |
All |
|
U246 |
All |
|
U247 |
All |
|
U248 |
All |
|
U249 |
All |
|
U271 |
Mixed with radioactive wastes |
|
U271 |
All others |
July 8, 1996 |
U277 |
Mixed with radioactive wastes |
|
U277 |
All others |
July 8, 1996 |
U278 |
Mixed with radioactive wastes |
|
U278 |
All others |
July 8, 1996 |
U279 |
Mixed with radioactive wastes |
|
U279 |
All others |
July 8, 1996 |
U280 |
Mixed with radioactive wastes |
|
U280 |
All others |
July 8, 1996 |
U328 |
Mixed with radioactive wastes |
June 30, 1994 |
U328 |
All others |
|
U353 |
Mixed with radioactive wastes |
June 30, 1994 |
U353 |
All others |
|
U359 |
Mixed with radioactive wastes |
June 30, 1994 |
U359 |
All others |
|
U364 |
Mixed with radioactive wastes |
|
U364 |
All others |
July 8, 1996 |
U365 |
Mixed with radioactive wastes |
|
U365 |
All others |
July 8, 1996 |
U366 |
Mixed with radioactive wastes |
|
U366 |
All others |
July 8, 1996 |
U367 |
Mixed with radioactive wastes |
|
U367 |
All others |
July 8, 1996 |
U372 |
Mixed with radioactive wastes |
|
U372 |
All others |
July 8, 1996 |
U373 |
Mixed with radioactive wastes |
|
U373 |
All others |
July 8, 1996 |
U375 |
Mixed with radioactive wastes |
|
U375 |
All others |
July 8, 1996 |
U376 |
Mixed with radioactive wastes |
|
U376 |
All others |
July 8, 1996 |
U377 |
Mixed with radioactive wastes |
|
U377 |
All others |
July 8, 1996 |
U378 |
Mixed with radioactive wastes |
|
U378 |
All others |
July 8, 1996 |
U379 |
Mixed with radioactive wastes |
|
U379 |
All others |
July 8, 1996 |
U381 |
Mixed with radioactive wastes |
|
U381 |
All others |
July 8, 1996 |
U382 |
Mixed with radioactive wastes |
|
U382 |
All others |
July 8, 1996 |
U383 |
Mixed with radioactive wastes |
|
U383 |
All others |
July 8, 1996 |
U384 |
Mixed with radioactive wastes |
|
U384 |
All others |
July 8, 1996 |
U385 |
Mixed with radioactive wastes |
|
U385 |
All others |
July 8, 1996 |
U386 |
Mixed with radioactive wastes |
|
U386 |
All others |
July 8, 1996 |
U387 |
Mixed with radioactive wastes |
|
U387 |
All others |
July 8, 1996 |
U389 |
Mixed with radioactive wastes |
|
U389 |
All others |
July 8, 1996 |
U390 |
Mixed with radioactive wastes |
|
U390 |
All others |
July 8, 1996 |
U391 |
Mixed with radioactive wastes |
|
U391 |
All others |
July 8, 1996 |
U392 |
Mixed with radioactive wastes |
|
U392 |
All others |
July 8, 1996 |
U393 |
Mixed with radioactive wastes |
|
U393 |
All others |
July 8, 1996 |
U394 |
Mixed with radioactive wastes |
|
U394 |
All others |
July 8, 1996 |
U395 |
Mixed with radioactive wastes |
|
U395 |
All others |
July 8, 1996 |
U396 |
Mixed with radioactive wastes |
|
U396 |
All others |
July 8, 1996 |
U400 |
Mixed with radioactive wastes |
|
U400 |
All others |
July 8, 1996 |
U401 |
Mixed with radioactive wastes |
|
U401 |
All others |
July 8, 1996 |
U402 |
Mixed with radioactive wastes |
|
U402 |
All others |
July 8, 1996 |
U403 |
Mixed with radioactive wastes |
|
U403 |
All others |
July 8, 1996 |
U404 |
Mixed with radioactive wastes |
|
U404 |
All others |
July 8, 1996 |
U407 |
Mixed with radioactive wastes |
|
U407 |
All others |
July 8, 1996 |
U409 |
Mixed with radioactive wastes |
|
U409 |
All others |
July 8, 1996 |
U410 |
Mixed with radioactive wastes |
|
U410 |
All others |
July 8, 1996 |
U411 |
Mixed with radioactive wastes |
|
U411 |
All others |
July 8, 1996 |
a | This table does not include mixed radioactive wastes (from the First, Second, and Third Third rules) |
b | The standard was revised in the Third Third Final Rule (adopted by USEPA at 55 Fed. Reg. 22520 (June 1, 1990) and by the Board in docket R90-11 by orders dated April 11, May 23, and August 8 and 22, 1991). |
c | USEPA amended the standard in the Third Third Emergency Rule (at 58 Fed. Reg. 29860 (May 24, 1993), which the Board adopted in docket R93-16 on March 17, 1994); the original effective date was August 8, 1990. |
d | The standard was revised in the Phase II Final Rule ( |
e | The standards for selected reactive wastes was revised in the Phase III Final Rule ( |
TABLE 2
SUMMARY OF EFFECTIVE DATES OF LAND DISPOSAL RESTRICTIONS FOR CONTAMINATED SOIL AND DEBRIS (CSD)
Restricted hazardous waste in CSD |
Effective date |
1. Solvent- (F001-F005) and dioxin- (F020-F023 and F026-F028) containing soil and debris from CERCLA response or RCRA corrective actions. |
|
2. Soil and debris not from CERCLA response or RCRA corrective actions contaminated with less than one percent total solvents (F001-F005) or dioxins (F020-F023 and F026-F028). |
|
3. All soil and debris contaminated with First Third wastes for which treatment standards are based on incineration. |
|
4. All soil and debris contaminated with Second Third wastes for which treatment standards are based on incineration. |
June 8, 1991 |
5. All soil and debris contaminated with Third Third wastes or, First or Second Third “soft hammer” wastes |
May 8, 1992 |
6. Soil and debris contaminated with D012-D043, K141-K145, and K147-151 wastes. |
|
7. Debris (only) contaminated with F037, F038, K107-K112, K117, K118, K123-K126, K131, K132, K136, U328, U353, U359. |
|
8. Soil and debris contaminated with K156- K161, P127, P128, P188-P192, P194, P196- P199, P201-P205, U271, U277-U280, U364-U367, U372, U373, U375-U379, U381-U387, U389-U396, U400-U404, U407, and U409-U411 wastes. |
July 8, 1996 |
9. Soil and debris contaminated with K088 wastes. |
|
10. Soil and debris contaminated with radioactive wastes mixed with K088, K156-K161, P127, P128, P188-P192, P194, P196-P199, P201-P205, U271, U277-U280, U364-U367, U372, U373, U375-U379, U381-U387, U389-U396, U400-U404, U407, and U409-U411 wastes. |
April 8, 1998 |
11. Soil and debris contaminated with F032, F034, and F035. |
May 12, 1997 |
12. Soil and debris contaminated with newly identified D004-D011 toxicity characteristic wastes and mineral processing wastes. |
|
13. Soil and debris contaminated with mixed radioactive newly identified D011 characteristic wastes and mineral processing wastes. |
May 26, 2000 |
BOARD NOTE: This table is provided for the convenience of the reader.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Appendix H | |
National Capacity LDR Variances for UIC Wastes | |
See Notea
Waste code |
Waste category |
Effective date |
D001 (except High TOC Ignitable Liquids Subcategory)c |
All |
|
D001 (High TOC Ignitable Characteristic Liquids Subcategory) |
Nonwastewater |
|
D002b |
All |
May 8, 1992 |
D002c |
All |
|
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 |
|
D013 |
All |
|
D014 |
All |
|
D015 |
All |
|
D016 |
All |
|
D017 |
All |
|
D018 |
All, including mixed with radioactive wastes |
|
D019 |
All, including mixed with radioactive wastes |
|
D020 |
All, including mixed with radioactive wastes |
|
D021 |
All, including mixed with radioactive wastes |
|
D022 |
All, including mixed with radioactive wastes |
|
D023 |
All, including mixed with radioactive wastes |
|
D024 |
All, including mixed with radioactive wastes |
|
D025 |
All, including mixed with radioactive wastes |
|
D026 |
All, including mixed with radioactive wastes |
|
D027 |
All, including mixed with radioactive wastes |
|
D028 |
All, including mixed with radioactive wastes |
|
D029 |
All, including mixed with radioactive wastes |
|
D030 |
All, including mixed with radioactive wastes |
|
D031 |
All, including mixed with radioactive wastes |
|
D032 |
All, including mixed with radioactive wastes |
|
D033 |
All, including mixed with radioactive wastes |
|
D034 |
All, including mixed with radioactive wastes |
|
D035 |
All, including mixed with radioactive wastes |
|
D036 |
All, including mixed with radioactive wastes |
|
D037 |
All, including mixed with radioactive wastes |
|
D038 |
All, including mixed with radioactive wastes |
|
D039 |
All, including mixed with radioactive wastes |
|
D040 |
All, including mixed with radioactive wastes |
|
D041 |
All, including mixed with radioactive wastes |
|
D042 |
All, including mixed with radioactive wastes |
|
D043 |
All, including mixed with radioactive wastes |
|
F001-F005 |
All spent F001-F005 solvent containing less than 1 percent total F001-F005 solvent constituents |
|
F007 |
All |
June 8, 1991 |
F032 |
All, including mixed with radioactive wastes |
May 12, 1999 |
F034 |
All, including mixed with radioactive wastes |
May 12,1999 |
F035 |
All, including mixed with radioactive wastes |
May 12, 1999 |
F037 |
All |
|
F038 |
All |
|
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 |
|
K050 |
All |
|
K051 |
All |
|
K052 |
All |
|
K062 |
All |
|
K071 |
All |
|
K088 |
All |
|
K104 |
All |
|
K107 |
All |
|
K108 |
All |
|
K109 |
All |
|
K110 |
All |
|
K111 |
All |
|
K112 |
All |
|
K117 |
All |
June 30, 1995 |
K118 |
All |
June 30, 1995 |
K123 |
All |
|
K124 |
All |
|
K125 |
All |
|
K126 |
All |
|
K131 |
All |
June 30, 1995 |
K132 |
All |
June 30, 1995 |
K136 |
All |
|
K141 |
All |
|
K142 |
All |
|
K143 |
All |
|
K144 |
All |
|
K145 |
All |
|
K147 |
All |
|
K148 |
All |
|
K149 |
All |
|
K150 |
All |
|
K151 |
All |
|
K156 |
All |
July 8, 1996 |
K157 |
All |
July 8, 1996 |
K158 |
All |
July 8, 1996 |
K159 |
All |
July 8, 1996 |
K160 |
All |
July 8, 1996 |
K161 |
All |
July 8, 1996 |
NA |
Newly identified mineral processing wastes from titanium dioxide production and mixed radioactive/newly identified D004-D011 characteristic wastes and mineral processing wastes |
May 26, 2000 |
P127 |
All |
July 8, 1996 |
P128 |
All |
July 8, 1996 |
P185 |
All |
July 8, 1996 |
P188 |
All |
July 8, 1996 |
P189 |
All |
July 8, 1996 |
P190 |
All |
July 8, 1996 |
P191 |
All |
July 8, 1996 |
P192 |
All |
July 8, 1996 |
P194 |
All |
July 8, 1996 |
P196 |
All |
July 8, 1996 |
P197 |
All |
July 8, 1996 |
P198 |
All |
July 8, 1996 |
P199 |
All |
July 8, 1996 |
P201 |
All |
July 8, 1996 |
P202 |
All |
July 8, 1996 |
P203 |
All |
July 8, 1996 |
P204 |
All |
July 8, 1996 |
P205 |
All |
July 8, 1996 |
U271 |
All |
July 8, 1996 |
U277 |
All |
July 8, 1996 |
U278 |
All |
July 8, 1996 |
U279 |
All |
July 8, 1996 |
U280 |
All |
July 8, 1996 |
U328 |
All |
|
U353 |
All |
|
U359 |
All |
|
U364 |
All |
July 8, 1996 |
U365 |
All |
July 8, 1996 |
U366 |
All |
July 8, 1996 |
U367 |
All |
July 8, 1996 |
U372 |
All |
July 8, 1996 |
U373 |
All |
July 8, 1996 |
U375 |
All |
July 8, 1996 |
U376 |
All |
July 8, 1996 |
U377 |
All |
July 8, 1996 |
U378 |
All |
July 8, 1996 |
U379 |
All |
July 8, 1996 |
U381 |
All |
July 8, 1996 |
U382 |
All |
July 8, 1996 |
U383 |
All |
July 8, 1996 |
U384 |
All |
July 8, 1996 |
U385 |
All |
July 8, 1996 |
U386 |
All |
July 8, 1996 |
U387 |
All |
July 8, 1996 |
U389 |
All |
July 8, 1996 |
U390 |
All |
July 8, 1996 |
U391 |
All |
July 8, 1996 |
U392 |
All |
July 8, 1996 |
U395 |
All |
July 8, 1996 |
U396 |
All |
July 8, 1996 |
U400 |
All |
July 8, 1996 |
U401 |
All |
July 8, 1996 |
U402 |
All |
July 8, 1996 |
U403 |
All |
July 8, 1996 |
U404 |
All |
July 8, 1996 |
U407 |
All |
July 8, 1996 |
U409 |
All |
July 8, 1996 |
U410 |
All |
July 8, 1996 |
U411 |
All |
July 8, 1996 |
a | Wastes that are deep well disposed on-site receive a six-month variance, with restrictions, effective in November 1990. |
b | Deep well injected D002 liquids with a pH less than |
c | Managed in systems defined in 35 Ill. Adm. Code 730.105(e) as Class V injection wells that do not engage in CWA-equivalent treatment before injection. |
BOARD NOTE: This table is provided for the convenience of the reader.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Appendix I | |
EP Toxicity Test Method and Structural Integrity Test | |
Note: The EP (Method 1310) is published in “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,”, U.S. EPA USEPA Publication SW-846, as incorporated by reference in 35 Ill. Adm. Code 720.111.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Appendix K | |
BOARD NOTE: A combustion unit is defined as any thermal technology subject to Subpart O of 35 Ill. Adm. Code 724.Subpart O, Subpart O of 35 Ill. Adm. Code 725.Subpart O, or Subpart H of 35 Ill. Adm. Code 726.Subpart H.
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 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 |
F012 | Quenching waste water treatment sludges from metal |
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 (I) cyanide Cu(CN). |
P074 | Nickel (II) cyanide Ni(CN)2. |
P087 | Osmium (VIII) tetroxide OsO4. |
P099 | Potassium silver cyanide KAg(CN)2. |
P104 | Silver cyanide AgCN. |
P113 | Thallic (III) oxide Tl2O3. |
P114 | Thallium (I) selenite Tl2SeO3. |
P115 | Thallium (I) sulfate Tl2SO4. |
P119 | Ammonium (V) vanadate NH3VO3. |
P120 | Vanadium (V) oxide V2O5. |
P121 | Zinc cyanide ZnCN. |
U032 | Calcium chromate CaCrO4. |
U145 | Lead phosphate. |
U151 | Mercury. |
U204 | Selenous acid H2SeO3. |
U205 | Selenium (IV) disulfide SeS2. |
U216 | Thallium (I) chloride TlCl. |
U217 | Thallium (I) nitrate TlNO3. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Table A | Constituent Concentrations in Waste Extract (CCWE) |
For the requirements previously found in this Section and Section 728.141, refer to Section 728.140 and 728.Table T to this Part, “Treatment Standards for Hazardous Wastes.”.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Table B | Constituent Concentrations in Wastes (CCW) |
For the requirements previously found in this Section and for treatment standards in Section 728.143, “Constituent Concentrations in Wastes (CCW),”, refer to Section 728.140 and 728.Table T to this Part, “Treatment Standards for Hazardous Wastes.”.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Table C | Technology Codes and Description of Technology-Based Standards |
Technology
Description of | |
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 or piping; physical penetration of the container; 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 (TOC) 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, or organic constituents, operated so that a surrogate compound or indicator parameter has not undergone breakthrough (e.g., total organic carbon (TOC) 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 or 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; or |
9) | other oxidizing reagents of equivalent efficiency, performed in units operated so that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., total organic carbon (TOC) can often be used as an indicator parameter for the oxidation of many organic constituents that cannot be directly analyzed in wastewater residues). Chemical oxidation specifically includes what is commonly referred to as alkaline chlorination. |
CHRED | Chemical reduction utilizing the following reducing reagents (or waste reagents) or combinations of reagents: |
1) | sulfur dioxide; |
2) | sodium, potassium, or alkali salts of sulfites, bisulfites, metabisulfites, and polyethylene glycols (e.g., NaPEG and KPEG); |
3) | sodium hydrosulfide; |
4) | ferrous salts; 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 (TOX) 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 Subpart O of 35 Ill. Adm. Code 724 |
DEACT | Deactivation to remove the hazardous characteristics of a waste due to its ignitability, corrosivity, or reactivity. |
FSUBS | Fuel substitution in units operated in accordance with applicable technical operating requirements. |
HLVIT | Vitrification of |
IMERC | Incineration of wastes containing organics and mercury in units operated in accordance with the technical operating requirements of Subpart O of 35 Ill. Adm. Code 724 |
INCIN | Incineration in units operated in accordance with the technical operating requirements of Subpart O of 35 Ill. Adm. Code 724 |
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 or 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 35 Ill. Adm. Code 720.110. |
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 |
NLDBR | No land disposal based on recycling. |
POLYM | Formation of complex high-molecular weight solids through polymerization of monomers in high-TOC D001 nonwastewaters that are chemical components in the manufacture of plastics. |
PRECP | Chemical precipitation of metals and other inorganics as insoluble precipitates of oxides, hydroxides, carbonates, sulfides, sulfates, chlorides, fluorides, or phosphates. The following reagents (or waste reagents) are typically used alone or in combination: |
1) | lime (i.e., containing oxides or hydroxides of calcium or magnesium); |
2) | caustic (i.e., sodium 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 or processes that enhance sludge dewatering characteristics are not precluded from use. |
RBERY | Thermal recovery of beryllium. |
RCGAS | Recovery or reuse of compressed gases including techniques such as reprocessing of the gases for reuse or resale; filtering or 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; 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 (40 CFR 61, Subpart E); |
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 (including 35 Ill. Adm. Code 201 through 203); or |
c) | A state permit that establishes emission limitations (within meaning of Section 302 of the Clean Air Act) for mercury, including a permit issued pursuant to 35 Ill. Adm. Code 201. 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 or removal technologies: |
1) | ion exchange; |
2) | resin or solid (i.e., zeolites) adsorption; |
3) | reverse osmosis; |
4) | chelation or solvent extraction; |
5) | freeze crystallization; |
6) | ultrafiltration; 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 or crystallization (including freeze crystallization); or |
8) | chemical phase separation techniques (i.e., addition of acids, bases, demulsifiers, or similar chemicals). |
Note: This does not preclude the use of other physical phase separation techniques such as decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies.
RTHRM | Thermal recovery of metals or inorganics from nonwastewaters in units defined as cement kilns, blast furnaces, smelting, melting and refining furnaces, combustion devices used to recover sulfur values from spent sulfuric acid and “other devices” determined by the Agency pursuant to 35 Ill. Adm. Code 720.110, the definition of “industrial furnace.” |
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 or 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 or cure time 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 or 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 (TOC) 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 or 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 |
Note 2: | When more than one technology (or treatment train) are specified as alternative treatment standards, the five letter technology codes (or the treatment trains) are separated by a semicolon (;) with the last technology preceded by the word “OR.” |
BOARD NOTE: Derived from 40 CFR 268.42, Table 1 (1997) (2002).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Table D | Technology-Based Standards by RCRA Waste Code |
BOARD NOTE: For the requirements previously found in this Section, refer to Sections Section 728.140 and 728.Table T to this Part.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Table E | Standards for Radioactive Mixed Waste |
BOARD NOTE: For the requirements previously found in this Section, refer to Sections Section 728.140 and 728.Table T to this Part.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Table F | Alternative Treatment Standards For Hazardous Debris |
a) | Hazardous debris must be treated by either the standards indicated in this Table F or by 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. |
b) | Definitions. For the purposes of this Table F, the following terms are defined as follows: |
“Clean debris surface” means the surface, when viewed without magnification, shall must 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 must be limited to no more than 5% five percent of each square inch of surface area.
“Contaminant restriction” means that the technology is not BDAT for that contaminant. If debris containing a restricted contaminant is treated by the technology, the contaminant must be subsequently treated by a technology for which it is not restricted in order to be land disposed (and excluded from Subtitle C regulation).
“Dioxin-listed wastes” means wastes having any of U.S. EPA USEPA Hhazardous hazardous waste numbers FO20, FO21, FO22, FO23, FO26, or FO27.
c) | Notes. In |
1 Acids, solvents, and chemical reagents may react with some debris and contaminants to form hazardous compounds. For example, acid washing of cyanide-contaminated debris could result in the formation of hydrogen cyanide. Some acids may also react violently with some debris and contaminants, depending on the concentration of the acid and the type of debris and contaminants. Debris treaters should refer to the safety precautions specified in Material Safety Data Sheets for various acids to avoid applying an incompatible acid to a particular debris/contaminant combination. For example, concentrated sulfuric acid may react violently with certain organic compounds, such as acrylonitrile.
2 If reducing the particle size of debris to meet the treatment standards results in material that no longer meets the 60 mm minimum particle size limit for debris, such material is subject to the waste-specific treatment standards for the waste contaminating the material, unless the debris has been cleaned and separated from contaminated soil and waste prior to size reduction. At a minimum, simple physical or mechanical means must be used to provide such cleaning and separation of nondebris materials to ensure that the debris surface is free of caked soil, waste, or other nondebris material.
3 Thermal desorption is distinguished from thermal destruction in that the primary purpose of thermal desorption is to volatilize contaminants and to remove them from the treatment chamber for subsequent destruction or other treatment.
4 The demonstration of “equivalent technology” under Section 728.142(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.
5 Any soil, waste, and other nondebris material that remains on the debris surface (or remains mixed with the debris) after treatment is considered a treatment residual that must B 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 subsection (b) above of this Section 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.
Technology description |
Performance or design and operating standard |
Contaminant restrictions |
A. Extraction Technologies: |
||
1. Physical Extraction |
||
a. Abrasive Blasting: Removal of contaminated debris surface layers using water |
Glass, Metal, Plastic, Rubber: Treatment to a clean debris surface. Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Removal of at least 0.6 cm of the surface layer; treatment to a clean debris surface. |
All Debris: None. |
b. Scarification, Grinding, and Planing: Process utilizing striking piston heads, saws, or rotating grinding wheels such that contaminated debris surface layers are removed. |
Same as above |
Same as above |
c. Spalling: Drilling or chipping holes at appropriate locations and depth in the contaminated debris surface and applying a tool |
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.1 |
Same as above |
Same as above |
e. High Pressure Steam and Water Sprays: Application of water or steam sprays of sufficient temperature, pressure, residence time, agitation, surfactants, and detergents to remove hazardous contaminants from debris surfaces or to remove contaminated debris surface layers |
Same as above |
Same as above. |
2. Chemical Extraction |
||
a. Water Washing and Spraying: Application of water sprays or water baths of sufficient temperature, pressure, residence time, agitation, surfactants, acids, bases, and detergents to remove hazardous contaminants from debris surfaces and surface pores or to remove contaminated debris surface layers. |
All Debris: Treatment to a clean debris surface; Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (½ inch) in one dimension (i.e., thickness limit,2 except that this thickness limit may be waived under an “Equivalent Technology” approval under |
Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Contaminant must be soluble to at least |
b. Liquid Phase Solvent Extraction: Removal of hazardous contaminants from debris surfaces and surface pores by applying a nonaqueous liquid or liquid solution |
Same as above |
Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Same as above, except that contaminant must be soluble to at least |
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.1 |
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, |
For refining furnaces, treated debris must be separated from treatment residuals using simple physical or mechanical means,5 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:2 Obtain an “Equivalent Technology” approval under |
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.3 |
All Debris: Obtain an “Equivalent Technology” approval under Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 10 cm (4 inches) in one dimension (i.e., thickness limit),2 except that this thickness limit may be waived under the “Equivalent Technology” approval |
All Debris: Metals other than mercury. |
B. Destruction Technologies: |
||
1. Biological Destruction (Biodegradation): Removal of hazardous contaminants from debris surfaces and surface pores in an aqueous solution and biodegration 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 Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (½ inch) in one dimension (i.e., thickness limit),2 except that this thickness limit may be waived under the “Equivalent Technology” approval |
All Debris: Metal contaminants. |
2. Chemical Destruction |
||
a. Chemical Oxidation: Chemical or |
All Debris: Obtain an “Equivalent Technology” approval under 35 Ill. Adm. Code.142(b);4 treated debris must be separated from treatment residuals using simple physical or mechanical means,5 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 (½ inch) in one dimension (i.e., thickness limit),2 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; |
Same as above |
Same as above. |
3. Thermal Destruction: Treatment in an incinerator operating in accordance with Subpart O of 35 Ill. Adm. Code 724 |
Treated debris must be separated from treatment residuals using simple physical or mechanical means,5 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.3 Obtain an “Equivalent Technology” approval under |
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 |
Leachability of the hazardous contaminants must be reduced. |
None. |
3. Sealing: Application of an appropriate material |
Sealing must avoid exposure of the debris surface to potential leaching media and sealant must be |
None. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Table G | Alternative Treatment Standards Based on HTMR |
For the treatment standards previously found in this Section and Section 728.146, refer to Sections Section 728.140 and 728.Table T to this Part, “Treatment Standards for Hazardous Wastes.”.
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Table H | Wastes Excluded from CCW Treatment Standards |
The following facilities are excluded from the treatment standard under Section 728.143(a) and Table B to this Part, and are subject to the following constituent concentrations. These facilities have received a treatability exception by regulatory action from USEPA pursuant to 40 CFR 268.44 (1991) (2002), and have demonstrated that the Board needs to adopt the treatability exception as part of the Illinois RCRA program. The Board may also grant an “adjusted treatment standard” pursuant to Section 728.144.
Facility name and address |
Waste Code |
See Also |
Regulated hazardous constituent |
Wastewaters Concentration (mg/L) |
Notes |
Nonwastewaters Concentration (mg/L) |
Notes |
Craftsman Plating and Tinning Corp., Chicago, IL |
F006 |
Section 728.140 |
Cyanides (Total) |
1.2 |
B |
1800 |
D |
Cyanides (amenable) |
0.86 |
B and C |
30 |
D |
|||
Cadmium |
1.6 |
NA |
|||||
Chromium |
0.32 |
NA |
|||||
Lead |
0.40 |
NA |
|||||
Nickel |
0.44 |
NA |
Northwestern Plating Works, Inc., Chicago, IL |
F006 |
Section 728.140 |
Cyanides (Total) |
1.2 |
B |
970 |
D |
Cyanides (amenable) |
0.86 |
B and C |
30 |
D |
|||
Cadmium |
1.6 |
NA |
|||||
Chromium |
0.32 |
NA |
|||||
Lead |
0.40 |
NA |
|||||
Nickel |
0.44 |
NA |
Notes:
A | An owner or operator may certify compliance with these treatment standards according to the provisions of Section 728.107. |
B | Cyanide wastewater standards for F006 are based on analysis of composite samples. |
C | These owners and operators |
D | Cyanide nonwastewaters are analyzed using SW-846 Method 9010 or 9012, sample size 10 g, distillation time one hour and fifteen minutes. SW-846 is incorporated by reference in 35 Ill. Adm. Code 720.111. |
NA | Not applicable. |
BOARD NOTE: Derived from table to 40 CFR 268.44(o) (1997) (2002).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Table I | Generator Paperwork Requirements |
Subsection of Section 728.107 under Which the Paperwork is Required: |
Required information |
(a)(2) |
(a)(3) |
(a)(4) |
(a)(9) |
1. USEPA hazardous waste numbers and manifest number of first shipment |
ü |
ü |
ü |
ü |
2. Statement: this waste is not prohibited from land disposal |
ü |
|||
3. The waste is subject to the LDRs. The constituents of concern for USEPA hazardous waste numbers F001 through F005 and F039 waste, and underlying hazardous constituents in characteristic waste, 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 |
ü |
ü |
||
4. The notice must include the applicable wastewater/ nonwastewater category (see Section 728.102(d) and (f)) and subdivisions made within a waste code based on waste-specific criteria (such as D003 reactive cyanide) |
ü |
ü |
||
5. Waste analysis data (when available) |
ü |
ü |
ü |
|
6. Date the waste is subject to the prohibition |
ü |
|||
7. For hazardous debris, when treating with the alternative treatment technologies provided by Section 728.145: the contaminants subject to treatment, as described in Section 728.145(b); and an indication that these contaminants are being treated to comply with Section 728.145 |
ü |
ü |
||
8. For contaminated soil subject to LDRs as provided in Section 728.149(a), the constituents subject to treatment as described in Section 728.149(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 Section 728.149(c) or the universal treatment standards |
ü |
ü |
||
9. A certification is needed (see applicable subsection for exact wording) |
ü |
ü |
BOARD NOTE: Derived from Table 1 to 40 CFR 268.7(a)(4) (1997) (2002), as amended at 63 Fed. Reg. 28639 (May 26, 1998).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Table T | Treatment Standards for Hazardous Wastes |
Note: The treatment standards that heretofore appeared in tables in Sections 728.141, 728.142, and 728.143 have been consolidated into this table.
Waste Code
Waste Description and Treatment or Regulatory Subcategory1
Regulated Hazardous Constituent |
Wastewaters |
Nonwastewaters |
Common Name |
CAS2 Number |
Concentration in mg/l3; or Technology Code4 |
Concentration in mg/kg5 unless noted as “mg/l TCLP”; or Technology Code4 |
D0019
Ignitable Characteristic Wastes, except for the 35 Ill. Adm. Code 721.121(a)(1) High TOC Subcategory.
NA |
NA |
DEACT and meet Section 728.148 standards8; or RORGS; or CMBST |
DEACT and meet Section 728.148 standards8; or RORGS; or CMBST |
D0019
High TOC Ignitable Characteristic Liquids Subcategory based on 35 Ill. Adm. Code 721.121(a)(1) - Greater than or equal to 10 percent total organic carbon.
(Note: This subcategory consists of nonwastewaters only.)
NA |
NA |
NA |
RORGS; CMBST; or POLYM |
D0029
Corrosive Characteristic Wastes.
NA |
NA |
DEACT and meet Section 728.148 standards8 |
DEACT and meet Section 728.148 standards8 |
D002, D004, D005, D006, D007, D008, D009, D010, D011
Radioactive high level wastes generated during the reprocessing of fuel rods.
(Note: This subcategory consists of nonwastewaters only.)
Corrosivity (pH) |
NA |
NA |
HLVIT |
Arsenic |
7440-38-2 |
NA |
HLVIT |
Barium |
7440-39-3 |
NA |
HLVIT |
Cadmium |
7440-43-9 |
NA |
HLVIT |
Chromium (Total) |
7440-47-3 |
NA |
HLVIT |
Lead |
7439-92-1 |
NA |
HLVIT |
Mercury |
7439-97-6 |
NA |
HLVIT |
Selenium |
7782-49-2 |
NA |
HLVIT |
Silver |
7440-22-4 |
NA |
HLVIT |
D0039
Reactive Sulfides Subcategory based on 35 Ill. Adm. Code 721.123(a)(5).
NA |
NA |
DEACT |
DEACT |
D0039
Explosive subcategory based on 35 Ill. Adm. Code 721.123(a)(6), (a)(7), and (a)(8).
NA |
NA |
DEACT and meet Section 728.148 standards8 |
DEACT and meet Section 728.148 standards8 |
D0039
Unexploded ordnance and other explosive devices that have been the subject of an emergency response.
NA |
NA |
DEACT |
DEACT |
D0039
Other Reactives Subcategory based on 35 Ill. Adm. Code 721.123(a)(1).
NA |
NA |
DEACT and meet Section 728.148 standards8 |
DEACT and meet Section 728.148 standards8 |
D0039
Water Reactive Subcategory based on 35 Ill. Adm. Code 721.123(a)(2), (a)(3), and (a)(4).
(Note: This subcategory consists of nonwastewaters only.)
NA |
NA |
NA |
DEACT and meet Section 728.148 standards8 |
D0039
Reactive Cyanides Subcategory based on 35 Ill. Adm. Code 721.123(a)(5).
Cyanides (Total)7 |
57-12-5 |
-- |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
D0049
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for arsenic based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Arsenic |
7440-38-2 |
1.4 and meet Section 728.148 standards8 |
5.0 mg/l TCLP and meet Section 728.148 standards8 |
D0059
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for barium based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Barium |
7440-39-3 |
1.2 and meet Section 728.148 standards8 |
21 mg/l TCLP and meet Section 728.148 standards8 |
D0069
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for cadmium based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Cadmium |
7440-43-9 |
0.69 and meet Section 728.148 standards8 |
0.11 mg/l TCLP and meet Section 728.148 standards8 |
D0069
Cadmium-Containing Batteries Subcategory.
(Note: This subcategory consists of nonwastewaters only.)
Cadmium |
7440-43-9 |
NA |
RTHRM |
D0069
Radioactively contaminated cadmium-containing batteries.
(Note: This subcategory consists of nonwastewaters only.)
Cadmium |
7440-43-9 |
NA |
Macroencapsulation in accordance with Section 728.145 |
D0079
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for chromium based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Chromium (Total) |
7440-47-3 |
2.77 and meet Section 728.148 standards8 |
0.60 mg/l TCLP and meet Section 728.148 standards8 |
D0089
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for lead based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Lead |
7439-92-1 |
0.69 and meet Section 728.148 standards8 |
0.75 mg/l TCLP and meet Section 728.148 standards8 |
D0089
Lead Acid Batteries Subcategory
(Note: This standard only applies to lead acid batteries that are identified as RCRA hazardous wastes and that are not excluded elsewhere from regulation under the land disposal restrictions of this Part or exempted under other regulations (see 35 Ill. Adm. Code 726.180). This subcategory consists of nonwastewaters only.)
Lead |
7439-92-1 |
NA |
RLEAD |
D0089
Radioactive Lead Solids Subcategory
(Note: These lead solids include, but are not limited to, all forms of lead shielding and other elemental forms of lead. These lead solids do not include treatment residuals such as hydroxide sludges, other wastewater treatment residuals, or incinerator ashes that can undergo conventional pozzolanic stabilization, nor do they include organo-lead materials that can be incinerated and stabilized as ash. This subcategory consists of nonwastewaters only.)
Lead |
7439-92-1 |
NA |
MACRO |
D0099
Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311; and contain greater than or equal to 260 mg/kg total mercury that also contain organics and are not incinerator residues. (High Mercury-Organic Subcategory)
Mercury |
7439-97-6 |
NA |
IMERC; or RMERC |
D0099
Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311; and contain greater than or equal to 260 mg/kg total mercury that are inorganic, including incinerator residues and residues from RMERC. (High Mercury-Inorganic Subcategory)
Mercury |
7439-97-6 |
NA |
RMERC |
D0099
Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311; and contain less than 260 mg/kg total mercury. (Low Mercury Subcategory)
Mercury |
7439-97-6 |
NA |
0.20 mg/l TCLP and meet Section 728.148 standards8 |
D0099
All other nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311; and contain less than 260 mg/kg total mercury and that are not residues from RMERC. (Low Mercury Subcategory)
Mercury |
7439-97-6 |
NA |
0.025 mg/l TCLP and meet Section 728.148 standards8 |
D0099
All D009 wastewaters.
Mercury |
7439-97-6 |
0.15 and meet Section 728.148 standards8 |
NA |
D0099
Elemental mercury contaminated with radioactive materials.
(Note: This subcategory consists of nonwastewaters only.)
Mercury |
7439-97-6 |
NA |
AMLGM |
D0099
Hydraulic oil contaminated with Mercury Radioactive Materials Subcategory.
(Note: This subcategory consists of nonwastewaters only.)
Mercury |
7439-97-6 |
NA |
IMERC |
D0099
Radioactively contaminated mercury-containing batteries.
(Note: This subcategory consists of nonwastewaters only.)
Mercury |
7439-97-6 |
NA |
Macroencapsulation in accordance with Section 728.145 |
D0109
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for selenium based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Selenium |
7782-49-2 |
0.82 |
5.7 mg/l TCLP and meet Section 728.148 standards8 |
D0119
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for silver based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Silver |
7440-22-4 |
0.43 |
0.14 mg/l TCLP and meet Section 728.148 standards8 |
D0119
Radioactively contaminated silver-containing batteries.
(Note: This subcategory consists of nonwastewaters only.)
Silver |
7440-22-4 |
NA |
Macroencapsulation in accordance with Section 728.145 |
D0129
Wastes that are TC for Endrin based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Endrin |
72-20-8 |
BIODG; or CMBST |
0.13 and meet Section 728.148 standards8 |
Endrin aldehyde |
7421-93-4 |
BIODG; or CMBST |
0.13 and meet Section 728.148 standards8 |
D0139
Wastes that are TC for Lindane based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
a -BHC |
319-84-6 |
CARBN; or CMBST |
0.066 and meet Section 728.148 standards8 |
b -BHC |
319-85-7 |
CARBN; or CMBST |
0.066 and meet Section 728.148 standards8 |
d -BHC |
319-86-8 |
CARBN; or CMBST |
0.066 and meet Section 728.148 standards8 |
g -BHC (Lindane) |
58-89-9 |
CARBN; or CMBST |
0.066 and meet Section 728.148 standards8 |
D0149
Wastes that are TC for Methoxychlor based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Methoxychlor |
72-43-5 |
WETOX or CMBST |
0.18 and meet Section 728.148 standards8 |
D0159
Wastes that are TC for Toxaphene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Toxaphene |
8001-35-2 |
BIODG or CMBST |
2.6 and meet Section 728.148 standards8 |
D0169
Wastes that are TC for 2,4-D (2,4-Dichlorophenoxyacetic acid) based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
2,4-D (2,4-Dichlorophenoxyacetic acid) |
94-75-7 |
CHOXD; BIODG; or CMBST |
10 and meet Section 728.148 standards8 |
D0179
Wastes that are TC for 2,4,5-TP (Silvex) based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
2,4,5-TP (Silvex) |
93-72-1 |
CHOXD or CMBST |
7.9 and meet Section 728.148 standards8 |
D0189
Wastes that are TC for Benzene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Benzene |
71-43-2 |
0.14 and meet Section 728.148 standards8 |
10 and meet Section 728.148 standards8 |
D0199
Wastes that are TC for Carbon tetrachloride based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Carbon tetrachloride |
56-23-5 |
0.057 and meet Section 728.148 standards8 |
6.0 and meet Section 728.148 standards8 |
D0209
Wastes that are TC for Chlordane based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Chlordane ( a and c isomers) |
57-74-9 |
0.0033 and meet Section 728.148 standards8 |
0.26 and meet Section 728.148 standards8 |
D0219
Wastes that are TC for Chlorobenzene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Chlorobenzene |
108-90-7 |
0.057 and meet Section 728.148 standards8 |
6.0 and meet Section 728.148 standards8 |
D0229
Wastes that are TC for Chloroform based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Chloroform |
67-66-3 |
0.046 and meet Section 728.148 standards8 |
6.0 and meet Section 728.148 standards8 |
D0239
Wastes that are TC for o-Cresol based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
o-Cresol |
95-48-7 |
0.11 and meet Section 728.148 standards8 |
5.6 and meet Section 728.148 standards8 |
D0249
Wastes that are TC for m-Cresol based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
m-Cresol (difficult to distinguish from p-cresol) |
108-39-4 |
0.77 and meet Section 728.148 standards8 |
5.6 and meet Section 728.148 standards8 |
D0259
Wastes that are TC for p-Cresol based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
p-Cresol (difficult to distinguish from m-cresol) |
106-44-5 |
0.77 and meet Section 728.148 standards8 |
5.6 and meet Section 728.148 standards8 |
D0269
Wastes that are TC for Cresols (Total) based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations) |
1319-77-3 |
0.88 and meet Section 728.148 standards8 |
11.2 and meet Section 728.148 standards8 |
D0279
Wastes that are TC for p-Dichlorobenzene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
p-Dichlorobenzene (1,4-Dichlorobenzene) |
106-46-7 |
0.090 and meet Section 728.148 standards8 |
6.0 and meet Section 728.148 standards8 |
D0289
Wastes that are TC for 1,2-Dichloroethane based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
1,2-Dichloroethane |
107-06-2 |
0.21 and meet Section 728.148 standards8 |
6.0 and meet Section 728.148 standards8 |
D0299
Wastes that are TC for 1,1-Dichloroethylene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
1,1-Dichloroethylene |
75-35-4 |
0.025 and meet Section 728.148 standards8 |
6.0 and meet Section 728.148 standards8 |
D0309
Wastes that are TC for 2,4-Dinitrotoluene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
2,4-Dinitrotoluene |
121-14-2 |
0.32 and meet Section 728.148 standards8 |
140 and meet Section 728.148 standards8 |
D0319
Wastes that are TC for Heptachlor based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Heptachlor |
76-44-8 |
0.0012 and meet Section 728.148 standards8 |
0.066 and meet Section 728.148 standards8 |
Heptachlor epoxide |
1024-57-3 |
0.016 and meet Section 728.148 standards8 |
0.066 and meet Section 728.148 standards8 |
D0329
Wastes that are TC for Hexachlorobenzene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Hexachlorobenzene |
118-74-1 |
0.055 and meet Section 728.148 standards8 |
10 and meet Section 728.148 standards8 |
D0339
Wastes that are TC for Hexachlorobutadiene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Hexachlorobutadiene |
87-68-3 |
0.055 and meet Section 728.148 standards8 |
5.6 and meet Section 728.148 standards8 |
D0349
Wastes that are TC for Hexachloroethane based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Hexachloroethane |
67-72-1 |
0.055 and meet Section 728.148 standards8 |
30 and meet Section 728.148 standards8 |
D0359
Wastes that are TC for Methyl ethyl ketone based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Methyl ethyl ketone |
78-93-3 |
0.28 and meet Section 728.148 standards8 |
36 and meet Section 728.148 standards8 |
D0369
Wastes that are TC for Nitrobenzene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Nitrobenzene |
98-95-3 |
0.068 and meet Section 728.148 standards8 |
14 and meet Section 728.148 standards8 |
D0379
Wastes that are TC for Pentachlorophenol based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Pentachlorophenol |
87-86-5 |
0.089 and meet Section 728.148 standards8 |
7.4 and meet Section 728.148 standards8 |
D0389
Wastes that are TC for Pyridine based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Pyridine |
110-86-1 |
0.014 and meet Section 728.148 standards8 |
16 and meet Section 728.148 standards8 |
D0399
Wastes that are TC for Tetrachloroethylene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Tetrachloroethylene |
127-18-4 |
0.056 and meet Section 728.148 standards8 |
6.0 and meet Section 728.148 standards8 |
D0409
Wastes that are TC for Trichloroethylene based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Trichloroethylene |
79-01-6 |
0.054 and meet Section 728.148 standards8 |
6.0 and meet Section 728.148 standards8 |
D0419
Wastes that are TC for 2,4,5-Trichlorophenol based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
2,4,5-Trichlorophenol |
95-95-4 |
0.18 and meet Section 728.148 standards8 |
7.4 and meet Section 728.148 standards8 |
D0429
Wastes that are TC for 2,4,6-Trichlorophenol based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
2,4,6-Trichlorophenol |
88-06-2 |
0.035 and meet Section 728.148 standards8 |
7.4 and meet Section 728.148 standards8 |
D0439
Wastes that are TC for Vinyl chloride based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Vinyl chloride |
75-01-4 |
0.27 and meet Section 728.148 standards8 |
6.0 and meet Section 728.148 standards8 |
F001, F002, F003, F004 & F005
F001, F002, F003, F004, or F005 solvent wastes that contain any combination of one or more of the following spent solvents: acetone, benzene, n-butyl alcohol, carbon disulfide, carbon tetrachloride, chlorinated fluorocarbons, chlorobenzene, o-cresol, m-cresol, p-cresol, cyclohexanone, o-dichlorobenzene, 2-ethoxyethanol, ethyl acetate, ethyl benzene, ethyl ether, isobutyl alcohol, methanol, methylene chloride, methyl ethyl ketone, methyl isobutyl ketone, nitrobenzene, 2-nitropropane, pyridine, tetrachloroethylene, toluene, 1,1,1-trichloroethane, 1,1,2-trichloroethane, 1,1,2-trichloro-1,2,2-trifluoroethane, trichloroethylene, trichloromonofluoromethane, or xylenes (except as specifically noted in other subcategories). See further details of these listings in 35 Ill. Adm. Code 721.131.
Acetone |
67-64-1 |
0.28 |
160 |
Benzene |
71-43-2 |
0.14 |
10 |
n-Butyl alcohol |
71-36-3 |
5.6 |
2.6 |
Carbon disulfide |
75-15-0 |
3.8 |
NA |
Carbon tetrachloride |
56-23-5 |
0.057 |
6.0 |
Chlorobenzene |
108-90-7 |
0.057 |
6.0 |
o-Cresol |
95-48-7 |
0.11 |
5.6 |
m-Cresol (difficult to distinguish from p-cresol) |
108-39-4 |
0.77 |
5.6 |
p-Cresol (difficult to distinguish from m-cresol) |
106-44-5 |
0.77 |
5.6 |
Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations) |
1319-77-3 |
0.88 |
11.2 |
Cyclohexanone |
108-94-1 |
0.36 |
NA |
o-Dichlorobenzene |
95-50-1 |
0.088 |
6.0 |
Ethyl acetate |
141-78-6 |
0.34 |
33 |
Ethyl benzene |
100-41-4 |
0.057 |
10 |
Ethyl ether |
60-29-7 |
0.12 |
160 |
Isobutyl alcohol |
78-83-1 |
5.6 |
170 |
Methanol |
67-56-1 |
5.6 |
NA |
Methylene chloride |
75-9-2 |
0.089 |
30 |
Methyl ethyl ketone |
78-93-3 |
0.28 |
36 |
Methyl isobutyl ketone |
108-10-1 |
0.14 |
33 |
Nitrobenzene |
98-95-3 |
0.068 |
14 |
Pyridine |
110-86-1 |
0.014 |
16 |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
Toluene |
108-88-3 |
0.080 |
10 |
1,1,1-Trichloroethane |
71-55-6 |
0.054 |
6.0 |
1,1,2-Trichloroethane |
79-00-5 |
0.054 |
6.0 |
1,1,2-Trichloro-1,2,2-trifluoroethane |
76-13-1 |
0.057 |
30 |
Trichloroethylene |
79-01-6 |
0.054 |
6.0 |
Trichloromonofluoromethane |
75-69-4 |
0.020 |
30 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
F001, F002, F003, F004 & F005
F003 and F005 solvent wastes that contain any combination of one or more of the following three solvents as the only listed F001 through F005 solvents: carbon disulfide, cyclohexanone, or methanol. (Formerly Section 728.141(c)).
Carbon disulfide |
75-15-0 |
3.8 |
4.8 mg/l TCLP |
Cyclohexanone |
108-94-1 |
0.36 |
0.75 mg/l TCLP |
Methanol |
67-56-1 |
5.6 |
0.75 mg/l TCLP |
F001, F002, F003, F004 & F005
F005 solvent waste containing 2-Nitropropane as the only listed F001 through F005 solvent.
2-Nitropropane |
79-46-9 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
F001, F002, F003, F004 & F005
F005 solvent waste containing 2-Ethoxyethanol as the only listed F001 through F005 solvent.
2-Ethoxyethanol |
110-80-5 |
BIODG; or CMBST |
CMBST |
F006
Wastewater treatment sludges from electroplating operations except from the following processes: (1) Sulfuric acid anodizing of aluminum; (2) tin plating on carbon steel; (3) zinc plating (segregated basis) on carbon steel; (4) aluminum or zinc-aluminum plating on carbon steel; (5) cleaning or stripping associated with tin, zinc, and aluminum plating on carbon steel; and (6) chemical etching and milling of aluminum.
Cadmium |
7440-43-9 |
0.69 |
0.11 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
Silver |
7440-22-4 |
NA |
0.14 mg/l TCLP |
F007
Spent cyanide plating bath solutions from electroplating operations.
Cadmium |
7440-43-9 |
NA |
0.11 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
Silver |
7440-22-4 |
NA |
0.14 mg/l TCLP |
F008
Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process.
Cadmium |
7440-43-9 |
NA |
0.11 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
Silver |
7440-22-4 |
NA |
0.14 mg/l TCLP |
F009
Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process.
Cadmium |
7440-43-9 |
NA |
0.11 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
Silver |
7440-22-4 |
NA |
0.14 mg/l TCLP |
F010
Quenching bath residues from oil baths from metal heat treating heat-treating operations where cyanides are used in the process.
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
NA |
F011
Spent cyanide solutions from salt bath pot cleaning from metal heat treating heat-treating operations.
Cadmium |
7440-43-9 |
NA |
0.11 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
Silver |
7440-22-4 |
NA |
0.14 mg/l TCLP |
F012
Quenching wastewater treatment sludges from metal heat treating heat-treating operations where cyanides are used in the process.
Cadmium |
7440-43-9 |
NA |
0.11 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
Silver |
7440-22-4 |
NA |
0.14 mg/l TCLP |
F019
Wastewater treatment sludges from the chemical conversion coating of aluminum, except from zirconium phosphating in aluminum can washing when such phosphating is an exclusive conversion coating process.
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
F020, F021, F022, F023, F026
Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of: (1) tri- or tetrachlorophenol, or of intermediates used to produce their pesticide derivatives, excluding wastes from the production of Hexachlorophene from highly purified 2,4,5-trichlorophenol (i.e., F020); (2) pentachlorophenol, or of intermediates used to produce its derivatives (i.e., F021); (3) tetra-, penta-, or hexachlorobenzenes under alkaline conditions (i.e., F022) and wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials on equipment previously used for the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of: (1) tri- or tetrachlorophenols, excluding wastes from equipment used only for the production of Hexachlorophene from highly purified 2,4,5-trichlorophenol (F023) or (2) tetra-, penta-, or hexachlorobenzenes under alkaline conditions (i.e., F026).
HxCDDs (All Hexachlorodibenzo-p-dioxins) |
NA |
0.000063 |
0.001 |
HxCDFs (All Hexachlorodibenzofurans) |
55684-94-1 |
0.000063 |
0.001 |
PeCDDs (All Pentachlorodibenzo-p-dioxins) |
36088-22-9 |
0.000063 |
0.001 |
PeCDFs (All Pentachlorodibenzofurans) |
30402-15-4 |
0.000035 |
0.001 |
Pentachlorophenol |
87-86-5 |
0.089 |
7.4 |
TCDDs (All Tetrachlorodibenzo-p-dioxins) |
41903-57-5 |
0.000063 |
0.001 |
TCDFs (All Tetrachlorodibenzofurans) |
55722-27-5 |
0.000063 |
0.001 |
2,4,5-Trichlorophenol |
95-95-4 |
0.18 |
7.4 |
2,4,6-Trichlorophenol |
88-06-2 |
0.035 |
7.4 |
2,3,4,6-Tetrachlorophenol |
58-90-2 |
0.030 |
7.4 |
F024
Process wastes, including but not limited to, distillation residues, heavy ends, tars, and reactor clean-out wastes, from the production of certain chlorinated aliphatic hydrocarbons by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. (This listing does not include wastewaters, wastewater treatment sludges, spent catalysts, and wastes listed in 35 Ill. Adm. Code 721.131 or 721.132.)
All F024 wastes |
NA |
CMBST11 |
CMBST11 |
2-Chloro-1,3-butadiene |
126-99-8 |
0.057 |
0.28 |
3-Chloropropylene |
107-05-1 |
0.036 |
30 |
1,1-Dichloroethane |
75-34-3 |
0.059 |
6.0 |
1,2-Dichloroethane |
107-06-2 |
0.21 |
6.0 |
1,2-Dichloropropane |
78-87-5 |
0.85 |
18 |
cis-1,3-Dichloropropylene |
10061-01-5 |
0.036 |
18 |
trans-1,3-Dichloropropylene |
10061-02-6 |
0.036 |
18 |
bis(2-Ethylhexyl) phthalate |
117-81-7 |
0.28 |
28 |
Hexachloroethane |
67-72-1 |
0.055 |
30 |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
F025
Condensed light ends from the production of certain chlorinated aliphatic hydrocarbons by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one up to and including five, with varying amounts and positions of chlorine substitution. F025--Light Ends Subcategory.
Carbon tetrachloride |
56-23-5 |
0.057 |
6.0 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
1,2-Dichloroethane |
107-06-2 |
0.21 |
6.0 |
1,1-Dichloroethylene |
75-35-4 |
0.025 |
6.0 |
Methylene chloride |
75-9-2 |
0.089 |
30 |
1,1,2-Trichloroethane |
79-00-5 |
0.054 |
6.0 |
Trichloroethylene |
79-01-6 |
0.054 |
6.0 |
Vinyl chloride |
75-01-4 |
0.27 |
6.0 |
F025
Spent filters and filter aids, and spent desiccant wastes from the production of certain chlorinated aliphatic hydrocarbons by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. F025--Spent Filters/Aids and Desiccants Subcategory.
Carbon tetrachloride |
56-23-5 |
0.057 |
6.0 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
Hexachlorobenzene |
118-74-1 |
0.055 |
10 |
Hexachlorobutadiene |
87-68-3 |
0.055 |
5.6 |
Hexachloroethane |
67-72-1 |
0.055 |
30 |
Methylene chloride |
75-9-2 |
0.089 |
30 |
1,1,2-Trichloroethane |
79-00-5 |
0.054 |
6.0 |
Trichloroethylene |
79-01-6 |
0.054 |
6.0 |
Vinyl chloride |
75-01-4 |
0.27 |
6.0 |
F027
Discarded unused formulations containing tri-, tetra-, or pentachlorophenol or discarded unused formulations containing compounds derived from these chlorophenols. (This listing does not include formulations containing hexachlorophene synthesized from prepurified 2,4,5-trichlorophenol as the sole component.)
HxCDDs (All Hexachlorodibenzo-p-dioxins) |
NA |
0.000063 |
0.001 |
HxCDFs (All Hexachlorodibenzofurans) |
55684-94-1 |
0.000063 |
0.001 |
PeCDDs (All Pentachlorodibenzo-p-dioxins) |
36088-22-9 |
0.000063 |
0.001 |
PeCDFs (All Pentachlorodibenzofurans) |
30402-15-4 |
0.000035 |
0.001 |
Pentachlorophenol |
87-86-5 |
0.089 |
7.4 |
TCDDs (All Tetrachlorodibenzo-p-dioxins) |
41903-57-5 |
0.000063 |
0.001 |
TCDFs (All Tetrachlorodibenzofurans) |
55722-27-5 |
0.000063 |
0.001 |
2,4,5-Trichlorophenol |
95-95-4 |
0.18 |
7.4 |
2,4,6-Trichlorophenol |
88-06-2 |
0.035 |
7.4 |
2,3,4,6-Tetrachlorophenol |
58-90-2 |
0.030 |
7.4 |
F028
Residues resulting from the incineration or thermal treatment of soil contaminated with USEPA hazardous waste numbers F020, F021, F023, F026, and F027.
HxCDDs (All Hexachlorodibenzo-p-dioxins) |
NA |
0.000063 |
0.001 |
HxCDFs (All Hexachlorodibenzofurans) |
55684-94-1 |
0.000063 |
0.001 |
PeCDDs (All Pentachlorodibenzo-p-dioxins) |
36088-22-9 |
0.000063 |
0.001 |
PeCDFs (All Pentachlorodibenzofurans) |
30402-15-4 |
0.000035 |
0.001 |
Pentachlorophenol |
87-86-5 |
0.089 |
7.4 |
TCDDs (All Tetrachlorodibenzo-p-dioxins) |
41903-57-5 |
0.000063 |
0.001 |
TCDFs (All Tetrachlorodibenzofurans) |
55722-27-5 |
0.000063 |
0.001 |
2,4,5-Trichlorophenol |
95-95-4 |
0.18 |
7.4 |
2,4,6-Trichlorophenol |
88-06-2 |
0.035 |
7.4 |
2,3,4,6-Tetrachlorophenol |
58-90-2 |
0.030 |
7.4 |
F032
Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that currently use or have previously used chlorophenolic formulations (except potentially cross-contaminated wastes that have had the F032 waste code deleted in accordance with 35 Ill. Adm. Code 721.135 or potentially cross-contaminated wastes that are otherwise currently regulated as hazardous wastes (i.e., F034 or F035), where the generator does not resume or initiate use of chlorophenolic formulations). This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote or penta-chlorophenol.
Acenaphthene |
83-32-9 |
0.059 |
3.4 |
Anthracene |
120-12-7 |
0.059 |
3.4 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(b)fluoranthene (difficult to distinguish from benzo(k) fluoranthene) |
205-99-2 |
0.11 |
6.8 |
Benzo(k)fluoranthene (difficult to distinguish from benzo(b) fluoranthene) |
207-08-9 |
0.11 |
6.8 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Dibenz(a,h)anthracene |
53-70-3 |
0.055 |
8.2 |
2-4-Dimethyl phenol |
105-67-9 |
0.036 |
14 |
Fluorene |
86-73-7 |
0.059 |
3.4 |
Hexachlorodibenzo-p-dioxins |
NA |
0.000063 or CMBST11 |
0.001 or CMBST11 |
Hexachlorodibenzofurans |
NA |
0.000063 or CMBST11 |
0.001 or CMBST11 |
Indeno (1,2,3-c,d) pyrene |
193-39-5 |
0.0055 |
3.4 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Pentachlorodibenzo-p-dioxins |
NA |
0.000063 or CMBST11 |
0.001 or CMBST11 |
Pentachlorodibenzofurans |
NA |
0.000035 or CMBST11 |
0.001 or CMBST11 |
Pentachlorophenol |
87-86-5 |
0.089 |
7.4 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Tetrachlorodibenzo-p-dioxins |
NA |
0.000063 or CMBST11 |
0.001 or CMBST11 |
Tetrachlorodibenzofurans |
NA |
0.000063 or CMBST11 |
0.001 or CMBST11 |
2,3,4,6-Tetrachlorophenol |
58-90-2 |
0.030 |
7.4 |
2,4,6-Trichlorophenol |
88-06-2 |
0.035 |
7.4 |
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
F034
Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use creosote formulations. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote or pentachlorophenol.
Acenaphthene |
83-32-9 |
0.059 |
3.4 |
Anthracene |
120-12-7 |
0.059 |
3.4 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) |
205-99-2 |
0.11 |
6.8 |
Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) |
207-08-9 |
0.11 |
6.8 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Dibenz(a,h)anthracene |
53-70-3 |
0.055 |
8.2 |
Fluorene |
86-73-7 |
0.059 |
3.4 |
Indeno (1,2,3-c,d) pyrene |
193-39-5 |
0.0055 |
3.4 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
F035
Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes that are generated at plants that use inorganic preservatives containing arsenic or chromium. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote or pentachlorophenol.
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
F037
Petroleum refinery primary oil/water/solids separation sludge--Any sludge generated from the gravitational separation of oil/water/solids during the storage or treatment of process wastewaters and oily cooling wastewaters from petroleum refineries. Such sludges include, but are not limited to, those generated in: oil/water/solids separators; tanks, and impoundments; ditches, and other conveyances; sumps; and stormwater units receiving dry weather flow. Sludge generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges generated in aggressive biological treatment units as defined in 35 Ill. Adm. Code 721.131(b)(2) (including sludges generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and K051 wastes are not included in this listing.
Acenaphthene |
83-32-9 |
0.059 |
NA |
Anthracene |
120-12-7 |
0.059 |
3.4 |
Benzene |
71-43-2 |
0.14 |
10 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
bis(2-Ethylhexyl) phthalate |
117-81-7 |
0.28 |
28 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Di-n-butyl phthalate |
84-74-2 |
0.057 |
28 |
Ethylbenzene |
100-41-4 |
0.057 |
10 |
Fluorene |
86-73-7 |
0.059 |
NA |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Toluene |
108-88-3 |
0.080 |
10 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Lead |
7439-92-1 |
0.69 |
NA |
Nickel |
7440-02-0 |
NA |
11 mg/l TCLP |
F038
Petroleum refinery secondary (emulsified) oil/water/solids separation sludge or float generated from the physical or chemical separation of oil/water/solids in process wastewaters and oily cooling wastewaters from petroleum refineries. Such wastes include, but are not limited to, all sludges and floats generated in: induced air floatation (IAF) units, tanks, and impoundments, and all sludges generated in DAF units. Sludges generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges, and floats generated in aggressive biological treatment units as defined in 35 Ill. Adm. Code 721.131(b)(2) (including sludges and floats generated in one or more additional units after wastewaters have been treated in aggressive biological units) and F037, K048, and K051 are not included in this listing.
Benzene |
71-43-2 |
0.14 |
10 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
bis(2-Ethylhexyl) phthalate |
117-81-7 |
0.28 |
28 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Di-n-butyl phthalate |
84-74-2 |
0.057 |
28 |
Ethylbenzene |
100-41-4 |
0.057 |
10 |
Fluorene |
86-73-7 |
0.059 |
NA |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Toluene |
108-88-3 |
0.080 |
10 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Lead |
7439-92-1 |
0.69 |
NA |
Nickel |
7440-02-0 |
NA |
11 mg/l TCLP |
F039
Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one restricted waste classified as hazardous under Subpart D of this Part. (Leachate resulting from the disposal of one or more of the following USEPA hazardous wastes and no other hazardous wastes retains its USEPA hazardous waste numbers: F020, F021, F022, F026, F027, or F028.).
Acenaphthylene |
208-96-8 |
0.059 |
3.4 |
Acenaphthene |
83-32-9 |
0.059 |
3.4 |
Acetone |
67-64-1 |
0.28 |
160 |
Acetonitrile |
75-05-8 |
5.6 |
NA |
Acetophenone |
96-86-2 |
0.010 |
9.7 |
2-Acetylaminofluorene |
53-96-3 |
0.059 |
140 |
Acrolein |
107-02-8 |
0.29 |
NA |
Acrylonitrile |
107-13-1 |
0.24 |
84 |
Aldrin |
309-00-2 |
0.021 |
0.066 |
4-Aminobiphenyl |
92-67-1 |
0.13 |
NA |
Aniline |
62-53-3 |
0.81 |
14 |
Anthracene |
120-12-7 |
0.059 |
3.4 |
Aramite |
140-57-8 |
0.36 |
NA |
a -BHC |
319-84-6 |
0.00014 |
0.066 |
b -BHC |
319-85-7 |
0.00014 |
0.066 |
d -BHC |
319-86-8 |
0.023 |
0.066 |
g -BHC |
58-89-9 |
0.0017 |
0.066 |
Benzene |
71-43-2 |
0.14 |
10 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) |
205-99-2 |
0.11 |
6.8 |
Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) |
207-08-9 |
0.11 |
6.8 |
Benzo(g,h,i)perylene |
191-24-2 |
0.0055 |
1.8 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Bromodichloromethane |
75-27-4 |
0.35 |
15 |
Methyl bromide (Bromomethane) |
74-83-9 |
0.11 |
15 |
4-Bromophenyl phenyl ether |
101-55-3 |
0.055 |
15 |
n-Butyl alcohol |
71-36-3 |
5.6 |
2.6 |
Butyl benzyl phthalate |
85-68-7 |
0.017 |
28 |
2-sec-Butyl-4,6-dinitrophenol (Dinoseb) |
88-85-7 |
0.066 |
2.5 |
Carbon disulfide |
75-15-0 |
3.8 |
NA |
Carbon tetrachloride |
56-23-5 |
0.057 |
6.0 |
Chlordane ( a and c isomers) |
57-74-9 |
0.0033 |
0.26 |
p-Chloroaniline |
106-47-8 |
0.46 |
16 |
Chlorobenzene |
108-90-7 |
0.057 |
6.0 |
Chlorobenzilate |
510-15-6 |
0.10 |
NA |
2-Chloro-1,3-butadiene |
126-99-8 |
0.057 |
NA |
Chlorodibromomethane |
124-48-1 |
0.057 |
15 |
Chloroethane |
75-00-3 |
0.27 |
6.0 |
bis(2-Chloroethoxy)methane |
111-91-1 |
0.036 |
7.2 |
bis(2-Chloroethyl)ether |
111-44-4 |
0.033 |
6.0 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
bis(2-Chloroisopropyl)ether |
39638-32-9 |
0.055 |
7.2 |
p-Chloro-m-cresol |
59-50-7 |
0.018 |
14 |
Chloromethane (Methyl chloride) |
74-87-3 |
0.19 |
30 |
2-Chloronaphthalene |
91-58-7 |
0.055 |
5.6 |
2-Chlorophenol |
95-57-8 |
0.044 |
5.7 |
3-Chloropropylene |
107-05-1 |
0.036 |
30 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
o-Cresol |
95-48-7 |
0.11 |
5.6 |
m-Cresol (difficult to distinguish from p-cresol) |
108-39-4 |
0.77 |
5.6 |
p-Cresol (difficult to distinguish from m-cresol) |
106-44-5 |
0.77 |
5.6 |
Cyclohexanone |
108-94-1 |
0.36 |
NA |
1,2-Dibromo-3-chloropropane |
96-12-8 |
0.11 |
15 |
Ethylene dibromide (1,2-Dibromoethane) |
106-93-4 |
0.028 |
15 |
Dibromomethane |
74-95-3 |
0.11 |
15 |
2,4-D (2,4-Dichlorophenoxyacetic acid) |
94-75-7 |
0.72 |
10 |
o,p'-DDD |
53-19-0 |
0.023 |
0.087 |
p,p'-DDD |
72-54-8 |
0.023 |
0.087 |
o,p'-DDE |
3424-82-6 |
0.031 |
0.087 |
p,p'-DDE |
72-55-9 |
0.031 |
0.087 |
o,p'-DDT |
789-02-6 |
0.0039 |
0.087 |
p,p'-DDT |
50-29-3 |
0.0039 |
0.087 |
Dibenz(a,h)anthracene |
53-70-3 |
0.055 |
8.2 |
Dibenz(a,e)pyrene |
192-65-4 |
0.061 |
NA |
m-Dichlorobenzene |
541-73-1 |
0.036 |
6.0 |
o-Dichlorobenzene |
95-50-1 |
0.088 |
6.0 |
p-Dichlorobenzene |
106-46-7 |
0.090 |
6.0 |
Dichlorodifluoromethane |
75-71-8 |
0.23 |
7.2 |
1,1-Dichloroethane |
75-34-3 |
0.059 |
6.0 |
1,2-Dichloroethane |
107-06-2 |
0.21 |
6.0 |
1,1-Dichloroethylene |
75-35-4 |
0.025 |
6.0 |
trans-1,2-Dichloroethylene |
156-60-5 |
0.054 |
30 |
2,4-Dichlorophenol |
120-83-2 |
0.044 |
14 |
2,6-Dichlorophenol |
87-65-0 |
0.044 |
14 |
1,2-Dichloropropane |
78-87-5 |
0.85 |
18 |
cis-1,3-Dichloropropylene |
10061-01-5 |
0.036 |
18 |
trans-1,3-Dichloropropylene |
10061-02-6 |
0.036 |
18 |
Dieldrin |
60-57-1 |
0.017 |
0.13 |
Diethyl phthalate |
84-66-2 |
0.20 |
28 |
2-4-Dimethyl phenol |
105-67-9 |
0.036 |
14 |
Dimethyl phthalate |
131-11-3 |
0.047 |
28 |
Di-n-butyl phthalate |
84-74-2 |
0.057 |
28 |
1,4-Dinitrobenzene |
100-25-4 |
0.32 |
2.3 |
4,6-Dinitro-o-cresol |
534-52-1 |
0.28 |
160 |
2,4-Dinitrophenol |
51-28-5 |
0.12 |
160 |
2,4-Dinitrotoluene |
121-14-2 |
0.32 |
140 |
2,6-Dinitrotoluene |
606-20-2 |
0.55 |
28 |
Di-n-octyl phthalate |
117-84-0 |
0.017 |
28 |
Di-n-propylnitrosamine |
621-64-7 |
0.40 |
14 |
1,4-Dioxane |
123-91-1 |
12.0 |
170 |
Diphenylamine (difficult to distinguish from diphenylnitrosamine) |
122-39-4 |
0.92 |
NA |
Diphenylnitrosamine (difficult to distinguish from diphenylamine) |
86-30-6 |
0.92 |
NA |
1,2-Diphenylhydrazine |
122-66-7 |
0.087 |
NA |
Disulfoton |
298-04-4 |
0.017 |
6.2 |
Endosulfan I |
939-98-8 |
0.023 |
0.066 |
Endosulfan II |
33213-6-5 |
0.029 |
0.13 |
Endosulfan sulfate |
1031-07-8 |
0.029 |
0.13 |
Endrin |
72-20-8 |
0.0028 |
0.13 |
Endrin aldehyde |
7421-93-4 |
0.025 |
0.13 |
Ethyl acetate |
141-78-6 |
0.34 |
33 |
Ethyl cyanide (Propanenitrile) |
107-12-0 |
0.24 |
360 |
Ethyl benzene |
100-41-4 |
0.057 |
10 |
Ethyl ether |
60-29-7 |
0.12 |
160 |
bis(2-Ethylhexyl) phthalate |
117-81-7 |
0.28 |
28 |
Ethyl methacrylate |
97-63-2 |
0.14 |
160 |
Ethylene oxide |
75-21-8 |
0.12 |
NA |
Famphur |
52-85-7 |
0.017 |
15 |
Fluoranthene |
206-44-0 |
0.068 |
3.4 |
Fluorene |
86-73-7 |
0.059 |
3.4 |
Heptachlor |
76-44-8 |
0.0012 |
0.066 |
1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD) |
35822-46-9 |
0.000035 |
0.0025 |
1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF) |
67562-39-4 |
0.000035 |
0.0025 |
1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF) |
55673-89-7 |
0.000035 |
0.0025 |
Heptachlor epoxide |
1024-57-3 |
0.016 |
0.066 |
Hexachlorobenzene |
118-74-1 |
0.055 |
10 |
Hexachlorobutadiene |
87-68-3 |
0.055 |
5.6 |
Hexachlorocyclopentadiene |
77-47-4 |
0.057 |
2.4 |
HxCDDs (All Hexachlorodibenzo-p-dioxins) |
NA |
0.000063 |
0.001 |
HxCDFs (All Hexachlorodibenzofurans) |
55684-94-1 |
0.000063 |
0.001 |
Hexachloroethane |
67-72-1 |
0.055 |
30 |
Hexachloropropylene |
1888-71-7 |
0.035 |
30 |
Indeno (1,2,3-c,d) pyrene |
193-39-5 |
0.0055 |
3.4 |
Iodomethane |
74-88-4 |
0.19 |
65 |
Isobutyl alcohol |
78-83-1 |
5.6 |
170 |
Isodrin |
465-73-6 |
0.021 |
0.066 |
Isosafrole |
120-58-1 |
0.081 |
2.6 |
Kepone |
143-50-8 |
0.0011 |
0.13 |
Methacrylonitrile |
126-98-7 |
0.24 |
84 |
Methanol |
67-56-1 |
5.6 |
NA |
Methapyrilene |
91-80-5 |
0.081 |
1.5 |
Methoxychlor |
72-43-5 |
0.25 |
0.18 |
3-Methylcholanthrene |
56-49-5 |
0.0055 |
15 |
4,4-Methylene bis(2-chloroaniline) |
101-14-4 |
0.50 |
30 |
Methylene chloride |
75-09-2 |
0.089 |
30 |
Methyl ethyl ketone |
78-93-3 |
0.28 |
36 |
Methyl isobutyl ketone |
108-10-1 |
0.14 |
33 |
Methyl methacrylate |
80-62-6 |
0.14 |
160 |
Methyl methansulfonate |
66-27-3 |
0.018 |
NA |
Methyl parathion |
298-00-0 |
0.014 |
4.6 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
2-Naphthylamine |
91-59-8 |
0.52 |
NA |
p-Nitroaniline |
100-01-6 |
0.028 |
28 |
Nitrobenzene |
98-95-3 |
0.068 |
14 |
5-Nitro-o-toluidine |
99-55-8 |
0.32 |
28 |
p-Nitrophenol |
100-02-7 |
0.12 |
29 |
N-Nitrosodiethylamine |
55-18-5 |
0.40 |
28 |
N-Nitrosodimethylamine |
62-75-9 |
0.40 |
NA |
N-Nitroso-di-n-butylamine |
924-16-3 |
0.40 |
17 |
N-Nitrosomethylethylamine |
10595-95-6 |
0.40 |
2.3 |
N-Nitrosomorpholine |
59-89-2 |
0.40 |
2.3 |
N-Nitrosopiperidine |
100-75-4 |
0.013 |
35 |
N-Nitrosopyrrolidine |
930-55-2 |
0.013 |
35 |
1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (1,2,3,4,6,7,8,9-OCDD) |
3268-87-9 |
0.000063 |
0.0025 |
Parathion |
56-38-2 |
0.014 |
4.6 |
Total PCBs (sum of all PCB isomers, or all Aroclors) |
1336-36-3 |
0.10 |
10 |
Pentachlorobenzene |
608-93-5 |
0.055 |
10 |
PeCDDs (All Pentachlorodibenzo-p-dioxins) |
36088-22-9 |
0.000063 |
0.001 |
PeCDFs (All Pentachlorodibenzofurans) |
30402-15-4 |
0.000035 |
0.001 |
Pentachloronitrobenzene |
82-68-8 |
0.055 |
4.8 |
Pentachlorophenol |
87-86-5 |
0.089 |
7.4 |
Phenacetin |
62-44-2 |
0.081 |
16 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Phorate |
298-02-2 |
0.021 |
4.6 |
Phthalic anhydride |
85-44-9 |
0.055 |
NA |
Pronamide |
23950-58-5 |
0.093 |
1.5 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Pyridine |
110-86-1 |
0.014 |
16 |
Safrole |
94-59-7 |
0.081 |
22 |
Silvex (2,4,5-TP) |
93-72-1 |
0.72 |
7.9 |
2,4,5-T |
93-76-5 |
0.72 |
7.9 |
1,2,4,5-Tetrachlorobenzene |
95-94-3 |
0.055 |
14 |
TCDDs (All Tetrachlorodibenzo-p-dioxins) |
41903-57-5 |
0.000063 |
0.001 |
TCDFs (All Tetrachlorodibenzofurans) |
55722-27-5 |
0.000063 |
0.001 |
1,1,1,2-Tetrachloroethane |
630-20-6 |
0.057 |
6.0 |
1,1,2,2-Tetrachloroethane |
79-34-6 |
0.057 |
6.0 |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
2,3,4,6-Tetrachlorophenol |
58-90-2 |
0.030 |
7.4 |
Toluene |
108-88-3 |
0.080 |
10 |
Toxaphene |
8001-35-2 |
0.0095 |
2.6 |
Bromoform (Tribromomethane) |
75-25-2 |
0.63 |
15 |
1,2,4-Trichlorobenzene |
120-82-1 |
0.055 |
19 |
1,1,1-Trichloroethane |
71-55-6 |
0.054 |
6.0 |
1,1,2-Trichloroethane |
79-00-5 |
0.054 |
6.0 |
Trichloroethylene |
79-01-6 |
0.054 |
6.0 |
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 |
1,2,3-Trichloropropane |
96-18-4 |
0.85 |
30 |
1,1,2-Trichloro-1,2,2-trifluoroethane |
76-13-1 |
0.057 |
30 |
tris(2,3-Dibromopropyl) phosphate |
126-72-7 |
0.11 |
NA |
Vinyl chloride |
75-01-4 |
0.27 |
6.0 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
Antimony |
7440-36-0 |
1.9 |
1.15 mg/l TCLP |
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
Barium |
7440-39-3 |
1.2 |
21 mg/l TCLP |
Beryllium |
7440-41-7 |
0.82 |
NA |
Cadmium |
7440-43-9 |
0.69 |
0.11 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
NA |
Fluoride |
16964-48-8 |
35 |
NA |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Mercury |
7439-97-6 |
0.15 |
0.025 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
Selenium |
7782-49-2 |
0.82 |
5.7 mg/l TCLP |
Silver |
7440-22-4 |
0.43 |
0.14 mg/l TCLP |
Sulfide |
8496-25-8 |
14 |
NA |
Thallium |
7440-28-0 |
1.4 |
NA |
Vanadium |
7440-62-2 |
4.3 |
NA |
K001
Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote or pentachlorophenol.
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Pentachlorophenol |
87-86-5 |
0.089 |
7.4 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Toluene |
108-88-3 |
0.080 |
10 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
K002
Wastewater treatment sludge from the production of chrome yellow and orange pigments.
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
K003
Wastewater treatment sludge from the production of molybdate orange pigments.
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
K004
Wastewater treatment sludge from the production of zinc yellow pigments.
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
K005
Wastewater treatment sludge from the production of chrome green pigments.
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
K006
Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous).
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
K006
Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated).
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
NA |
K007
Wastewater treatment sludge from the production of iron blue pigments.
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
K008
Oven residue from the production of chrome oxide green pigments.
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
K009
Distillation bottoms from the production of acetaldehyde from ethylene.
Chloroform |
67-66-3 |
0.046 |
6.0 |
K010
Distillation side cuts from the production of acetaldehyde from ethylene.
Chloroform |
67-66-3 |
0.046 |
6.0 |
K011
Bottom stream from the wastewater stripper in the production of acrylonitrile.
Acetonitrile |
75-05-8 |
5.6 |
38 |
Acrylonitrile |
107-13-1 |
0.24 |
84 |
Acrylamide |
79-06-1 |
19 |
23 |
Benzene |
71-43-2 |
0.14 |
10 |
Cyanide (Total) |
57-12-5 |
1.2 |
590 |
K013
Bottom stream from the acetonitrile column in the production of acrylonitrile.
Acetonitrile |
75-05-8 |
5.6 |
38 |
Acrylonitrile |
107-13-1 |
0.24 |
84 |
Acrylamide |
79-06-1 |
19 |
23 |
Benzene |
71-43-2 |
0.14 |
10 |
Cyanide (Total) |
57-12-5 |
1.2 |
590 |
K014
Bottoms from the acetonitrile purification column in the production of acrylonitrile.
Acetonitrile |
75-05-8 |
5.6 |
38 |
Acrylonitrile |
107-13-1 |
0.24 |
84 |
Acrylamide |
79-06-1 |
19 |
23 |
Benzene |
71-43-2 |
0.14 |
10 |
Cyanide (Total) |
57-12-5 |
1.2 |
590 |
K015
Still bottoms from the distillation of benzyl chloride.
Anthracene |
120-12-7 |
0.059 |
3.4 |
Benzal chloride |
98-87-3 |
0.055 |
6.0 |
Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) |
205-99-2 |
0.11 |
6.8 |
Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) |
207-08-9 |
0.11 |
6.8 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Toluene |
108-88-3 |
0.080 |
10 |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
K016
Heavy ends or distillation residues from the production of carbon tetrachloride.
Hexachlorobenzene |
118-74-1 |
0.055 |
10 |
Hexachlorobutadiene |
87-68-3 |
0.055 |
5.6 |
Hexachlorocyclopentadiene |
77-47-4 |
0.057 |
2.4 |
Hexachloroethane |
67-72-1 |
0.055 |
30 |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
K017
Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.
bis(2-Chloroethyl)ether |
111-44-4 |
0.033 |
6.0 |
1,2-Dichloropropane |
78-87-5 |
0.85 |
18 |
1,2,3-Trichloropropane |
96-18-4 |
0.85 |
30 |
K018
Heavy ends from the fractionation column in ethyl chloride production.
Chloroethane |
75-00-3 |
0.27 |
6.0 |
Chloromethane |
74-87-3 |
0.19 |
NA |
1,1-Dichloroethane |
75-34-3 |
0.059 |
6.0 |
1,2-Dichloroethane |
107-06-2 |
0.21 |
6.0 |
Hexachlorobenzene |
118-74-1 |
0.055 |
10 |
Hexachlorobutadiene |
87-68-3 |
0.055 |
5.6 |
Hexachloroethane |
67-72-1 |
0.055 |
30 |
Pentachloroethane |
76-01-7 |
NA |
6.0 |
1,1,1-Trichloroethane |
71-55-6 |
0.054 |
6.0 |
K019
Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production.
bis(2-Chloroethyl)ether |
111-44-4 |
0.033 |
6.0 |
Chlorobenzene |
108-90-7 |
0.057 |
6.0 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
p-Dichlorobenzene |
106-46-7 |
0.090 |
NA |
1,2-Dichloroethane |
107-06-2 |
0.21 |
6.0 |
Fluorene |
86-73-7 |
0.059 |
NA |
Hexachloroethane |
67-72-1 |
0.055 |
30 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
1,2,4,5-Tetrachlorobenzene |
95-94-3 |
0.055 |
NA |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
1,2,4-Trichlorobenzene |
120-82-1 |
0.055 |
19 |
1,1,1-Trichloroethane |
71-55-6 |
0.054 |
6.0 |
K020
Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.
1,2-Dichloroethane |
107-06-2 |
0.21 |
6.0 |
1,1,2,2-Tetrachloroethane |
79-34-6 |
0.057 |
6.0 |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
K021
Aqueous spent antimony catalyst waste from fluoromethanes production.
Carbon tetrachloride |
56-23-5 |
0.057 |
6.0 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
Antimony |
7440-36-0 |
1.9 |
1.15 mg/l TCLP |
K022
Distillation bottom tars from the production of phenol or acetone from cumene.
Toluene |
108-88-3 |
0.080 |
10 |
Acetophenone |
96-86-2 |
0.010 |
9.7 |
Diphenylamine (difficult to distinguish from diphenylnitrosamine) |
122-39-4 |
0.92 |
13 |
Diphenylnitrosamine (difficult to distinguish from diphenylamine) |
86-30-6 |
0.92 |
13 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
K023
Distillation light ends from the production of phthalic anhydride from naphthalene.
Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) |
100-21-0 |
0.055 |
28 |
Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) |
85-44-9 |
0.055 |
28 |
K024
Distillation bottoms from the production of phthalic anhydride from naphthalene.
Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) |
100-21-0 |
0.055 |
28 |
Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) |
85-44-9 |
0.055 |
28 |
K025
Distillation bottoms from the production of nitrobenzene by the nitration of benzene.
NA |
NA |
LLEXT fb SSTRP fb CARBN; or CMBST |
CMBST |
K026
Stripping still tails from the production of methyl ethyl pyridines.
NA |
NA |
CMBST |
CMBST |
K027
Centrifuge and distillation residues from toluene diisocyanate production.
NA |
NA |
CARBN; or CMBST |
CMBST |
K028
Spent catalyst from the hydrochlorinator reactor in the production of 1,1,1-trichloroethane.
1,1-Dichloroethane |
75-34-3 |
0.059 |
6.0 |
trans-1,2-Dichloroethylene |
156-60-5 |
0.054 |
30 |
Hexachlorobutadiene |
87-68-3 |
0.055 |
5.6 |
Hexachloroethane |
67-72-1 |
0.055 |
30 |
Pentachloroethane |
76-01-7 |
NA |
6.0 |
1,1,1,2-Tetrachloroethane |
630-20-6 |
0.057 |
6.0 |
1,1,2,2-Tetrachloroethane |
79-34-6 |
0.057 |
6.0 |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
1,1,1-Trichloroethane |
71-55-6 |
0.054 |
6.0 |
1,1,2-Trichloroethane |
79-00-5 |
0.054 |
6.0 |
Cadmium |
7440-43-9 |
0.69 |
NA |
Chromium(Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
K029
Waste from the product steam stripper in the production of 1,1,1-trichloroethane.
Chloroform |
67-66-3 |
0.046 |
6.0 |
1,2-Dichloroethane |
107-06-2 |
0.21 |
6.0 |
1,1-Dichloroethylene |
75-35-4 |
0.025 |
6.0 |
1,1,1-Trichloroethane |
71-55-6 |
0.054 |
6.0 |
Vinyl chloride |
75-01-4 |
0.27 |
6.0 |
K030
Column bodies or heavy ends from the combined production of trichloroethylene and perchloroethylene.
o-Dichlorobenzene |
95-50-1 |
0.088 |
NA |
p-Dichlorobenzene |
106-46-7 |
0.090 |
NA |
Hexachlorobutadiene |
87-68-3 |
0.055 |
5.6 |
Hexachloroethane |
67-72-1 |
0.055 |
30 |
Hexachloropropylene |
1888-71-7 |
NA |
30 |
Pentachlorobenzene |
608-93-5 |
NA |
10 |
Pentachloroethane |
76-01-7 |
NA |
6.0 |
1,2,4,5-Tetrachlorobenzene |
95-94-3 |
0.055 |
14 |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
1,2,4-Trichlorobenzene |
120-82-1 |
0.055 |
19 |
K031
By-product salts generated in the production of MSMA and cacodylic acid.
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
K032
Wastewater treatment sludge from the production of chlordane.
Hexachlorocyclopentadiene |
77-47-4 |
0.057 |
2.4 |
Chlordane ( a and g isomers) |
57-74-9 |
0.0033 |
0.26 |
Heptachlor |
76-44-8 |
0.0012 |
0.066 |
Heptachlor epoxide |
1024-57-3 |
0.016 |
0.066 |
K033
Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane.
Hexachlorocyclopentadiene |
77-47-4 |
0.057 |
2.4 |
K034
Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.
Hexachlorocyclopentadiene |
77-47-4 |
0.057 |
2.4 |
K035
Wastewater treatment sludges generated in the production of creosote.
Acenaphthene |
83-32-9 |
NA |
3.4 |
Anthracene |
120-12-7 |
NA |
3.4 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
o-Cresol |
95-48-7 |
0.11 |
5.6 |
m-Cresol (difficult to distinguish from p-cresol) |
108-39-4 |
0.77 |
5.6 |
p-Cresol (difficult to distinguish from m-cresol) |
106-44-5 |
0.77 |
5.6 |
Dibenz(a,h)anthracene |
53-70-3 |
NA |
8.2 |
Fluoranthene |
206-44-0 |
0.068 |
3.4 |
Fluorene |
86-73-7 |
NA |
3.4 |
Indeno(1,2,3-cd)pyrene |
193-39-5 |
NA |
3.4 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
K036
Still bottoms from toluene reclamation distillaiton in the production of disulfoton.
Disulfoton |
298-04-4 |
0.017 |
6.2 |
K037
Wastewater treatment sludges from the production of disulfoton.
Disulfoton |
298-04-4 |
0.017 |
6.2 |
Toluene |
108-88-3 |
0.080 |
10 |
K038
Wastewater from the washing and stripping of phorate production.
Phorate |
298-02-2 |
0.021 |
4.6 |
K039
Filter cake from the filtration of diethylphosphorodithioic acid in the production of phorate.
NA |
NA |
CARBN; or CMBST |
CMBST |
K040
Wastewater treatment sludge from the production of phorate.
Phorate |
298-02-2 |
0.021 |
4.6 |
K041
Wastewater treatment sludge from the production of toxaphene.
Toxaphene |
8001-35-2 |
0.0095 |
2.6 |
K042
Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5-T.
o-Dichlorobenzene |
95-50-1 |
0.088 |
6.0 |
p-Dichlorobenzene |
106-46-7 |
0.090 |
6.0 |
Pentachlorobenzene |
608-93-5 |
0.055 |
10 |
1,2,4,5-Tetrachlorobenzene |
95-94-3 |
0.055 |
14 |
1,2,4-Trichlorobenzene |
120-82-1 |
0.055 |
19 |
K043
2,6-Dichlorophenol waste from the production of 2,4-D.
2,4-Dichlorophenol |
120-83-2 |
0.044 |
14 |
2,6-Dichlorophenol |
187-65-0 |
0.044 |
14 |
2,4,5-Trichlorophenol |
95-95-4 |
0.18 |
7.4 |
2,4,6-Trichlorophenol |
88-06-2 |
0.035 |
7.4 |
2,3,4,6-Tetrachlorophenol |
58-90-2 |
0.030 |
7.4 |
Pentachlorophenol |
87-86-5 |
0.089 |
7.4 |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
HxCDDs (All Hexachlorodibenzo-p-dioxins) |
NA |
0.000063 |
0.001 |
HxCDFs (All Hexachlorodibenzofurans) |
55684-94-1 |
0.000063 |
0.001 |
PeCDDs (All Pentachlorodibenzo-p-dioxins) |
36088-22-9 |
0.000063 |
0.001 |
PeCDFs (All Pentachlorodibenzofurans) |
30402-15-4 |
0.000035 |
0.001 |
TCDDs (All Tetrachlorodibenzo-p-dioxins) |
41903-57-5 |
0.000063 |
0.001 |
TCDFs (All Tetrachlorodibenzofurans) |
55722-27-5 |
0.000063 |
0.001 |
K044
Wastewater treatment sludges from the manufacturing and processing of explosives.
NA |
NA |
DEACT |
DEACT |
K045
Spent carbon from the treatment of wastewater containing explosives.
NA |
NA |
DEACT |
DEACT |
K046
Wastewater treatment sludges from the manufacturing, formulation and loading of lead-based initiating compounds.
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
K047
Pink or red water from TNT operations.
NA |
NA |
DEACT |
DEACT |
K048
Dissolved air flotation (DAF) float from the petroleum refining industry.
Benzene |
71-43-2 |
0.14 |
10 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
bis(2-Ethylhexyl) phthalate |
117-81-7 |
0.28 |
28 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Di-n-butyl phthalate |
84-74-2 |
0.057 |
28 |
Ethylbenzene |
100-41-4 |
0.057 |
10 |
Fluorene |
86-73-7 |
0.059 |
NA |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Toluene |
108-88-33 |
0.080 |
10 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Lead |
7439-92-1 |
0.69 |
NA |
Nickel |
7440-02-0 |
NA |
11 mg/l TCLP |
K049
Slop oil emulsion solids from the petroleum refining industry.
Anthracene |
120-12-7 |
0.059 |
3.4 |
Benzene |
71-43-2 |
0.14 |
10 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
bis(2-Ethylhexyl) phthalate |
117-81-7 |
0.28 |
28 |
Carbon disulfide |
75-15-0 |
3.8 |
NA |
Chrysene |
2218-01-9 |
0.059 |
3.4 |
2,4-Dimethylphenol |
105-67-9 |
0.036 |
NA |
Ethylbenzene |
100-41-4 |
0.057 |
10 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Toluene |
108-88-3 |
0.080 |
10 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
NA |
Nickel |
7440-02-0 |
NA |
11 mg/l TCLP |
K050
Heat exchanger bundle cleaning sludge from the petroleum refining industry.
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
NA |
Nickel |
7440-02-0 |
NA |
11 mg/l TCLP |
K051
API separator sludge from the petroleum refining industry.
Acenaphthene |
83-32-9 |
0.059 |
NA |
Anthracene |
120-12-7 |
0.059 |
3.4 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzene |
71-43-2 |
0.14 |
10 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
bis(2-Ethylhexyl) phthalate |
117-81-7 |
0.28 |
28 |
Chrysene |
2218-01-9 |
0.059 |
3.4 |
Di-n-butyl phthalate |
105-67-9 |
0.057 |
28 |
Ethylbenzene |
100-41-4 |
0.057 |
10 |
Fluorene |
86-73-7 |
0.059 |
NA |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Toluene |
108-88-3 |
0.08 |
10 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
NA |
Nickel |
7440-02-0 |
NA |
11 mg/l TCLP |
K052
Tank bottoms (leaded) from the petroleum refining industry.
Benzene |
71-43-2 |
0.14 |
10 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
o-Cresol |
95-48-7 |
0.11 |
5.6 |
m-Cresol (difficult to distinguish from p-cresol) |
108-39-4 |
0.77 |
5.6 |
p-Cresol (difficult to distinguish from m-cresol) |
106-44-5 |
0.77 |
5.6 |
2,4-Dimethylphenol |
105-67-9 |
0.036 |
NA |
Ethylbenzene |
100-41-4 |
0.057 |
10 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Toluene |
108-88-3 |
0.08 |
10 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Lead |
7439-92-1 |
0.69 |
NA |
Nickel |
7440-02-0 |
NA |
11 mg/l TCLP |
K060
Ammonia still lime sludge from coking operations.
Benzene |
71-43-2 |
0.14 |
10 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
K061
Emission control dust or sludge from the primary production of steel in electric furnaces.
Antimony |
7440-36-0 |
NA |
1.15 mg/l TCLP |
Arsenic |
7440-38-2 |
NA |
5.0 mg/l TCLP |
Barium |
7440-39-3 |
NA |
21 mg/l TCLP |
Beryllium |
7440-41-7 |
NA |
1.22 mg/l TCLP |
Cadmium |
7440-43-9 |
0.69 |
0.11 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Mercury |
7439-97-6 |
NA |
0.025 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
Selenium |
7782-49-2 |
NA |
5.7 mg/l TCLP |
Silver |
7440-22-4 |
NA |
0.14 mg/l TCLP |
Thallium |
7440-28-0 |
NA |
0.20 mg/l TCLP |
Zinc |
7440-66-6 |
NA |
4.3 mg/l TCLP |
K062
Spent pickle liquor generated by steel finishing operations of facilities within the iron and steel industry (SIC Codes 331 and 332).
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
NA |
K069
Emission control dust or sludge from secondary lead smelting. - Calcium sulfate (Low Lead) Subcategory.
Cadmium |
7440-43-9 |
0.69 |
0.11 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
K069
Emission control dust or sludge from secondary lead smelting. - Non-Calcium sulfate (High Lead) Subcategory.
NA |
NA |
NA |
RLEAD |
K071
K071 (Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used) nonwastewaters that are residues from RMERC.
Mercury |
7439-97-6 |
NA |
0.20 mg/l TCLP |
K071
K071 (Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used) nonwastewaters that are not residues from RMERC.
Mercury |
7439-97-6 |
NA |
0.025 mg/l TCLP |
K071
All K071 wastewaters.
Mercury |
7439-97-6 |
0.15 |
NA |
K073
Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production.
Carbon tetrachloride |
56-23-5 |
0.057 |
6.0 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
Hexachloroethane |
67-72-1 |
0.055 |
30 |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
1,1,1-Trichloroethane |
71-55-6 |
0.054 |
6.0 |
K083
Distillation bottoms from aniline production.
Aniline |
62-53-3 |
0.81 |
14 |
Benzene |
71-43-2 |
0.14 |
10 |
Cyclohexanone |
108-94-1 |
0.36 |
NA |
Diphenylamine (difficult to distinguish from diphenylnitrosamine) |
122-39-4 |
0.92 |
13 |
Diphenylnitrosamine (difficult to distinguish from diphenylamine) |
86-30-6 |
0.92 |
13 |
Nitrobenzene |
98-95-3 |
0.068 |
14 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
K084
Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
K085
Distillation or fractionation column bottoms from the production of chlorobenzenes.
Benzene |
71-43-2 |
0.14 |
10 |
Chlorobenzene |
108-90-7 |
0.057 |
6.0 |
m-Dichlorobenzene |
541-73-1 |
0.036 |
6.0 |
o-Dichlorobenzene |
95-50-1 |
0.088 |
6.0 |
p-Dichlorobenzene |
106-46-7 |
0.090 |
6.0 |
Hexachlorobenzene |
118-74-1 |
0.055 |
10 |
Total PCBs (sum of all PCB isomers, or all Aroclors) |
1336-36-3 |
0.10 |
10 |
Pentachlorobenzene |
608-93-5 |
0.055 |
10 |
1,2,4,5-Tetrachlorobenzene |
95-94-3 |
0.055 |
14 |
1,2,4-Trichlorobenzene |
120-82-1 |
0.055 |
19 |
K086
Solvent wastes and sludges, caustic washes and sludges, or water washes and sludges from cleaning tubs and equipment used in the formulation of ink from pigments, driers, soaps, and stabilizers containing chromium and lead.
Acetone |
67-64-1 |
0.28 |
160 |
Acetophenone |
96-86-2 |
0.010 |
9.7 |
bis(2-Ethylhexyl) phthalate |
117-81-7 |
0.28 |
28 |
n-Butyl alcohol |
71-36-3 |
5.6 |
2.6 |
Butylbenzyl phthalate |
85-68-7 |
0.017 |
28 |
Cyclohexanone |
108-94-1 |
0.36 |
NA |
o-Dichlorobenzene |
95-50-1 |
0.088 |
6.0 |
Diethyl phthalate |
84-66-2 |
0.20 |
28 |
Dimethyl phthalate |
131-11-3 |
0.047 |
28 |
Di-n-butyl phthalate |
84-74-2 |
0.057 |
28 |
Di-n-octyl phthalate |
117-84-0 |
0.017 |
28 |
Ethyl acetate |
141-78-6 |
0.34 |
33 |
Ethylbenzene |
100-41-4 |
0.057 |
10 |
Methanol |
67-56-1 |
5.6 |
NA |
Methyl ethyl ketone |
78-93-3 |
0.28 |
36 |
Methyl isobutyl ketone |
108-10-1 |
0.14 |
33 |
Methylene chloride |
75-09-2 |
0.089 |
30 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Nitrobenzene |
98-95-3 |
0.068 |
14 |
Toluene |
108-88-3 |
0.080 |
10 |
1,1,1-Trichloroethane |
71-55-6 |
0.054 |
6.0 |
Trichloroethylene |
79-01-6 |
0.054 |
6.0 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
K087
Decanter tank tar sludge from coking operations.
Acenaphthylene |
208-96-8 |
0.059 |
3.4 |
Benzene |
71-43-2 |
0.14 |
10 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Fluoranthene |
206-44-0 |
0.068 |
3.4 |
Indeno(1,2,3-cd)pyrene |
193-39-5 |
0.0055 |
3.4 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Toluene |
108-88-3 |
0.080 |
10 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
K088
Spent potliners from primary aluminum reduction.
Acenaphthene |
83-32-9 |
0.059 |
3.4 |
Anthracene |
120-12-7 |
0.059 |
3.4 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Benzo(b)fluoranthene |
205-99-2 |
0.11 |
6.8 |
Benzo(k)fluoranthene |
207-08-9 |
0.11 |
6.8 |
Benzo(g,h,i)perylene |
191-24-2 |
0.0055 |
1.8 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Dibenz(a,h)anthracene |
53-70-3 |
0.055 |
8.2 |
Fluoranthene |
206-44-0 |
0.068 |
3.4 |
Indeno(1,2,3-c,d)pyrene |
193-39-5 |
0.0055 |
3.4 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Antimony |
7440-36-0 |
1.9 |
1.15 mg/l TCLP |
Arsenic |
7440-38-2 |
1.4 |
26.1 mg/l |
Barium |
7440-39-3 |
1.2 |
21 mg/l TCLP |
Beryllium |
7440-41-7 |
0.82 |
1.22 mg/l TCLP |
Cadmium |
7440-43-9 |
0.69 |
0.11 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Mercury |
7439-97-6 |
0.15 |
0.025 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
Selenium |
7782-49-2 |
0.82 |
5.7 mg/l TCLP |
Silver |
7440-22-4 |
0.43 |
0.14 mg/l TCLP |
Cyanide (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanide (Amenable)7 |
57-12-5 |
0.86 |
30 |
Fluoride |
16984-48-8 |
35 |
NA |
K093
Distillation light ends from the production of phthalic anhydride from ortho-xylene.
Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) |
100-21-0 |
0.055 |
28 |
Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) |
85-44-9 |
0.055 |
28 |
K094
Distillation bottoms from the production of phthalic anhydride from ortho-xylene.
Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) |
100-21-0 |
0.055 |
28 |
Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) |
85-44-9 |
0.055 |
28 |
K095
Distillation bottoms from the production of 1,1,1-trichloroethane.
Hexachloroethane |
67-72-1 |
0.055 |
30 |
Pentachloroethane |
76-01-7 |
0.055 |
6.0 |
1,1,1,2-Tetrachloroethane |
630-20-6 |
0.057 |
6.0 |
1,1,2,2-Tetrachloroethane |
79-34-6 |
0.057 |
6.0 |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
1,1,2-Trichloroethane |
79-00-5 |
0.054 |
6.0 |
Trichloroethylene |
79-01-6 |
0.054 |
6.0 |
K096
Heavy ends from the heavy ends column from the production of 1,1,1-trichloroethane.
m-Dichlorobenzene |
541-73-1 |
0.036 |
6.0 |
Pentachloroethane |
76-01-7 |
0.055 |
6.0 |
1,1,1,2-Tetrachloroethane |
630-20-6 |
0.057 |
6.0 |
1,1,2,2-Tetrachloroethane |
79-34-6 |
0.057 |
6.0 |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
1,2,4-Trichlorobenzene |
120-82-1 |
0.055 |
19 |
1,1,2-Trichloroethane |
79-00-5 |
0.054 |
6.0 |
Trichloroethylene |
79-01-6 |
0.054 |
6.0 |
K097
Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.
Chlordane ( a and c isomers) |
57-74-9 |
0.0033 |
0.26 |
Heptachlor |
76-44-8 |
0.0012 |
0.066 |
Heptachlor epoxide |
1024-57-3 |
0.016 |
0.066 |
Hexachlorocyclopentadiene |
77-47-4 |
0.057 |
2.4 |
K098
Untreated process wastewater from the production of toxaphene.
Toxaphene |
8001-35-2 |
0.0095 |
2.6 |
K099
Untreated wastewater from the production of 2,4-D.
2,4-Dichlorophenoxyacetic acid |
94-75-7 |
0.72 |
10 |
HxCDDs (All Hexachlorodibenzo-p-dioxins) |
NA |
0.000063 |
0.001 |
HxCDFs (All Hexachlorodibenzofurans) |
55684-94-1 |
0.000063 |
0.001 |
PeCDDs (All Pentachlorodibenzo-p-dioxins) |
36088-22-9 |
0.000063 |
0.001 |
PeCDFs (All Pentachlorodibenzofurans) |
30402-15-4 |
0.000035 |
0.001 |
TCDDs (All Tetrachlorodibenzo-p-dioxins) |
41903-57-5 |
0.000063 |
0.001 |
TCDFs (All Tetrachlorodibenzofurans) |
55722-27-5 |
0.000063 |
0.001 |
K100
Waste leaching solution from acid leaching of emission control dust or sludge from secondary lead smelting.
Cadmium |
7440-43-9 |
0.69 |
0.11 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
K101
Distillation tar residues from the distillation of aniline-based compounds in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.
o-Nitroaniline |
88-74-4 |
0.27 |
14 |
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
Cadmium |
7440-43-9 |
0.69 |
NA |
Lead |
7439-92-1 |
0.69 |
NA |
Mercury |
7439-97-6 |
0.15 |
NA |
K102
Residue from the use of activated carbon for decolorization in the production of veterinary pharmaceuticals from arsenic or organo-arsenic compounds.
o-Nitrophenol |
88-75-5 |
0.028 |
13 |
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
Cadmium |
7440-43-9 |
0.69 |
NA |
Lead |
7439-92-1 |
0.69 |
NA |
Mercury |
7439-97-6 |
0.15 |
NA |
K103
Process residues from aniline extraction from the production of aniline.
Aniline |
62-53-3 |
0.81 |
14 |
Benzene |
71-43-2 |
0.14 |
10 |
2,4-Dinitrophenol |
51-28-5 |
0.12 |
160 |
Nitrobenzene |
98-95-3 |
0.068 |
14 |
Phenol |
108-95-2 |
0.039 |
6.2 |
K104
Combined wastewater streams generated from nitrobenzene or aniline production.
Aniline |
62-53-3 |
0.81 |
14 |
Benzene |
71-43-2 |
0.14 |
10 |
2,4-Dinitrophenol |
51-28-5 |
0.12 |
160 |
Nitrobenzene |
98-95-3 |
0.068 |
14 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
K105
Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes.
Benzene |
71-43-2 |
0.14 |
10 |
Chlorobenzene |
108-90-7 |
0.057 |
6.0 |
2-Chlorophenol |
95-57-8 |
0.044 |
5.7 |
o-Dichlorobenzene |
95-50-1 |
0.088 |
6.0 |
p-Dichlorobenzene |
106-46-7 |
0.090 |
6.0 |
Phenol |
108-95-2 |
0.039 |
6.2 |
2,4,5-Trichlorophenol |
95-95-4 |
0.18 |
7.4 |
2,4,6-Trichlorophenol |
88-06-2 |
0.035 |
7.4 |
K106
K106 (wastewater treatment sludge from the mercury cell process in chlorine production) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.
Mercury |
7439-97-6 |
NA |
RMERC |
K106
K106 (wastewater treatment sludge from the mercury cell process in chlorine production) nonwastewaters that contain less than 260 mg/kg total mercury that are residues from RMERC.
Mercury |
7439-97-6 |
NA |
0.20 mg/l TCLP |
K106
Other K106 nonwastewaters that contain less than 260 mg/kg total mercury and are not residues from RMERC.
Mercury |
7439-97-6 |
NA |
0.025 mg/l TCLP |
K106
All K106 wastewaters.
Mercury |
7439-97-6 |
0.15 |
NA |
K107
Column bottoms from product separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
NA |
NA |
CMBST; or CHOXD fb CARBN; or BIODG fb CARBN |
CMBST |
K108
Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
NA |
NA |
CMBST; or CHOXD fb CARBN; or BIODG fb CARBN |
CMBST |
K109
Spent filter cartridges from product purification from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
NA |
NA |
CMBST; or CHOXD fb CARBN; or BIODG fb CARBN |
CMBST |
K110
Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
NA |
NA |
CMBST; or CHOXD fb CARBN; or BIODG fb CARBN |
CMBST |
K111
Product washwaters from the production of dinitrotoluene via nitration of toluene.
2,4-Dinitrotoluene |
121-1-1 |
0.32 |
140 |
2,6-Dinitrotoluene |
606-20-2 |
0.55 |
28 |
K112
Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene.
NA |
NA |
CMBST; or CHOXD fb CARBN; or BIODG fb CARBN |
CMBST |
K113
Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.
NA |
NA |
CARBN; or CMBST |
CMBST |
K114
Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.
NA |
NA |
CARBN; or CMBST |
CMBST |
K115
Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
NA |
NA |
CARBN; or CMBST |
CMBST |
K116
Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine.
NA |
NA |
CARBN; or CMBST |
CMBST |
K117
Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene.
Methyl bromide (Bromomethane) |
74-83-9 |
0.11 |
15 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
Ethylene dibromide (1,2-Dibromoethane) |
106-93-4 |
0.028 |
15 |
K118
Spent absorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.
Methyl bromide (Bromomethane) |
74-83-9 |
0.11 |
15 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
Ethylene dibromide (1,2-Dibromoethane) |
106-93-4 |
0.028 |
15 |
K123
Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salts.
NA |
NA |
CMBST; or CHOXD fb (BIODG or CARBN) |
CMBST |
K124
Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.
NA |
NA |
CMBST; or CHOXD fb (BIODG or CARBN) |
CMBST |
K125
Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts.
NA |
NA |
CMBST; or CHOXD fb (BIODG or CARBN) |
CMBST |
K126
Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts.
NA |
NA |
CMBST; or CHOXD fb (BIODG or CARBN) |
CMBST |
K131
Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide.
Methyl bromide (Bromomethane) |
74-83-9 |
0.11 |
15 |
K132
Spent absorbent and wastewater separator solids from the production of methyl bromide.
Methyl bromide (Bromomethane) |
74-83-9 |
0.11 |
15 |
K136
Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.
Methyl bromide (Bromomethane) |
74-83-9 |
0.11 |
15 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
Ethylene dibromide (1,2-Dibromoethane) |
106-93-4 |
0.028 |
15 |
K141
Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the production of coke or the recovery of coke by-products produced from coal. This listing does not include K087 (decanter tank tar sludge from coking operations).
Benzene |
71-43-2 |
0.14 |
10 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(a)pyrene |
50-2-8 |
0.061 |
3.4 |
Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) |
205-99-2 |
0.11 |
6.8 |
Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) |
207-08-9 |
0.11 |
6.8 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Dibenz(a,h)anthracene |
53-70-3 |
0.055 |
8.2 |
Indeno(1,2,3-cd)pyrene |
193-39-5 |
0.0055 |
3.4 |
K142
Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal.
Benzene |
71-43-2 |
0.14 |
10 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) |
205-99-2 |
0.11 |
6.8 |
Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) |
207-08-9 |
0.11 |
6.8 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Dibenz(a,h)anthracene |
53-70-3 |
0.055 |
8.2 |
Indeno(1,2,3-cd)pyrene |
193-39-5 |
0.0055 |
3.4 |
K143
Process residues from the recovery of light oil, including, but not limited to, those generated in stills, decanters, and wash oil recovery units from the recovery of coke by-products produced from coal.
Benzene |
71-43-2 |
0.14 |
10 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) |
205-99-2 |
0.11 |
6.8 |
Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) |
207-08-9 |
0.11 |
6.8 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
K144
Wastewater sump residues from light oil refining, including, but not limited to, intercepting or contamination sump sludges from the recovery of coke by-products produced from coal.
Benzene |
71-43-2 |
0.14 |
10 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) |
205-99-2 |
0.11 |
6.8 |
Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) |
207-08-9 |
0.11 |
6.8 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Dibenz(a,h)anthracene |
53-70-3 |
0.055 |
8.2 |
K145
Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal.
Benzene |
71-43-2 |
0.14 |
10 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Dibenz(a,h)anthracene |
53-70-3 |
0.055 |
8.2 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
K147
Tar storage tank residues from coal tar refining.
Benzene |
71-43-2 |
0.14 |
10 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) |
205-99-2 |
0.11 |
6.8 |
Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) |
207-08-9 |
0.11 |
6.8 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Dibenz(a,h)anthracene |
53-70-3 |
0.055 |
8.2 |
Indeno(1,2,3-cd)pyrene |
193-39-5 |
0.0055 |
3.4 |
K148
Residues from coal tar distillation, including, but not limited to, still bottoms.
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) |
205-99-2 |
0.11 |
6.8 |
Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) |
207-08-9 |
0.11 |
6.8 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Dibenz(a,h)anthracene |
53-70-3 |
0.055 |
8.2 |
Indeno(1,2,3-cd)pyrene |
193-39-5 |
0.0055 |
3.4 |
K149
Distillation bottoms from the production of a - (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. (This waste does not include still bottoms from the distillations of benzyl chloride.)
Chlorobenzene |
108-90-7 |
0.057 |
6.0 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
Chloromethane |
74-87-3 |
0.19 |
30 |
p-Dichlorobenzene |
106-46-7 |
0.090 |
6.0 |
Hexachlorobenzene |
118-74-1 |
0.055 |
10 |
Pentachlorobenzene |
608-93-5 |
0.055 |
10 |
1,2,4,5-Tetrachlorobenzene |
95-94-3 |
0.055 |
14 |
Toluene |
108-88-3 |
0.080 |
10 |
K150
Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydrochloric acid recovery processes associated with the production of a - (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.
Carbon tetrachloride |
56-23-5 |
0.057 |
6.0 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
Chloromethane |
74-87-3 |
0.19 |
30 |
p-Dichlorobenzene |
106-46-7 |
0.090 |
6.0 |
Hexachlorobenzene |
118-74-1 |
0.055 |
10 |
Pentachlorobenzene |
608-93-5 |
0.055 |
10 |
1,2,4,5-Tetrachlorobenzene |
95-94-3 |
0.055 |
14 |
1,1,2,2- Tetrachloroethane |
79-34-5 |
0.057 |
6.0 |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
1,2,4-Trichlorobenzene |
120-82-1 |
0.055 |
19 |
K151
Wastewater treatment sludges, excluding neutralization and biological sludges, generated during the treatment of wastewaters from the production of a - (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.
Benzene |
71-43-2 |
0.14 |
10 |
Carbon tetrachloride |
56-23-5 |
0.057 |
6.0 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
Hexachlorobenzene |
118-74-1 |
0.055 |
10 |
Pentachlorobenzene |
608-93-5 |
0.055 |
10 |
1,2,4,5-Tetrachlorobenzene |
95-94-3 |
0.055 |
14 |
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
Toluene |
108-88-3 |
0.080 |
10 |
K156
Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes.10
Acetonitrile |
75-05-8 |
5.6 |
1.8 |
Acetophenone |
96-86-2 |
0.010 |
9.7 |
Aniline |
62-53-3 |
0.81 |
14 |
Benomyl |
17804-35-2 |
0.056 |
1.4 |
Benzene |
71-43-2 |
0.14 |
10 |
Carbaryl |
63-25-21 |
0.006 |
0.14 |
Carbenzadim |
10605-21-7 |
0.056 |
1.4 |
Carbofuran |
1563-66-2 |
0.006 |
0.14 |
Carbosulfan |
55285-14-8 |
0.028 |
1.4 |
Chlorobenzene |
108-90-7 |
0.057 |
6.0 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
o-Dichlorobenzene |
95-50-1 |
0.088 |
6.0 |
Methomyl |
16752-77-5 |
0.028 |
0.14 |
Methylene chloride |
75-09-2 |
0.089 |
30 |
Methyl ethyl ketone |
78-93-3 |
0.28 |
36 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenol |
108-95-2 |
0.039 |
6.2 |
Pyridine |
110-86-1 |
0.014 |
16 |
Toluene |
108-88-3 |
0.080 |
10 |
Triethylamine |
121-44-8 |
0.081 |
1.5 |
K157
Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes.
Carbon tetrachloride |
56-23-5 |
0.057 |
6.0 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
Chloromethane |
74-87-3 |
0.19 |
30 |
Methomyl |
16752-77-5 |
0.028 |
0.14 |
Methylene chloride |
75-09-2 |
0.089 |
30 |
Methyl ethyl ketone |
78-93-3 |
0.28 |
36 |
Pyridine |
110-86-1 |
0.014 |
16 |
Triethylamine |
121-44-8 |
0.081 |
1.5 |
K158
Baghouse dusts and filter/separation solids from the production of carbamates and carbamoyl oximes.
Benomyl |
17804-35-2 |
0.056 |
1.4 |
Benzene |
71-43-2 |
0.14 |
10 |
Carbenzadim |
10605-21-7 |
0.056 |
1.4 |
Carbofuran |
1563-66-2 |
0.006 |
0.14 |
Carbosulfan |
55285-14-8 |
0.028 |
1.4 |
Chloroform |
67-66-3 |
0.046 |
6.0 |
Methylene chloride |
75-09-2 |
0.089 |
30 |
Phenol |
108-95-2 |
0.039 |
6.2 |
K159
Organics from the treatment of thiocarbamate wastes.10
Benzene |
71-43-2 |
0.14 |
10 |
Butylate |
2008-41-5 |
0.042 |
1.4 |
EPTC (Eptam) |
759-94-4 |
0.042 |
1.4 |
Molinate |
2212-67-1 |
0.042 |
1.4 |
Pebulate |
1114-71-2 |
0.042 |
1.4 |
Vernolate |
1929-77-7 |
0.042 |
1.4 |
K161
Purification solids (including filtration, evaporation, and centrifugation solids), baghouse dust and floor sweepings from the production of dithiocarbamate acids and their salts.
Antimony |
7440-36-0 |
1.9 |
1.1511 |
Arsenic |
7440-38-2 |
1.4 |
5.011 |
Carbon disulfide |
75-15-0 |
3.8 |
4.811 |
Dithiocarbamates (total) |
137-30-4 |
0.028 |
28 |
Lead |
7439-92-1 |
0.69 |
0.7511 |
Nickel |
7440-02-0 |
3.98 |
1111 |
Selenium |
7782-49-2 |
0.82 |
5.711 |
K169
Crude oil tank sediment from petroleum refining operations.
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzene |
71-43-2 |
0.14 |
10 |
Benzo(g,h,i)perylene |
191-24-2 |
0.0055 |
1.8 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Ethyl benzene |
100-41-4 |
0.057 |
10 |
Fluorene |
86-73-7 |
0.059 |
3.4 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
81-05-8 |
0.059 |
5.6 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Toluene (Methyl Benzene) |
108-88-3 |
0.080 |
10 |
Xylenes (Total) |
1330-20-7 |
0.32 |
30 |
K170
Clarified slurry oil sediment from petroleum refining operations.
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzene |
71-43-2 |
0.14 |
10 |
Benzo(g,h,i)perylene |
191-24-2 |
0.0055 |
1.8 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Dibenz(a,h)anthracene |
53-70-3 |
0.055 |
8.2 |
Ethyl benzene |
100-41-4 |
0.057 |
10 |
Fluorene |
86-73-7 |
0.059 |
3.4 |
Indeno(1,2,3,-cd)pyrene |
193-39-5 |
0.0055 |
3.4 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
81-05-8 |
0.059 |
5.6 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Toluene (Methyl Benzene) |
108-88-3 |
0.080 |
10 |
Xylenes (Total |
1330-20-7 |
0.32 |
30 |
K171
Spent hydrotreating catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors. (This listing does not include inert support media.)
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzene |
71-43-2 |
0.14 |
10 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
Ethyl benzene |
100-41-4 |
0.057 |
10 |
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Phenanthrene |
81-05-8 |
0.059 |
5.6 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Toluene (Methyl Benzene) |
108-88-3 |
0.080 |
10 |
Xylenes (Total) |
1330-20-7 |
0.32 |
30 |
Arsenic |
7740-38-2 |
1.4 |
5 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11.0 mg/l TCLP |
Vanadium |
7440-62-2 |
4.3 |
1.6 mg/l TCLP |
Reactive sulfides |
NA |
DEACT |
DEACT |
K172
Spent hydrorefining catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors. (This listing does not include inert support media.)
Benzene |
71-43-2 |
0.14 |
10 |
Ethyl benzene |
100-41-4 |
0.057 |
10 |
Toluene (Methyl Benzene) |
108-88-3 |
0.080 |
10 |
Xylenes (Total) |
1330-20-7 |
0.32 |
30 |
Antimony |
7740-36-0 |
1.9 |
1.15 mg/l TCLP |
Arsenic |
7740-38-2 |
1.4 |
5 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11.0 mg/l TCLP |
Vanadium |
7440-62-2 |
4.3 |
1.6 mg/l TCLP |
Reactive Sulfides |
NA |
DEACT |
DEACT |
K174
Wastewater treatment sludge from the production of ethylene dicholoride or vinyl choloride monomer.
1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD) |
35822-46-9 |
0.000035 or CMBST11 |
0.0025 or CMBST11 |
1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF) |
67562-39-4 |
0.000035 or CMBST11 |
0.0025 or CMBST11 |
1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF) |
55673-89-7 |
0.000035 or CMBST11 |
0.0025 or CMBST11 |
All hexachlorodibenzo-p-dioxins (HxCDDs) |
34465-46-8 |
0.000063 or CMBST11 |
0.001 or CMBST11 |
All hexachlorodibenzofurans (HxCDFs) |
55684-94-1 |
0.000063 or CMBST11 |
0.001 or CMBST11 |
1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (1,2,3,4,6,7,8,9-OCDD) |
3268-87-9 |
0.000063 or CMBST11 |
0.005 or CMBST11 |
1,2,3,4,6,7,8,9-Octachlorodibenzofuran (1,2,3,4,6,7,8,9-OCDF) |
39001-02-0 |
0.000063 or CMBST11 |
0.005 or CMBST11 |
All pentachlorodibenzo-p-dioxins (PeCDDs) |
36088-22-9 |
0.000063 or CMBST11 |
0.001 or CMBST11 |
All pentachlorodibenzofurans (PeCDFs) |
30402-15-4 |
0.000035 or CMBST11 |
0.001 or CMBST11 |
All tetrachlorodibenzo-p-dioxins (TCDDs) |
41903-57-5 |
0.000063 or CMBST11 |
0.001 or CMBST11 |
All tetrachlorodibenzofurans (TCDFs) |
55722-27-5 |
0.000063 or CMBST11 |
0.001 or CMBST11 |
Arsenic |
7440-36-0 |
1.4 |
5.0 mg/L TCLP |
K175
Wastewater treatment sludge from the production of vinyl choloride monomer using mercuric chloride catalyst in an acetylene-based process.
Mercury12 |
7439-97-6 |
NA |
0.025 mg/L TCLP |
PH12 |
NA |
pH £ 6.0 |
K175
All K175 wastewaters.
Mercury |
7439-97-6 |
0.15 |
NA |
K176
Baghouse filters from the production of antimony oxide, including filters from the production of intermediates e.g., antimony metal or crude antimony oxide).
Antimony |
7440-36-0 |
1.9 |
1.15 mg/L TCLP |
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/L TCLP |
Cadmium |
7440-43-9 |
0.69 |
0.11 mg/L TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/L TCLP |
Mercury |
7439-97-6 |
0.15 |
0.025 mg/L TCLP |
K177
Slag from the production of antimony oxide that is speculatively accumulated or disposed, including slag from the production of intermediates (e.g., antimony metal or crude antimony oxide).
Antimony |
7440-36-0 |
1.9 |
1.15 mg/L TCLP |
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/L TCLP |
Lead |
7439-92-1 |
0.69 |
0.75 mg/L TCLP |
K178
Residues from manufacturing and manufacturing-site storage of ferric chloride from acids formed during the production of titanium dioxide using the chloride-ilmenite process.
1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD) |
35822-46-9 |
0.000035 or CMBST11 |
0.0025 or CMBST11 |
1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF) |
67562-39-4 |
0.000035 or CMBST11 |
0.0025 or CMBST11 |
1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF) |
55673-89-7 |
0.000035 or CMBST11 |
0.0025 or CMBST11 |
HxCDDs (All Hexachlorodibenzo-p-dioxins) |
34465-46-8 |
0.000063 or CMBST11 |
0.001 or CMBST11 |
HxCDFs (All Hexachlorodibenzofurans) |
55684-94-1 |
0.000063 or CMBST11 |
0.001 or CMBST11 |
1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin (1,2,3,4,6,7,8,9-OCDD) |
3268-87-9 |
0.000063 or CMBST11 |
0.005 or CMBST11 |
1,2,3,4,6,7,8,9-Octachlorodibenzofuran (OCDF) |
39001-02-0 |
0.000063 or CMBST11 |
0.005 or CMBST11 |
PeCDDs (All Pentachlorodibenzo-p-dioxins) |
36088-22-9 |
0.000063 or CMBST11 |
0.001 or CMBST11 |
PeCDFs (All Pentachlorodibenzofurans) |
30402-15-4 |
0.000035 or CMBST11 |
0.001 or CMBST11 |
TCDDs (All Tetrachlorodibenzo-p-dioxins) |
41903-57-5 |
0.000063 or CMBST11 |
0.001 or CMBST11 |
TCDFs (All Tetrachlorodibenzofurans) |
55722-27-5 |
0.000063 or CMBST11 |
0.001 or CMBST11 |
Thallium |
7440-28-0 |
1.4 |
0.20 mg/L TCLP |
P001
Warfarin, & salts, when present at concentrations greater than 0.3 percent.
Warfarin |
81-81-2 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P002
1-Acetyl-2-thiourea.
1-Acetyl-2-thiourea |
591-08-2 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P003
Acrolein.
Acrolein |
107-02-8 |
0.29 |
CMBST |
P004
Aldrin.
Aldrin |
309-00-2 |
0.021 |
0.066 |
P005
Allyl alcohol.
Allyl alcohol |
107-18-6 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P006
Aluminum phosphide.
Aluminum phosphide |
20859-73-8 |
CHOXD; CHRED; or CMBST |
CHOXD; CHRED; or CMBST |
P007
5-Aminomethyl-3-isoxazolol.
5-Aminomethyl-3-isoxazolol |
2763-96-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P008
4-Aminopyridine.
4-Aminopyridine |
504-24-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P009
Ammonium picrate.
Ammonium picrate |
131-74-8 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED; or CMBST |
P010
Arsenic acid.
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
P011
Arsenic pentoxide.
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
P012
Arsenic trioxide.
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
P013
Barium cyanide.
Barium |
7440-39-3 |
NA |
21 mg/l TCLP |
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
P014
Thiophenol (Benzene thiol).
Thiophenol (Benzene thiol) |
108-98-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P015
Beryllium dust.
Beryllium |
7440-41-7 |
RMETL;or RTHRM |
RMETL; or RTHRM |
P016
Dichloromethyl ether (Bis(chloromethyl)ether).
Dichloromethyl ether |
542-88-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P017
Bromoacetone.
Bromoacetone |
598-31-2 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P018
Brucine.
Brucine |
357-57-3 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P020
2-sec-Butyl-4,6-dinitrophenol (Dinoseb).
2-sec-Butyl-4,6-dinitrophenol (Dinoseb) |
88-85-7 |
0.066 |
2.5 |
P021
Calcium cyanide.
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
P022
Carbon disulfide.
Carbon disulfide |
75-15-0 |
3.8 |
CMBST |
Carbon disulfide; alternate6 standard for nonwastewaters only |
75-15-0 |
NA |
4.8 mg/l TCLP |
P023
Chloroacetaldehyde.
Chloroacetaldehyde |
107-20-0 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P024
p-Chloroaniline.
p-Chloroaniline |
106-47-8 |
0.46 |
16 |
P026
1-(o-Chlorophenyl)thiourea.
1-(o-Chlorophenyl)thiourea |
5344-82-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P027
3-Chloropropionitrile.
3-Chloropropionitrile |
542-76-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P028
Benzyl chloride.
Benzyl chloride |
100-44-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P029
Copper cyanide.
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
P030
Cyanides (soluble salts and complexes).
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
P031
Cyanogen.
Cyanogen |
460-19-5 |
CHOXD; WETOX; or CMBST |
CHOXD; WETOX; or CMBST |
P033
Cyanogen chloride.
Cyanogen chloride |
506-77-4 |
CHOXD; WETOX; or CMBST |
CHOXD; WETOX; or CMBST |
P034
2-Cyclohexyl-4,6-dinitrophenol.
2-Cyclohexyl-4,6-dinitrophenol |
131-89-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P036
Dichlorophenylarsine.
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
P037
Dieldrin.
Dieldrin |
60-57-1 |
0.017 |
0.13 |
P038
Diethylarsine.
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
P039
Disulfoton.
Disulfoton |
298-04-4 |
0.017 |
6.2 |
P040
O,O-Diethyl-O-pyrazinyl-phosphorothioate.
O,O-Diethyl-O-pyrazinylphosphorothioate |
297-97-2 |
CARBN; or CMBST |
CMBST |
P041
Diethyl-p-nitrophenyl phosphate.
Diethyl-p-nitrophenyl phosphate |
311-45-5 |
CARBN; or CMBST |
CMBST |
P042
Epinephrine.
Epinephrine |
51-43-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P043
Diisopropylfluorophosphate (DFP).
Diisopropylfluorophosphate (DFP) |
55-91-4 |
CARBN; or CMBST |
CMBST |
P044
Dimethoate.
Dimethoate |
60-51-5 |
CARBN; or CMBST |
CMBST |
P045
Thiofanox.
Thiofanox |
39196-18-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P046
a , a -Dimethylphenethylamine.
a , a -Dimethylphenethylamine |
122-09-8 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P047
4,6-Dinitro-o-cresol.
4,6-Dinitro-o-cresol |
543-52-1 |
0.28 |
160 |
P047
4,6-Dinitro-o-cresol salts.
NA |
NA |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P048
2,4-Dinitrophenol.
2,4-Dinitrophenol |
51-28-5 |
0.12 |
160 |
P049
Dithiobiuret.
Dithiobiuret |
541-53-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P050
Endosulfan.
Endosulfan I |
939-98-8 |
0.023 |
0.066 |
Endosulfan II |
33213-6-5 |
0.029 |
0.13 |
Endosulfan sulfate |
1031-07-8 |
0.029 |
0.13 |
P051
Endrin.
Endrin |
72-20-8 |
0.0028 |
0.13 |
Endrin aldehyde |
7421-93-4 |
0.025 |
0.13 |
P054
Aziridine.
Aziridine |
151-56-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P056
Fluorine.
Fluoride (measured in wastewaters only) |
16964-48-8 |
35 |
ADGAS fb NEUTR |
P057
Fluoroacetamide.
Fluoroacetamide |
640-19-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P058
Fluoroacetic acid, sodium salt.
Fluoroacetic acid, sodium salt |
62-74-8 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P059
Heptachlor.
Heptachlor |
76-44-8 |
0.0012 |
0.066 |
Heptachlor epoxide |
1024-57-3 |
0.016 |
0.066 |
P060
Isodrin.
Isodrin |
465-73-6 |
0.021 |
0.066 |
P062
Hexaethyl tetraphosphate.
Hexaethyl tetraphosphate |
757-58-4 |
CARBN; or CMBST |
CMBST |
P063
Hydrogen cyanide.
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
P064
Isocyanic acid, ethyl ester.
Isocyanic acid, ethyl ester |
624-83-9 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P065
P065 (mercury fulminate) nonwastewaters, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC.
Mercury |
7439-97-6 |
NA |
IMERC |
P065
P065 (mercury fulminate) nonwastewaters that are either incinerator residues or are residues from RMERC; and contain greater than or equal to 260 mg/kg total mercury.
Mercury |
7339-97-6 |
NA |
RMERC |
P065
P065 (mercury fulminate) nonwastewaters that are residues from RMERC and contain less than 260 mg/kg total mercury.
Mercury |
7439-97-6 |
NA |
0.20 mg/l TCLP |
P065
P065 (mercury fulminate) nonwastewaters that are incinerator residues and contain less than 260 mg/kg total mercury.
Mercury |
7439-97-6 |
NA |
0.025 mg/l TCLP |
P065
All P065 (mercury fulminate) wastewaters.
Mercury |
7439-97-6 |
0.15 |
NA |
P066
Methomyl.
Methomyl |
16752-77-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P067
2-Methyl-aziridine.
2-Methyl-aziridine |
75-55-8 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P068
Methyl hydrazine.
Methyl hydrazine |
60-34-4 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED, or CMBST |
P069
2-Methyllactonitrile.
2-Methyllactonitrile |
75-86-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P070
Aldicarb.
Aldicarb |
116-06-3 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P071
Methyl parathion.
Methyl parathion |
298-00-0 |
0.014 |
4.6 |
P072
1-Naphthyl-2-thiourea.
1-Naphthyl-2-thiourea |
86-88-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P073
Nickel carbonyl.
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
P074
Nickel cyanide.
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
P075
Nicotine and salts.
Nicotine and salts |
54-11-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P076
Nitric oxide.
Nitric oxide |
10102-43-9 |
ADGAS |
ADGAS |
P077
p-Nitroaniline.
p-Nitroaniline |
100-01-6 |
0.028 |
28 |
P078
Nitrogen dioxide.
Nitrogen dioxide |
10102-44-0 |
ADGAS |
ADGAS |
P081
Nitroglycerin.
Nitroglycerin |
55-63-0 |
CHOXD; CHRED; CARBN; BIODG or CMBST |
CHOXD; CHRED; or CMBST |
P082
N-Nitrosodimethylamine.
N-Nitrosodimethylamine |
62-75-9 |
0.40 |
2.3 |
P084
N-Nitrosomethylvinylamine.
N-Nitrosomethylvinylamine |
4549-40-0 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P085
Octamethylpyrophosphoramide.
Octamethylpyrophosphoramide |
152-16-9 |
CARBN; or CMBST |
CMBST |
P087
Osmium tetroxide.
Osmium tetroxide |
20816-12-0 |
RMETL; or RTHRM |
RMETL; or RTHRM |
P088
Endothall.
Endothall |
145-73-3 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P089
Parathion.
Parathion |
56-38-2 |
0.014 |
4.6 |
P092
P092 (phenyl mercuric acetate) nonwastewaters, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC.
Mercury |
7439-97-6 |
NA |
IMERC; or RMERC |
P092
P092 (phenyl mercuric acetate) nonwastewaters that are either incinerator residues or are residues from RMERC; and still contain greater than or equal to 260 mg/kg total mercury.
Mercury |
7439-97-6 |
NA |
RMERC |
P092
P092 (phenyl mercuric acetate) nonwastewaters that are residues from RMERC and contain less than 260 mg/kg total mercury.
Mercury |
7439-97-6 |
NA |
0.20 mg/l TCLP |
P092
P092 (phenyl mercuric acetate) nonwastewaters that are incinerator residues and contain less than 260 mg/kg total mercury.
Mercury |
7439-97-6 |
NA |
0.025 mg/l TCLP |
P092
All P092 (phenyl mercuric acetate) wastewaters.
Mercury |
7439-97-6 |
0.15 |
NA |
P093
Phenylthiourea.
Phenylthiourea |
103-85-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P094
Phorate.
Phorate |
298-02-2 |
0.021 |
4.6 |
P095
Phosgene.
Phosgene |
75-44-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P096
Phosphine.
Phosphine |
7803-51-2 |
CHOXD; CHRED; or CMBST |
CHOXD; CHRED; or CMBST |
P097
Famphur.
Famphur |
52-85-7 |
0.017 |
15 |
P098
Potassium cyanide.
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
P099
Potassium silver cyanide.
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
Silver |
7440-22-4 |
0.43 |
0.14 mg/l TCLP |
P101
Ethyl cyanide (Propanenitrile).
Ethyl cyanide (Propanenitrile) |
107-12-0 |
0.24 |
360 |
P102
Propargyl alcohol.
Propargyl alcohol |
107-19-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P103
Selenourea.
Selenium |
7782-49-2 |
0.82 |
5.7 mg/l TCLP |
P104
Silver cyanide.
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
Silver |
7440-22-4 |
0.43 |
0.14 mg/l TCLP |
P105
Sodium azide.
Sodium azide |
26628-22-8 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED; or CMBST |
P106
Sodium cyanide.
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
P108
Strychnine and salts.
Strychnine and salts |
57-24-9 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P109
Tetraethyldithiopyrophosphate.
Tetraethyldithiopyrophosphate |
3689-24-5 |
CARBN; or CMBST |
CMBST |
P110
Tetraethyl lead.
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
P111
Tetraethylpyrophosphate.
Tetraethylpyrophosphate |
107-49-3 |
CARBN; or CMBST |
CMBST |
P112
Tetranitromethane.
Tetranitromethane |
509-14-8 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED; or CMBST |
P113
Thallic oxide.
Thallium (measured in wastewaters only) |
7440-28-0 |
1.4 |
RTHRM; or STABL |
P114
Thallium selenite.
Selenium |
7782-49-2 |
0.82 |
5.7 mg/l TCLP |
P115
Thallium (I) sulfate.
Thallium (measured in wastewaters only) |
7440-28-0 |
1.4 |
RTHRM; or STABL |
P116
Thiosemicarbazide.
Thiosemicarbazide |
79-19-6 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P118
Trichloromethanethiol.
Trichloromethanethiol |
75-70-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
P119
Ammonium vanadate.
Vanadium (measured in wastewaters only) |
7440-62-2 |
4.3 |
STABL |
P120
Vanadium pentoxide.
Vanadium (measured in wastewaters only) |
7440-62-2 |
4.3 |
STABL |
P121
Zinc cyanide.
Cyanides (Total)7 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)7 |
57-12-5 |
0.86 |
30 |
P122
Zinc phosphide Zn3P2, when present at concentrations greater than 10 percent.
Zinc Phosphide |
1314-84-7 |
CHOXD; CHRED; or CMBST |
CHOXD; CHRED; or CMBST |
P123
Toxaphene.
Toxaphene |
8001-35-2 |
0.0095 |
2.6 |
P127
Carbofuran.
Carbofuran |
1563-66-2 |
0.006 |
0.14 |
P128
Mexacarbate.
Mexacarbate |
315-18-4 |
0.056 |
1.4 |
P185
Tirpate.10
Tirpate |
26419-73-8 |
0.056 |
0.28 |
P188
Physostigimine salicylate.
Physostigmine salicylate |
57-64-7 |
0.056 |
1.4 |
P189
Carbosulfan.
Carbosulfan |
55285-14-8 |
0.028 |
1.4 |
P190
Metolcarb.
Metolcarb |
1129-41-5 |
0.056 |
1.4 |
P191
Dimetilan.10
Dimetilan |
644-64-4 |
0.056 |
1.4 |
P192
Isolan.10
Isolan |
119-38-0 |
0.056 |
1.4 |
P194
Oxamyl.
Oxamyl |
23135-22-0 |
0.056 |
0.28 |
P196
Manganese dimethyldithiocarbamates (total).
Dithiocarbamates (total) |
NA |
0.028 |
28 |
P197
Formparanate.10
Formparanate |
17702-57-7 |
0.056 |
1.4 |
P198
Formetanate hydrochloride.
Formetanate hydrochloride |
23422-53-9 |
0.056 |
1.4 |
P199
Methiocarb.
Methiocarb |
2032-65-7 |
0.056 |
1.4 |
P201
Promecarb.
Promecarb |
2631-37-0 |
0.056 |
1.4 |
P202
m-Cumenyl methylcarbamate.
m-Cumenyl methylcarbamate |
64-00-6 |
0.056 |
1.4 |
P203
Aldicarb sulfone.
Aldicarb sulfone |
1646-88-4 |
0.056 |
0.28 |
P204
Physostigmine.
Physostigmine |
57-47-6 |
0.056 |
1.4 |
P205
Ziram.
Dithiocarbamates (total) |
NA |
0.028 |
28 |
U001
Acetaldehyde.
Acetaldehyde |
75-07-0 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U002
Acetone.
Acetone |
67-64-1 |
0.28 |
160 |
U003
Acetonitrile.
Acetonitrile |
75-05-8 |
5.6 |
CMBST |
Acetonitrile; alternate6 standard for nonwastewaters only |
75-05-8 |
NA |
38 |
U004
Acetophenone.
Acetophenone |
98-86-2 |
0.010 |
9.7 |
U005
2-Acetylaminofluorene.
2-Acetylaminofluorene |
53-96-3 |
0.059 |
140 |
U006
Acetyl chloride.
Acetyl chloride |
75-36-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U007
Acrylamide.
Acrylamide |
79-06-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U008
Acrylic acid.
Acrylic acid |
79-10-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U009
Acrylonitrile.
Acrylonitrile |
107-13-1 |
0.24 |
84 |
U010
Mitomycin C.
Mitomycin C |
50-07-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U011
Amitrole.
Amitrole |
61-82-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U012
Aniline.
Aniline |
62-53-3 |
0.81 |
14 |
U014
Auramine.
Auramine |
492-80-8 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U015
Azaserine.
Azaserine |
115-02-6 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U016
Benz(c)acridine.
Benz(c)acridine |
225-51-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U017
Benzal chloride.
Benzal chloride |
98-87-3 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U018
Benz(a)anthracene.
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
U019
Benzene.
Benzene |
71-43-2 |
0.14 |
10 |
U020
Benzenesulfonyl chloride.
Benzenesulfonyl chloride |
98-09-9 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U021
Benzidine.
Benzidine |
92-87-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U022
Benzo(a)pyrene.
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
U023
Benzotrichloride.
Benzotrichloride |
98-07-7 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED; or CMBST |
U024
bis(2-Chloroethoxy)methane.
bis(2-Chloroethoxy)methane |
111-91-1 |
0.036 |
7.2 |
U025
bis(2-Chloroethyl)ether.
bis(2-Chloroethyl)ether |
111-44-4 |
0.033 |
6.0 |
U026
Chlornaphazine.
Chlornaphazine |
494-03-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U027
bis(2-Chloroisopropyl)ether.
bis(2-Chloroisopropyl)ether |
39638-32-9 |
0.055 |
7.2 |
U028
bis(2-Ethylhexyl)phthalate.
bis(2-Ethylhexyl)phthalate |
117-81-7 |
0.28 |
28 |
U029
Methyl bromide (Bromomethane).
Methyl bromide (Bromomethane) |
74-83-9 |
0.11 |
15 |
U030
4-Bromophenyl phenyl ether.
4-Bromophenyl phenyl ether |
101-55-3 |
0.055 |
15 |
U031
n-Butyl alcohol.
n-Butyl alcohol |
71-36-3 |
5.6 |
2.6 |
U032
Calcium chromate.
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
U033
Carbon oxyfluoride.
Carbon oxyfluoride |
353-50-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U034
Trichloroacetaldehyde (Chloral).
Trichloroacetaldehyde (Chloral) |
75-87-6 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U035
Chlorambucil.
Chlorambucil |
305-03-3 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U036
Chlordane.
Chlordane ( a and c isomers) |
57-74-9 |
0.0033 |
0.26 |
U037
Chlorobenzene.
Chlorobenzene |
108-90-7 |
0.057 |
6.0 |
U038
Chlorobenzilate.
Chlorobenzilate |
510-15-6 |
0.10 |
CMBST |
U039
p-Chloro-m-cresol.
p-Chloro-m-cresol |
59-50-7 |
0.018 |
14 |
U041
Epichlorohydrin (1-Chloro-2,3-epoxypropane).
Epichlorohydrin (1-Chloro-2,3-epoxypropane) |
106-89-8 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U042
2-Chloroethyl vinyl ether.
2-Chloroethyl vinyl ether |
110-75-8 |
0.062 |
CMBST |
U043
Vinyl chloride.
Vinyl chloride |
75-01-4 |
0.27 |
6.0 |
U044
Chloroform.
Chloroform |
67-66-3 |
0.046 |
6.0 |
U045
Chloromethane (Methyl chloride).
Chloromethane (Methyl chloride) |
74-87-3 |
0.19 |
30 |
U046
Chloromethyl methyl ether.
Chloromethyl methyl ether |
107-30-2 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U047
2-Chloronaphthalene.
2-Chloronaphthalene |
91-58-7 |
0.055 |
5.6 |
U048
2-Chlorophenol.
2-Chlorophenol |
95-57-8 |
0.044 |
5.7 |
U049
4-Chloro-o-toluidine hydrochloride.
4-Chloro-o-toluidine hydrochloride |
3165-93-3 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U050
Chrysene.
Chrysene |
218-01-9 |
0.059 |
3.4 |
U051
Creosote.
Naphthalene |
91-20-3 |
0.059 |
5.6 |
Pentachlorophenol |
87-86-5 |
0.089 |
7.4 |
Phenanthrene |
85-01-8 |
0.059 |
5.6 |
Pyrene |
129-00-0 |
0.067 |
8.2 |
Toluene |
108-88-3 |
0.080 |
10 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
U052
Cresols (Cresylic acid).
o-Cresol |
95-48-7 |
0.11 |
5.6 |
m-Cresol (difficult to distinguish from p-cresol) |
108-39-4 |
0.77 |
5.6 |
p-Cresol (difficult to distinguish from m-cresol) |
106-44-5 |
0.77 |
5.6 |
Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations) |
1319-77-3 |
0.88 |
11.2 |
U053
Crotonaldehyde.
Crotonaldehyde |
4170-30-3 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U055
Cumene.
Cumene |
98-82-8 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U056
Cyclohexane.
Cyclohexane |
110-82-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U057
Cyclohexanone.
Cyclohexanone |
108-94-1 |
0.36 |
CMBST |
Cyclohexanone; alternate6 standard for nonwastewaters only |
108-94-1 |
NA |
0.75 mg/l TCLP |
U058
Cyclophosphamide.
Cyclophosphamide |
50-18-0 |
CARBN; or CMBST |
CMBST |
U059
Daunomycin.
Daunomycin |
20830-81-3 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U060
DDD.
o,p'-DDD |
53-19-0 |
0.023 |
0.087 |
p,p'-DDD |
72-54-8 |
0.023 |
0.087 |
U061
DDT.
o,p'-DDT |
789-02-6 |
0.0039 |
0.087 |
p,p'-DDT |
50-29-3 |
0.0039 |
0.087 |
o,p'-DDD |
53-19-0 |
0.023 |
0.087 |
p,p'-DDD |
72-54-8 |
0.023 |
0.087 |
o,p'-DDE |
3424-82-6 |
0.031 |
0.087 |
p,p'-DDE |
72-55-9 |
0.031 |
0.087 |
U062
Diallate.
Diallate |
2303-16-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U063
Dibenz(a,h)anthracene.
Dibenz(a,h)anthracene |
53-70-3 |
0.055 |
8.2 |
U064
Dibenz(a,i)pyrene.
Dibenz(a,i)pyrene |
189-55-9 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U066
1,2-Dibromo-3-chloropropane.
1,2-Dibromo-3-chloropropane |
96-12-8 |
0.11 |
15 |
U067
Ethylene dibromide (1,2-Dibromoethane).
Ethylene dibromide (1,2-Dibromoethane) |
106-93-4 |
0.028 |
15 |
U068
Dibromomethane.
Dibromomethane |
74-95-3 |
0.11 |
15 |
U069
Di-n-butyl phthalate.
Di-n-butyl phthalate |
84-74-2 |
0.057 |
28 |
U070
o-Dichlorobenzene.
o-Dichlorobenzene |
95-50-1 |
0.088 |
6.0 |
U071
m-Dichlorobenzene.
m-Dichlorobenzene |
541-73-1 |
0.036 |
6.0 |
U072
p-Dichlorobenzene.
p-Dichlorobenzene |
106-46-7 |
0.090 |
6.0 |
U073
3,3'-Dichlorobenzidine.
3,3'-Dichlorobenzidine |
91-94-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U074
1,4-Dichloro-2-butene.
cis-1,4-Dichloro-2-butene |
1476-11-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
trans-1,4-Dichloro-2-butene |
764-41-0 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U075
Dichlorodifluoromethane.
Dichlorodifluoromethane |
75-71-8 |
0.23 |
7.2 |
U076
1,1-Dichloroethane.
1,1-Dichloroethane |
75-34-3 |
0.059 |
6.0 |
U077
1,2-Dichloroethane.
1,2-Dichloroethane |
107-06-2 |
0.21 |
6.0 |
U078
1,1-Dichloroethylene.
1,1-Dichloroethylene |
75-35-4 |
0.025 |
6.0 |
U079
1,2-Dichloroethylene.
trans-1,2-Dichloroethylene |
156-60-5 |
0.054 |
30 |
U080
Methylene chloride.
Methylene chloride |
75-09-2 |
0.089 |
30 |
U081
2,4-Dichlorophenol.
2,4-Dichlorophenol |
120-83-2 |
0.044 |
14 |
U082
2,6-Dichlorophenol.
2,6-Dichlorophenol |
87-65-0 |
0.044 |
14 |
U083
1,2-Dichloropropane.
1,2-Dichloropropane |
78-87-5 |
0.85 |
18 |
U084
1,3-Dichloropropylene.
cis-1,3-Dichloropropylene |
10061-01-5 |
0.036 |
18 |
trans-1,3-Dichloropropylene |
10061-02-6 |
0.036 |
18 |
U085
1,2:3,4-Diepoxybutane.
1,2:3,4-Diepoxybutane |
1464-53-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U086
N,N'-Diethylhydrazine.
N,N'-Diethylhydrazine |
1615-80-1 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED; or CMBST |
U087
O,O-Diethyl-S-methyldithiophosphate.
O,O-Diethyl-S-methyldithiophosphate |
3288-58-2 |
CARBN; or CMBST |
CMBST |
U088
Diethyl phthalate.
Diethyl phthalate |
84-66-2 |
0.20 |
28 |
U089
Diethyl stilbestrol.
Diethyl stilbestrol |
56-53-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U090
Dihydrosafrole.
Dihydrosafrole |
94-58-6 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U091
3,3'-Dimethoxybenzidine.
3,3'-Dimethoxybenzidine |
119-90-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U092
Dimethylamine.
Dimethylamine |
124-40-3 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U093
p-Dimethylaminoazobenzene.
p-Dimethylaminoazobenzene |
60-11-7 |
0.13 |
CMBST |
U094
7,12-Dimethylbenz(a)anthracene.
7,12-Dimethylbenz(a)anthracene |
57-97-6 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U095
3,3'-Dimethylbenzidine.
3,3'-Dimethylbenzidine |
119-93-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U096
a , a -Dimethyl benzyl hydroperoxide.
a , a -Dimethyl benzyl hydroperoxide |
80-15-9 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED; or CMBST |
U097
Dimethylcarbamoyl chloride.
Dimethylcarbamoyl chloride |
79-44-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U098
1,1-Dimethylhydrazine.
1,1-Dimethylhydrazine |
57-14-7 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED; or CMBST |
U099
1,2-Dimethylhydrazine.
1,2-Dimethylhydrazine |
540-73-8 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED; or CMBST |
U101
2,4-Dimethylphenol.
2,4-Dimethylphenol |
105-67-9 |
0.036 |
14 |
U102
Dimethyl phthalate.
Dimethyl phthalate |
131-11-3 |
0.047 |
28 |
U103
Dimethyl sulfate.
Dimethyl sulfate |
77-78-1 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED; or CMBST |
U105
2,4-Dinitrotoluene.
2,4-Dinitrotoluene |
121-14-2 |
0.32 |
140 |
U106
2,6-Dinitrotoluene.
2,6-Dinitrotoluene |
606-20-2 |
0.55 |
28 |
U107
Di-n-octyl phthalate.
Di-n-octyl phthalate |
117-84-0 |
0.017 |
28 |
U108
1,4-Dioxane.
1,4-Dioxane |
123-91-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
1,4-Dioxane; alternate6 standard for nonwastewaters only |
123-91-1 |
12.0 |
170 |
U109
1,2-Diphenylhydrazine.
1,2-Diphenylhydrazine |
122-66-7 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED; or CMBST |
1,2-Diphenylhydrazine; alternate6 standard for wastewaters only |
122-66-7 |
0.087 |
NA |
U110
Dipropylamine.
Dipropylamine |
142-84-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U111
Di-n-propylnitrosamine.
Di-n-propylnitrosamine |
621-64-7 |
0.40 |
14 |
U112
Ethyl acetate.
Ethyl acetate |
141-78-6 |
0.34 |
33 |
U113
Ethyl acrylate.
Ethyl acrylate |
140-88-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U114
Ethylenebisdithiocarbamic acid salts and esters.
Ethylenebisdithiocarbamic acid |
111-54-6 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U115
Ethylene oxide.
Ethylene oxide |
75-21-8 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CHOXD; or CMBST |
Ethylene oxide; alternate6 standard for wastewaters only |
75-21-8 |
0.12 |
NA |
U116
Ethylene thiourea.
Ethylene thiourea |
96-45-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U117
Ethyl ether.
Ethyl ether |
60-29-7 |
0.12 |
160 |
U118
Ethyl methacrylate.
Ethyl methacrylate |
97-63-2 |
0.14 |
160 |
U119
Ethyl methane sulfonate.
Ethyl methane sulfonate |
62-50-0 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U120
Fluoranthene.
Fluoranthene |
206-44-0 |
0.068 |
3.4 |
U121
Trichloromonofluoromethane.
Trichloromonofluoromethane |
75-69-4 |
0.020 |
30 |
U122
Formaldehyde.
Formaldehyde |
50-00-0 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U123
Formic acid.
Formic acid |
64-18-6 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U124
Furan.
Furan |
110-00-9 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U125
Furfural.
Furfural |
98-01-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U126
Glycidylaldehyde.
Glycidylaldehyde |
765-34-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U127
Hexachlorobenzene.
Hexachlorobenzene |
118-74-1 |
0.055 |
10 |
U128
Hexachlorobutadiene.
Hexachlorobutadiene |
87-68-3 |
0.055 |
5.6 |
U129
Lindane.
a -BHC |
319-84-6 |
0.00014 |
0.066 |
b -BHC |
319-85-7 |
0.00014 |
0.066 |
d -BHC |
319-86-8 |
0.023 |
0.066 |
g -BHC (Lindane) |
58-89-9 |
0.0017 |
0.066 |
U130
Hexachlorocyclopentadiene.
Hexachlorocyclopentadiene |
77-47-4 |
0.057 |
2.4 |
U131
Hexachloroethane.
Hexachloroethane |
67-72-1 |
0.055 |
30 |
U132
Hexachlorophene.
Hexachlorophene |
70-30-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U133
Hydrazine.
Hydrazine |
302-01-2 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED; or CMBST |
U134
Hydrogen fluoride.
Fluoride (measured in wastewaters only) |
16964-48-8 |
35 |
ADGAS fb NEUTR; or NEUTR |
U135
Hydrogen sulfide.
Hydrogen sulfide |
7783-06-4 |
CHOXD; CHRED; or CMBST |
CHOXD; CHRED; or CMBST |
U136
Cacodylic acid.
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
U137
Indeno(1,2,3-c,d)pyrene.
Indeno(1,2,3-c,d)pyrene |
193-39-5 |
0.0055 |
3.4 |
U138
Iodomethane.
Iodomethane |
74-88-4 |
0.19 |
65 |
U140
Isobutyl alcohol.
Isobutyl alcohol |
78-83-1 |
5.6 |
170 |
U141
Isosafrole.
Isosafrole |
120-58-1 |
0.081 |
2.6 |
U142
Kepone.
Kepone |
143-50-8 |
0.0011 |
0.13 |
U143
Lasiocarpine.
Lasiocarpine |
303-34-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U144
Lead acetate.
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
U145
Lead phosphate.
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
U146
Lead subacetate.
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
U147
Maleic anhydride.
Maleic anhydride |
108-31-6 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U148
Maleic hydrazide.
Maleic hydrazide |
123-33-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U149
Malononitrile.
Malononitrile |
109-77-3 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U150
Melphalan.
Melphalan |
148-82-3 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U151
U151 (mercury) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.
Mercury |
7439-97-6 |
NA |
RMERC |
U151
U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are residues from RMERC only.
Mercury |
7439-97-6 |
NA |
0.20 mg/l TCLP |
U151
U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are not residues from RMERC only.
Mercury |
7439-97-6 |
NA |
0.025 mg/l TCLP |
U151
All U151 (mercury) wastewater.
Mercury |
7439-97-6 |
0.15 |
NA |
U151
Element Elemental Mercury Contaminated with Radioactive Materials.
Mercury |
7439-97-6 |
NA |
AMLGM |
U152
Methacrylonitrile.
Methacrylonitrile |
126-98-7 |
0.24 |
84 |
U153
Methanethiol.
Methanethiol |
74-93-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U154
Methanol.
Methanol |
67-56-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
Methanol; alternate6 set of standards for both wastewaters and nonwastewaters |
67-56-1 |
5.6 |
0.75 mg/l TCLP |
U155
Methapyrilene.
Methapyrilene |
91-80-5 |
0.081 |
1.5 |
U156
Methyl chlorocarbonate.
Methyl chlorocarbonate |
79-22-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U157
3-Methylcholanthrene.
3-Methylcholanthrene |
56-49-5 |
0.0055 |
15 |
U158
4,4'-Methylene bis(2-chloroaniline).
4,4'-Methylene bis(2-chloroaniline) |
101-14-4 |
0.50 |
30 |
U159
Methyl ethyl ketone.
Methyl ethyl ketone |
78-93-3 |
0.28 |
36 |
U160
Methyl ethyl ketone peroxide.
Methyl ethyl ketone peroxide |
1338-23-4 |
CHOXD; CHRED; CARBN; BIODG; or CMBST |
CHOXD; CHRED; or CMBST |
U161
Methyl isobutyl ketone.
Methyl isobutyl ketone |
108-10-1 |
0.14 |
33 |
U162
Methyl methacrylate.
Methyl methacrylate |
80-62-6 |
0.14 |
160 |
U163
N-Methyl-N'-nitro-N-nitrosoguanidine.
N-Methyl-N'-nitro-N-nitrosoguanidine |
70-25-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U164
Methylthiouracil.
Methylthiouracil |
56-04-2 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U165
Naphthalene.
Naphthalene |
91-20-3 |
0.059 |
5.6 |
U166
1,4-Naphthoquinone.
1,4-Naphthoquinone |
130-15-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U167
1-Naphthylamine.
1-Naphthylamine |
134-32-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U168
2-Naphthylamine.
2-Naphthylamine |
91-59-8 |
0.52 |
CMBST |
U169
Nitrobenzene.
Nitrobenzene |
98-95-3 |
0.068 |
14 |
U170
p-Nitrophenol.
p-Nitrophenol |
100-02-7 |
0.12 |
29 |
U171
2-Nitropropane.
2-Nitropropane |
79-46-9 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U172
N-Nitrosodi-n-butylamine.
N-Nitrosodi-n-butylamine |
924-16-3 |
0.40 |
17 |
U173
N-Nitrosodiethanolamine.
N-Nitrosodiethanolamine |
1116-54-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U174
N-Nitrosodiethylamine.
N-Nitrosodiethylamine |
55-18-5 |
0.40 |
28 |
U176
N-Nitroso-N-ethylurea.
N-Nitroso-N-ethylurea |
759-73-9 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U177
N-Nitroso-N-methylurea.
N-Nitroso-N-methylurea |
684-93-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U178
N-Nitroso-N-methylurethane.
N-Nitroso-N-methylurethane |
615-53-2 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U179
N-Nitrosopiperidine.
N-Nitrosopiperidine |
100-75-4 |
0.013 |
35 |
U180
N-Nitrosopyrrolidine.
N-Nitrosopyrrolidine |
930-55-2 |
0.013 |
35 |
U181
5-Nitro-o-toluidine.
5-Nitro-o-toluidine |
99-55-8 |
0.32 |
28 |
U182
Paraldehyde.
Paraldehyde |
123-63-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U183
Pentachlorobenzene.
Pentachlorobenzene |
608-93-5 |
0.055 |
10 |
U184
Pentachloroethane.
Pentachloroethane |
76-01-7 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
Pentachloroethane; alternate6 standards for both wastewaters and nonwastewaters |
76-01-7 |
0.055 |
6.0 |
U185
Pentachloronitrobenzene.
Pentachloronitrobenzene |
82-68-8 |
0.055 |
4.8 |
U186
1,3-Pentadiene.
1,3-Pentadiene |
504-60-9 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U187
Phenacetin.
Phenacetin |
62-44-2 |
0.081 |
16 |
U188
Phenol.
Phenol |
108-95-2 |
0.039 |
6.2 |
U189
Phosphorus sulfide.
Phosphorus sulfide |
1314-80-3 |
CHOXD; CHRED; or CMBST |
CHOXD; CHRED; or CMBST |
U190
Phthalic anhydride.
Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) |
100-21-0 |
0.055 |
28 |
Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) |
85-44-9 |
0.055 |
28 |
U191
2-Picoline.
2-Picoline |
109-06-8 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U192
Pronamide.
Pronamide |
23950-58-5 |
0.093 |
1.5 |
U193
1,3-Propane sultone.
1,3-Propane sultone |
1120-71-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U194
n-Propylamine.
n-Propylamine |
107-10-8 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U196
Pyridine.
Pyridine |
110-86-1 |
0.014 |
16 |
U197
p-Benzoquinone.
p-Benzoquinone |
106-51-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U200
Reserpine.
Reserpine |
50-55-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U201
Resorcinol
Resorcinol. |
108-46-3 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U202
Saccharin and salts.
Saccharin |
81-07-2 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U203
Safrole.
Safrole |
94-59-7 |
0.081 |
22 |
U204
Selenium dioxide.
Selenium |
7782-49-2 |
0.82 |
5.7 mg/l TCLP |
U205
Selenium sulfide.
Selenium |
7782-49-2 |
0.82 |
5.7 mg/l TCLP |
U206
Streptozotocin.
Streptozotocin |
18883-66-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U207
1,2,4,5-Tetrachlorobenzene.
1,2,4,5-Tetrachlorobenzene |
95-94-3 |
0.055 |
14 |
U208
1,1,1,2-Tetrachloroethane.
1,1,1,2-Tetrachloroethane |
630-20-6 |
0.057 |
6.0 |
U209
1,1,2,2-Tetrachloroethane.
1,1,2,2-Tetrachloroethane |
79-34-5 |
0.057 |
6.0 |
U210
Tetrachloroethylene.
Tetrachloroethylene |
127-18-4 |
0.056 |
6.0 |
U211
Carbon tetrachloride.
Carbon tetrachloride |
56-23-5 |
0.057 |
6.0 |
U213
Tetrahydrofuran.
Tetrahydrofuran |
109-99-9 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U214
Thallium (I) acetate.
Thallium (measured in wastewaters only) |
7440-28-0 |
1.4 |
RTHRM; or STABL |
U215
Thallium (I) carbonate.
Thallium (measured in wastewaters only) |
7440-28-0 |
1.4 |
RTHRM; or STABL |
U216
Thallium (I) chloride.
Thallium (measured in wastewaters only) |
7440-28-0 |
1.4 |
RTHRM; or STABL |
U217
Thallium (I) nitrate.
Thallium (measured in wastewaters only) |
7440-28-0 |
1.4 |
RTHRM; or STABL |
U218
Thioacetamide.
Thioacetamide |
62-55-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U219
Thiourea.
Thiourea |
62-56-6 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U220
Toluene.
Toluene |
108-88-3 |
0.080 |
10 |
U221
Toluenediamine.
Toluenediamine |
25376-45-8 |
CARBN; or CMBST |
CMBST |
U222
o-Toluidine hydrochloride.
o-Toluidine hydrochloride |
636-21-5 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U223
Toluene diisocyanate.
Toluene diisocyanate |
26471-62-5 |
CARBN; or CMBST |
CMBST |
U225
Bromoform (Tribromomethane).
Bromoform (Tribromomethane) |
75-25-2 |
0.63 |
15 |
U226
1,1,1-Trichloroethane.
1,1,1-Trichloroethane |
71-55-6 |
0.054 |
6.0 |
U227
1,1,2-Trichloroethane.
1,1,2-Trichloroethane |
79-00-5 |
0.054 |
6.0 |
U228
Trichloroethylene.
Trichloroethylene |
79-01-6 |
0.054 |
6.0 |
U234
1,3,5-Trinitrobenzene.
1,3,5-Trinitrobenzene |
99-35-4 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U235
tris-(2,3-Dibromopropyl)-phosphate.
tris-(2,3-Dibromopropyl)-phosphate |
126-72-7 |
0.11 |
0.10 |
U236
Trypan Blue.
Trypan Blue |
72-57-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U237
Uracil mustard.
Uracil mustard |
66-75-1 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U238
Urethane (Ethyl carbamate).
Urethane (Ethyl carbamate) |
51-79-6 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U239
Xylenes.
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
U240
2,4-D (2,4-Dichlorophenoxyacetic acid).
2,4-D (2,4-Dichlorophenoxyacetic acid) |
94-75-7 |
0.72 |
10 |
2,4-D (2,4-Dichlorophenoxyacetic acid) salts and esters |
NA |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U243
Hexachloropropylene.
Hexachloropropylene |
1888-71-7 |
0.035 |
30 |
U244
Thiram.
Thiram |
137-26-8 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U246
Cyanogen bromide.
Cyanogen bromide |
506-68-3 |
CHOXD; WETOX; or CMBST |
CHOXD; WETOX; or CMBST |
U247
Methoxychlor.
Methoxychlor |
72-43-5 |
0.25 |
0.18 |
U248
Warfarin, & salts, when present at concentrations of 0.3 percent or less.
Warfarin |
81-81-2 |
(WETOX or CHOXD) fb CARBN; or CMBST |
CMBST |
U249
Zinc phosphide, Zn3P2, when present at concentrations of 10 percent or less.
Zinc Phosphide |
1314-84-7 |
CHOXD; CHRED; or CMBST |
CHOXD; CHRED; or CMBST |
U271
Benomyl.
Benomyl |
17804-35-2 |
0.056 |
1.4 |
U278
Bendiocarb.
Bendiocarb |
22781-23-3 |
0.056 |
1.4 |
U279
Carbaryl.
Carbaryl |
63-25-2 |
0.006 |
0.14 |
U280
Barban.
Barban |
101-27-9 |
0.056 |
1.4 |
U328
o-Toluidine.
o-Toluidine |
95-53-4 |
CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN |
CMBST |
U353
p-Toluidine.
p-Toluidine |
106-49-0 |
CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN |
CMBST |
U359
2-Ethoxyethanol.
2-Ethoxyethanol |
110-80-5 |
CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN |
CMBST |
U364
Bendiocarb phenol.10
Bendiocarb phenol |
22961-82-6 |
0.056 |
1.4 |
U367
Carbofuran phenol.
Carbofuran phenol |
1563-38-8 |
0.056 |
1.4 |
U372
Carbendazim.
Carbendazim |
10605-21-7 |
0.056 |
1.4 |
U373
Propham.
Propham |
122-42-9 |
0.056 |
1.4 |
U387
Prosulfocarb.
Prosulfocarb |
52888-80-9 |
0.042 |
1.4 |
U389
Triallate.
Triallate |
2303-17-5 |
0.042 |
1.4 |
U394
A2213.10
A2213 |
30558-43-1 |
0.042 |
1.4 |
U395
Diethylene glycol, dicarbamate.10
Diethylene glycol, dicarbamate |
5952-26-1 |
0.056 |
1.4 |
U404
Triethylamine.
Triethylamine |
101-44-8 |
0.081 |
1.5 |
U409
Thiophanate-methyl.
Thiophanate-methyl |
23564-05-8 |
0.056 |
1.4 |
U410
Thiodicarb.
Thiodicarb |
59669-26-0 |
0.019 |
1.4 |
U411
Propoxur.
Propoxur |
114-26-1 |
0.056 |
1.4 |
Notes:
1 | The waste descriptions provided in this table do not replace waste descriptions in 35 Ill. Adm. Code 721. Descriptions of Treatment or Regulatory Subcategories are provided, as needed, to distinguish between applicability of different standards. |
2 | CAS means Chemical Abstract Services. When the waste code or regulated constituents are described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only. |
3 | Concentration standards for wastewaters are expressed in mg/l and are based on analysis of composite samples. |
4 | All treatment standards expressed as a Technology Code or combination of Technology Codes are explained in detail in Table C of this Part, “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 on incineration in units operated in accordance with the technical requirements of Subpart O of 35 Ill. Adm. Code 724 |
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 or Regulatory Subcategory or physical form (i.e., wastewater or nonwastewater) specified for that alternate standard. |
7 | 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 or Chemical Methods,” |
8 | These wastes, when rendered non-hazardous and then subsequently managed in CWA or CWA-equivalent systems, are not subject to treatment standards. (See Section 728.101(c)(3) and (c)(4).) |
9 | These wastes, when rendered non-hazardous and then subsequently injected in a Class I SDWA well, are not subject to treatment standards. (See 35 Ill. Adm. Code 738.101(d).) |
10 | The treatment standard for this waste may be satisfied by either meeting the constituent concentrations in the table in this Section or by treating the waste by the specified technologies: combustion, as defined by the technology code CMBST at Table C, 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 Table C, for wastewaters. |
11 | For these wastes, the definition of CMBST is limited to any of the following that have obtained a determination of equivalent treatment under Section 728.142(b): (1) combustion units operating under 35 Ill. Adm. Code 726, (2) combustion units permitted under Subpart O of 35 Ill. Adm. Code 724 |
12 | Disposal of USEPA hazardous waste number K175 waste that has complied with all applicable Section 728.140 treatment standards must also be macroencapsulated in accordance with Table F of this Part, unless the waste is placed in either of the following types of facilities: |
a) | A RCRA Subtitle C monofill containing only K175 wastes that meet all applicable 40 CFR 268.40 treatment standards; or |
b) | A dedicated RCRA Subtitle C landfill cell in which all other wastes being co-disposed are at pH≤6.0. |
BOARD NOTE: Derived from table to 40 CFR 268.40 (2000) (2002), as amended at 65 Fed. Reg. 67127 (November 8, 2000) and 66 Fed. Reg. 58258 (November 20, 2001).
NA | means not applicable. |
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)
Section 728.Table U | Universal Treatment Standards (UTS) |
Regulated Constituent-Common Name |
CAS1 No. |
Wastewater Standard Concentration (in mg/l2) |
Nonwastewater Standard Concentration (in mg/kg3 unless noted as “mg/l TCLP”) |
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 |
Aldicarb sulfone6 |
1646-88-4 |
0.056 |
0.28 |
Aldrin |
309-00-2 |
0.021 |
0.066 |
4-Aminobiphenyl |
92-67-1 |
0.13 |
NA |
Aniline |
62-53-3 |
0.81 |
14 |
Anthracene |
120-12-7 |
0.059 |
3.4 |
Aramite |
140-57-8 |
0.36 |
NA |
a -BHC |
319-84-6 |
0.00014 |
0.066 |
b -BHC |
319-85-7 |
0.00014 |
0.066 |
d -BHC |
319-86-8 |
0.023 |
0.066 |
g -BHC |
58-89-9 |
0.0017 |
0.066 |
Barban6 |
101-27-9 |
0.056 |
1.4 |
Bendiocarb6 |
22781-23-3 |
0.056 |
1.4 |
Benomyl6 |
17804-35-2 |
0.056 |
1.4 |
Benz(a)anthracene |
56-55-3 |
0.059 |
3.4 |
Benzal chloride |
98-87-3 |
0.055 |
6.0 |
Benzene |
71-43-2 |
0.14 |
10 |
Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) |
205-99-2 |
0.11 |
6.8 |
Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) |
207-08-9 |
0.11 |
6.8 |
Benzo(g,h,i)perylene |
191-24-2 |
0.0055 |
1.8 |
Benzo(a)pyrene |
50-32-8 |
0.061 |
3.4 |
Bromodichloromethane |
75-27-4 |
0.35 |
15 |
Methyl bromide (Bromomethane) |
74-83-9 |
0.11 |
15 |
4-Bromophenyl phenyl ether |
101-55-3 |
0.055 |
15 |
n-Butyl alcohol |
71-36-3 |
5.6 |
2.6 |
Butylate6 |
2008-41-5 |
0.042 |
1.4 |
Butyl benzyl phthalate |
85-68-7 |
0.017 |
28 |
2-sec-Butyl-4,6-dinitrophenol (Dinoseb) |
88-85-7 |
0.066 |
2.5 |
Carbaryl6 |
63-25-2 |
0.006 |
0.14 |
Carbenzadim6 |
10605-21-7 |
0.056 |
1.4 |
Carbofuran6 |
1563-66-2 |
0.006 |
0.14 |
Carbofuran phenol6 |
1563-38-8 |
0.056 |
1.4 |
Carbon disulfide |
75-15-0 |
3.8 |
4.8 mg/l TCLP |
Carbon tetrachloride |
56-23-5 |
0.057 |
6.0 |
Carbosulfan6 |
55285-14-8 |
0.028 |
1.4 |
Chlordane ( a and g 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 |
p-Chloro-m-cresol |
59-50-7 |
0.018 |
14 |
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 |
2-Chloroethyl vinyl ether |
110-75-8 |
0.062 |
NA |
Chloroform |
67-66-3 |
0.046 |
6.0 |
bis(2-Chloroisopropyl)ether |
39638-32-9 |
0.055 |
7.2 |
Chloromethane (Methyl chloride) |
74-87-3 |
0.19 |
30 |
2-Chloronaphthalene |
91-58-7 |
0.055 |
5.6 |
2-Chlorophenol |
95-57-8 |
0.044 |
5.7 |
3-Chloropropylene |
107-05-1 |
0.036 |
30 |
Chrysene |
218-01-9 |
0.059 |
3.4 |
o-Cresol |
95-48-7 |
0.11 |
5.6 |
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 |
m-Cumenyl methylcarbamate6 |
64-00-6 |
0.056 |
1.4 |
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-Dimethyl phenol |
105-67-9 |
0.036 |
14 |
Dimethyl phthalate |
131-11-3 |
0.047 |
28 |
Di-n-butyl phthalate |
84-74-2 |
0.057 |
28 |
1,4-Dinitrobenzene |
100-25-4 |
0.32 |
2.3 |
4,6-Dinitro-o-cresol |
534-52-1 |
0.28 |
160 |
2,4-Dinitrophenol |
51-28-5 |
0.12 |
160 |
2,4-Dinitrotoluene |
121-14-2 |
0.32 |
140 |
2,6-Dinitrotoluene |
606-20-2 |
0.55 |
28 |
Di-n-octyl phthalate |
117-84-0 |
0.017 |
28 |
Di-n-propylnitrosamine |
621-64-7 |
0.40 |
14 |
1,4-Dioxane |
123-91-1 |
12.0 |
170 |
Diphenylamine (difficult to distinguish from diphenylnitrosamine) |
122-39-4 |
0.92 |
13 |
Diphenylnitrosamine (difficult to distinguish from diphenylamine) |
86-30-6 |
0.92 |
13 |
1,2-Diphenylhydrazine |
122-66-7 |
0.087 |
NA |
Disulfoton |
298-04-4 |
0.017 |
6.2 |
Dithiocarbamates (total)6 |
137-30-4 |
0.028 |
28 |
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 |
EPTC6 |
759-94-4 |
0.042 |
1.4 |
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 |
Ethylene oxide |
75-21-8 |
0.12 |
NA |
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 |
Famphur |
52-85-7 |
0.017 |
15 |
Fluoranthene |
206-44-0 |
0.068 |
3.4 |
Fluorene |
86-73-7 |
0.059 |
3.4 |
Formetanate hydrochloride6 |
23422-53-9 |
0.056 |
1.4 |
Heptachlor |
76-44-8 |
0.0012 |
0.066 |
1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (1,2,3,4,6,7,8-HpCDD) |
35822-46-9 |
0.000035 |
0.0025 |
1,2,3,4,6,7,8-Heptachlorodibenzofuran (1,2,3,4,6,7,8-HpCDF) |
67562-39-4 |
0.000035 |
0.0025 |
1,2,3,4,7,8,9-Heptachlorodibenzofuran (1,2,3,4,7,8,9-HpCDF) |
55673-89-7 |
0.000035 |
0.0025 |
Heptachlor epoxide |
1024-57-3 |
0.016 |
0.066 |
Hexachlorobenzene |
118-74-1 |
0.055 |
10 |
Hexachlorobutadiene |
87-68-3 |
0.055 |
5.6 |
Hexachlorocyclopentadiene |
77-47-4 |
0.057 |
2.4 |
HxCDDs (All Hexachlorodibenzo-p-dioxins) |
NA |
0.000063 |
0.001 |
HxCDFs (All Hexachlorodibenzofurans) |
55684-94-1 |
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 |
Methiocarb6 |
2032-65-7 |
0.056 |
1.4 |
Methomyl6 |
16752-77-5 |
0.028 |
0.14 |
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 |
Metolcarb6 |
1129-41-5 |
0.056 |
1.4 |
Mexacarbate6 |
315-18-4 |
0.056 |
1.4 |
Molinate6 |
2212-67-1 |
0.042 |
1.4 |
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 (1,2,3,4,6,7,8,9-OCDD) |
3268-87-9 |
0.000063 |
0.005 |
1,2,3,4,6,7,8,9-Octachlorodibenzofuran (1,2,3,4,6,7,8,9-OCDF) |
39001-02-0 |
0.000063 |
0.005 |
Oxamyl6 |
23135-22-0 |
0.056 |
0.28 |
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 |
Pebulate6 |
1114-71-2 |
0.042 |
1.4 |
Pentachlorobenzene |
608-93-5 |
0.055 |
10 |
PeCDDs (All Pentachlorodibenzo-p-dioxins) |
36088-22-9 |
0.000063 |
0.001 |
PeCDFs (All Pentachlorodibenzofurans) |
30402-15-4 |
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 |
Phorate |
298-02-2 |
0.021 |
4.6 |
Phthalic acid |
100-21-0 |
0.055 |
28 |
Phthalic anhydride |
85-44-9 |
0.055 |
28 |
Physostigmine6 |
57-47-6 |
0.056 |
1.4 |
Physostigmine salicylate6 |
57-64-7 |
0.056 |
1.4 |
Promecarb6 |
2631-37-0 |
0.056 |
1.4 |
Pronamide |
23950-58-5 |
0.093 |
1.5 |
Propham6 |
122-42-9 |
0.056 |
1.4 |
Propoxur6 |
114-26-1 |
0.056 |
1.4 |
Prosulfocarb6 |
52888-80-9 |
0.042 |
1.4 |
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) |
41903-57-5 |
0.000063 |
0.001 |
TCDFs (All Tetrachlorodibenzofurans) |
55722-27-5 |
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 |
Thiodicarb6 |
59669-26-0 |
0.019 |
1.4 |
Thiophanate-methyl6 |
23564-05-8 |
0.056 |
1.4 |
Toluene |
108-88-3 |
0.080 |
10 |
Toxaphene |
8001-35-2 |
0.0095 |
2.6 |
Triallate6 |
2303-17-5 |
0.042 |
1.4 |
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 |
Triethylamine6 |
101-44-8 |
0.081 |
1.5 |
tris-(2,3-Dibromopropyl) phosphate |
126-72-7 |
0.11 |
0.10 |
Vernolate6 |
1929-77-7 |
0.042 |
1.4 |
Vinyl chloride |
75-01-4 |
0.27 |
6.0 |
Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) |
1330-20-7 |
0.32 |
30 |
Antimony |
7440-36-0 |
1.9 |
1.15 mg/l TCLP |
Arsenic |
7440-38-2 |
1.4 |
5.0 mg/l TCLP |
Barium |
7440-39-3 |
1.2 |
21 mg/l TCLP |
Beryllium |
7440-41-7 |
0.82 |
1.22 mg/l TCLP |
Cadmium |
7440-43-9 |
0.69 |
0.11 mg/l TCLP |
Chromium (Total) |
7440-47-3 |
2.77 |
0.60 mg/l TCLP |
Cyanides (Total)4 |
57-12-5 |
1.2 |
590 |
Cyanides (Amenable)4 |
57-12-5 |
0.86 |
30 |
Fluoride5 |
16984-48-8 |
35 |
NA |
Lead |
7439-92-1 |
0.69 |
0.75 mg/l TCLP |
Mercury-Nonwastewater from Retort |
7439-97-6 |
NA |
0.20 mg/l TCLP |
Mercury-All Others |
7439-97-6 |
0.15 |
0.025 mg/l TCLP |
Nickel |
7440-02-0 |
3.98 |
11 mg/l TCLP |
Selenium7 |
7782-49-2 |
0.82 |
5.7 mg/l TCLP |
Silver |
7440-22-4 |
0.43 |
0.14 mg/l TCLP |
Sulfide |
18496-25-8 |
14 |
NA |
Thallium |
7440-28-0 |
1.4 |
0.20 mg/l TCLP |
Vanadium5 |
7440-62-2 |
4.3 |
1.6 mg/l TCLP |
Zinc5 |
7440-66-6 |
2.61 |
4.3 mg/l TCLP |
1 | CAS means Chemical Abstract Services. When the waste code or regulated constituents are described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only. |
2 | Concentration standards for wastewaters are expressed in mg/l 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 on incineration in units operated in accordance with the technical requirements of Subpart O of 35 Ill. Adm. Code 724 |
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,” |
5 | These constituents are not “underlying hazardous constituents” in characteristic wastes, according to the definition at Section 728.102(i). |
6 | This footnote corresponds with footnote 6 to the table to 40 CFR 268.48(a), which has already expired by its own terms. This statement maintains structural consistency with the corresponding federal regulations. |
7 | This constituent is not an underlying hazardous constituent, as defined at Section 728.102(i), 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 USEPA hazardous waste numbers D004 through D011 only. |
Note: NA means not applicable.
BOARD NOTE: Derived from table to 40 CFR 268.48(a) (2000) (2002), as amended at 65 Fed. Reg. 81381 (December 26, 2000).
(Source: Amended at 27 Ill. Reg. ________, effective ______________________)