ILLINOIS POLLUTION CONTROL BOARD
April 18, 2002
IN THE MATTER OF:
)
)
R02-1
RCRA SUBTITLE C UPDATE, USEPA ) (Identical-in-Substance
AMENDMENTS (January 1, 2001 through ) Rulemaking - Land)
June 30, 2001)
)
________________________________________
RCRA SUBTITLE C UPDATE, USEPA ) R02-12
AMENDMENTS (July 1, 2001 through ) (Identical-in-Substance
December 31, 2001, January 22, 2002, ) Rulemaking - Land)
March 13, 2002, and April 9, 2002) )
________________________________________
UIC UPDATE, USEPA AMENDMENTS ) R02-17
(July 1, 2001 through December 31, 2001) ) (Identical-in-Substance
) Rulemaking - Land)
)
(Consolidated)
Adopted Rule. Final Order.
ORDER OF THE BOARD (by S.T. Lawton, Jr.):
The Board adopts amendments to the Illinois regulations that are “identical in
substance” to cover rules adopted by the United States Environmental Protection Agency
(USEPA) in two programs:
1. Hazardous waste regulations that the United States Environmental Protection Agency
(USEPA) adopted to implement Subtitle C of the federal Resource Conservation and
Recovery Act of 1976 (RCRA Subtitle C) (42 U.S.C. §§ 6921
et seq
. (2000)) are
adopted by the Board under Sections 7.2 and 22.4(a) of the Environmental Protection
Act (Act) (415 ILCS 5/7.2 and 22.4(a) (2000)). Today’s RCRA Subtitle C
amendments adopted by USEPA during the periods January 1, 2001 through June 30,
2001 and July 1, 2001 through December 31, 2001, and amendments that occurred on
January 22, 2002, March 13, 2002, and April 9, 2002.
2. Underground injection control (UIC) regulations that USEPA adopted to implement
Section 1421 of the federal Safe Drinking Water Act (SDWA) (42 U.S.C. § 300h
(2000))are adopted by the Board under Sections 7.2 and 13(c) of the Act (415 ILCS
5/7.2 and 13(c) (2000)). Today’s UIC amendments cover rules adopted by USEPA
during the period July 1, 2001 through December 31, 2001.
2
This order is supported by an opinion that the Board also adopts today.
IT IS SO ORDERED.
I, Dorothy M. Gunn, Clerk of the Illinois Pollution Control Board, certify that the
Board adopted the above oorder on April 18, 2002, by a vote of 6-0.
Dorothy M. Gunn, Clerk
Illinois Pollution Control Board
3
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
4
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
5
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 Why This Subpart Is Written in a Special 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
703.Appendix A 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
6
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. ________, effective
______________________.
SUBPART G: CHANGES TO PERMITS
Section 703.280 Permit Modification at the Request of the Permittee
a) Class 1 modifications. See Section 703.281.
b) Class 2 modifications. See Section 703.282.
c) Class 3 modifications. See Section 703.283.
d) Other modifications.
1) In the case of modifications not explicitly listed in Appendix A, the
permittee may submit a Class 3 modification request to the Agency, or
the permittee may request a determination by the Agency that the
modification be reviewed and approved as a Class 1 or Class 2
modification. If the permittee requests that the modification be classified
7
as a Class 1 or 2 modification, the permittee must provide the Agency
with the necessary information to support the requested classification.
2) The Agency must make the determination described in subsection (d)(1)
of this Section as promptly as practicable. In determining the
appropriate class for a specific modification, the Agency must consider
the similarity of the modification to other modifications codified in
Appendix A and the following criteria:
A) Class 1 modifications apply to minor changes that keep the permit
current with routine changes to the facility or its operation.
These changes do not substantially alter the permit conditions or
reduce the capacity of the facility to protect human health or the
environment. In the case of Class 1 modifications, the Agency
may require prior approval.
B) Class 2 modifications apply to changes that are necessary to
enable a permittee to respond, in a timely manner, to any of the
following:
i) Common variations in the types and quantities of the
wastes managed under the facility permit;
ii) Technological advances; and
iii) Changes necessary to comply with new regulations, where
these changes can be implemented without substantially
changing design specifications or management practices in
the permit.
C) Class 3 modifications substantially alter the facility or its
operation.
e) Temporary authorizations.
1) Upon request of the permittee, the Agency shall must, without prior
public notice and comment, grant the permittee a temporary
authorization in accordance with this subsection. Temporary
authorizations have a term of not more than 180 days.
2) Procedures.
8
A) The permittee may request a temporary authorization for the
following:
i) Any Class 2 modification meeting the criteria in
subsection (e)(3)(B) of this Section; and
ii) Any Class 3 modification that meets the criteria in
subsection (e)(3)(B)(i) or that meets the criteria in
subsections (e)(3)(B)(iii) through (v) and provides
improved management or treatment of a hazardous waste
already listed in the facility permit.
B) The temporary authorization request must include the following:
i) A description of the activities to be conducted under the
temporary authorization;
ii) An explanation of why the temporary authorization is
necessary; and
iii) Sufficient information to ensure compliance with 35 Ill.
Adm. Code 724 standards.
C) The permittee must send a notice about the temporary
authorization request to all persons on the facility mailing list
maintained by the Agency and to appropriate units of State and
local governments as specified in 35 Ill. Adm. Code
705.163(a)(5). This notification must be made within seven days
after submission of the authorization request.
3) The Agency must approve or deny the temporary authorization as
quickly as practical. To issue a temporary authorization, the Agency
must find as follows:
A) That the authorized activities are in compliance with the standards
of 35 Ill. Adm. Code 724.
B) That the temporary authorization is necessary to achieve one of
the following objectives before action is likely to be taken on a
modification request:
i) To facilitate timely implementation of closure or
corrective action activities;
9
ii) To allow treatment or storage in tanks, containers or in
containment buildings in accordance with 35 Ill. Adm.
Code 728;
iii) To prevent disruption of ongoing waste management
activities;
iv) To enable the permittee to respond to sudden changes in
the types or quantities of the wastes managed under the
facility permit; or
v) To facilitate other changes to protect human health and the
environment.
4) A temporary authorization must be reissued for one additional term of up
to 180 days, provided that the permittee has requested a Class 2 or 3
permit modification for the activity covered in the temporary
authorization and either of the following is true:
A) The reissued temporary authorization constitutes the Agency’s
decision on a Class 2 permit modification in accordance with
Section 703.282(f)(1)(D) or (f)(2)(D); or
B) The Agency determines that the reissued temporary authorization
involving a Class 3 permit modification request is warranted to
allow the authorized activities to continue while the modification
procedures of 35 Ill. Adm. Code 703.283 are conducted.
f) Public notice and appeals of permit modification decisions.
1) The Agency must notify persons on the facility mailing list and
appropriate units of State and local government within 10 days after any
decision to grant or deny a Class 2 or 3 permit modification request.
The Agency must also notify such persons within 10 days after an
automatic authorization for a Class 2 modification goes into effect under
Section 703.282(f)(3) or (f)(5).
2) The Agency’s decision to grant or deny a Class 2 or 3 permit
modification request may be appealed under the permit appeal
procedures of 35 Ill. Adm. Code 705.212.
10
3) An automatic authorization that goes into effect under Section
703.282(f)(3) or (f)(5) may be appealed under the permit appeal
procedures of 35 Ill. Adm. Code 705.212; however, the permittee may
continue to conduct the activities pursuant to the automatic authorization
until the Board enters a final order on the appeal notwithstanding the
provisions of 35 Ill. Adm. Code 705.204.
g) Newly regulated wastes and units.
1) The permittee is authorized to continue to manage wastes listed or
identified as hazardous under 35 Ill. Adm. Code 721, or to continue to
manage hazardous waste in units newly regulated as hazardous waste
management units, if each of the following is true:
A) The unit was in existence as a hazardous waste facility with
respect to the newly listed or characterized waste or newly
regulated waste management unit on the effective date of the final
rule listing or identifying the waste, or regulating the unit;
B) The permittee submits a Class 1 modification request on or before
the date on which the waste becomes subject to the new
requirements;
C) The permittee is in compliance with the applicable standards of
35 Ill. Adm. Code 725 and 726;
D) The permittee also submits a complete class 2 or 3 modification
request within 180 days after the effective date of the rule listing
or identifying the waste, or subjecting the unit to management
standards under 35 Ill. Adm. Code 724, 725 or 726; and
E) In the case of land disposal units, the permittee certifies that such
unit is in compliance with all applicable requirements of 35 Ill.
Adm. Code 725 for groundwater monitoring and financial
responsibility requirements on the date 12 months after the
effective date of the rule identifying or listing the waste as
hazardous, or regulating the unit as a hazardous waste
management unit. If the owner or operator fails to certify
compliance with all these requirements, the owner or operator
loses authority to operate under this Section.
11
2) New wastes or units added to a facility’s permit under this subsection do
not constitute expansions for the purpose of the 25 percent capacity
expansion limit for Class 2 modifications.
h) Military hazardous waste munitions treatment and disposal. The permittee is
authorized to continue to accept waste military munitions notwithstanding any
permit conditions barring the permittee from accepting off-site wastes, if each of
the following is true:
1) The facility was in existence as a hazardous waste facility and the facility
was already permitted to handle the waste military munitions on the date
when the waste military munitions became subject to hazardous waste
regulatory requirements;
2) On or before the date when the waste military munitions become subject
to hazardous waste regulatory requirements, the permittee submits a
Class 1 modification request to remove or amend the permit provision
restricting the receipt of off-site waste munitions; and
3) The permittee submits a complete Class 2 modification request within
180 days after the date when the waste military munitions became subject
to hazardous waste regulatory requirements.
i) Permit modification list. The Agency must maintain a list of all approved
permit modifications and must publish a notice once a year in a State-wide
newspaper that an updated list is available for review.
j) Combustion facility changes to meet federal 40 CFR 63 MACT standards. The
following procedures apply to hazardous waste combustion facility permit
modifications requested under Section 703.Appendix A, paragraph L(9).
1) Facility owners or operators must comply have complied with the federal
notification of intent to comply (NIC) requirements of 40 CFR
63.1210(b) and (c) before 63.1210 that was in effect prior to May 14,
2001, (see 40 CFR 63 (2000)) in order to request a permit modification
can be requested under this Section.
2) If the Agency does not act to either approve or deny the request within
90 days of receiving it, the request must be deemed approved. The
Agency may, at its discretion, extend this 90-day deadline one time for
up to 30 days by notifying the facility owner or operator in writing
before the 90 days has expired.
12
BOARD NOTE: Derived from 40 CFR 270.42(d) through (j) (2000), as amended at 65 Fed.
Reg. 42302 (July 10, 2000).
(Source: Amended at 26 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 regulation of certain hazardous waste Recycling Activities on a case-
by-case Basis
720.141 Procedures for case-by-case regulation of hazardous waste Recycling Activities
720.Appendix A Overview of 40 CFR, Subtitle C Regulations
13
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, 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. ________, effective ______________________.
SUBPART B: DEFINITIONS AND REFERENCES
Section 720.110 Definitions
When used in 35 Ill. Adm. Code 720 through 726 and 728 only, the following terms have the
meanings given below:
14
“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 of one or more electrically connected
electrochemical cells that 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.
15
“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
shall 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 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.
16
“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 35 Ill. Adm. Code
724.Subpart DD and 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.
“Corrective action management unit” or “CAMU” means an area within a facility
that is used only for managing remediation wastes for implementing corrective
action or cleanup at the facility.
BOARD NOTE: USEPA must also designate a CAMU until it grants this
authority to the Agency. See the note following 35 Ill. Adm. Code 724.652.
“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:
17
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);
The facility has received a RCRA permit from a state authorized by
USEPA pursuant to 40 CFR 271 (1999); or
The facility is regulated under 35 Ill. Adm. Code 721.106(c)(2) or
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, hexa, 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
18
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 which:
Is used for neutralizing wastes which are hazardous only because they
exhibit the corrosivity characteristic defined in 35 Ill. Adm. Code 721.122
or are listed in 35 Ill. Adm. Code 721.Subpart D only for this reason; and
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 35 Ill. Adm. Code
721.Subpart D and to each characteristic identified in 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
19
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:
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:
20
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:
21
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 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.
22
“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 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 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:
Meets the criteria for classification as a boiler, sludge dryer, or
carbon regeneration unit, nor
Is 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:
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,
23
violent reaction, toxic dusts, mists, fumes or gases, or flammable fumes or
gases.
(See 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
24
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”.)
25
“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 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
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.
26
“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 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 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, 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, as amended, have been completed.
“Mining overburden returned to the mine site” means any material overlying an
economic mineral deposit which is removed to gain access to that deposit and is
then used for reclamation of a surface mine.
27
“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 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 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.
28
(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,
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
29
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.
“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 contain
30
listed hazardous wastes or which themselves exhibit a hazardous waste
characteristic that are managed for the purpose of 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 basis.
31
“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 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 provide structural support.
“Tank system” means a hazardous waste storage or treatment tank and its
associated ancillary equipment and containment system.
32
“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-tetra-
chlorodibenzo-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 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:
A study in which a hazardous waste is subjected to a treatment process to
determine:
Whether the waste is amenable to the treatment process;
What pretreatment (if any) is required;
33
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.
34
“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:
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.
35
“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 is a hazardous waste as
defined in 35 Ill. Adm. Code 721.103, or treats or stores a wastewater
treatment sludge which 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 26 Ill. Reg. ________, effective ______________________)
36
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.
37
“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,
1916 Race Street, Philadelphia, PA 19103, 215-299-5400:
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 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 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.
38
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:
39
“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).
40
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:
41
“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 Information Center (RIC), 1235
Jefferson Davis Highway, first floor, Arlington, VA 22202 (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).
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 (2001)
10 CFR 20, Appendix B (2000) (2001)
10 CFR 71 (2001)
40 CFR 51.100(ii) (2000) (2001)
42
40 CFR 51, Appendix W (2000) (2001)
40 CFR 52.741, Appendix B (2000) (2001)
40 CFR 60 (2000), as amended at 65 Fed. Reg. 42297 (July 10, 2000)
(2001)
40 CFR 61, Subpart V (2000) (2001)
40 CFR 63 (2000) (2001), as amended at 65 Fed. Reg. 42296 (July 10,
2000) 66 Fed. Reg. 35087 (July 3, 2001), and 66 Fed. Reg. 52361
(October 15, 2001)
40 CFR 136 (2000), as amended at 65 Fed. Reg. 81295 (December 22,
2000) (2001)
40 CFR 142 (2000) (2001)
40 CFR 220 (2000) (2001)
40 CFR 232.2 (2000) (2001)
40 CFR 260.20 (2000) (2001)
40 CFR 264 (2000) (2001)
40 CFR 268.41 (1990)
40 CFR 268, Appendix IX (2000) (2001)
40 CFR 270.5 (2000) (2001)
40 CFR 302.4, 302.5, and 302.6 (2000) (2001)
40 CFR 761 (2000) (2001)
49 CFR 107 (2001)
49 CFR 171 (2000) (2001)
49 CFR 172 (2001)
43
49 CFR 173 (2000) (2001)
49 CFR 178 (2000) (2001)
49 CFR 179 (2001)
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 26 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
44
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
721.Appendix A Representative Sampling Methods
721.Appendix B Method 1311 Toxicity Characteristic Leaching Procedure (TCLP)
721.Appendix C 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)
721.Appendix G Basis for Listing Hazardous Wastes
721.Appendix H Hazardous Constituents
721.Appendix I Wastes Excluded by Administrative Action
Table A Wastes Excluded by U.S. EPA under 40 CFR 260.20 and 260.22 from
Non-Specific Sources
Table B Wastes Excluded by USEPA under 40 CFR 260.20 and 260.22 from
Specific Sources
Table C Wastes Excluded by U.S. EPA under 40 CFR 260.20 and 260.22 from
Commercial Chemical Products, Off-Specification Species, Container
Residues, and Soil Residues Thereof
Table D Wastes Excluded by the Board by Adjusted Standard
721.Appendix J Method of Analysis for Chlorinated Dibenzo-p-Dioxins and
Dibenzofurans (Repealed)
45
721.Appendix Y Table to Section 721.138
721.Appendix Z 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. ________, effective ______________________.
46
SUBPART A: GENERAL PROVISIONS
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:
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) Materials are solid waste if they are abandoned by being:
1) Disposed of; or
2) Burned or incinerated; or
3) Accumulated, stored or treated (but not recycled) before or in lieu of
being abandoned by being disposed of, burned or incinerated.
c) Materials are solid wastes if they are recycled--or accumulated, stored or treated
before recycling--as specified in subsections (c)(1) through (c)(4) of this Section
if they are:
1) Used in a manner constituting disposal.
A) Materials noted with a “yes” in column 1 of the table in
Appendix Z of this Part are solid wastes when they are:
i) Applied to or placed on the land in a manner that
constitutes disposal; or
47
ii) Used to produce products that are applied to or placed on
the land or are otherwise contained in products that are
applied to or placed on the land (in which cases the
product itself remains a solid waste).
B) However, commercial chemical products listed in Section
721.133 are not solid wastes if they are applied to the land and
that is their ordinary manner of use.
2) Burned for energy recovery.
A) Materials noted with a “yes” in column 2 of the table in
Appendix Z of this Part are solid wastes when they are:
i) Burned to recover energy;
ii) Used to produce a fuel or are otherwise contained in fuels
(in which case the fuel itself remains a solid waste);
iii) Contained in fuels (in which case the fuel itself remains a
solid waste).
B) However, commercial chemical products listed in Section
721.133 are not solid wastes if they are themselves fuels.
3) Reclaimed. Materials noted with a “yes” in column 3 of the table in
Appendix Z of this Part are solid wastes when reclaimed (except as
provided under Section 721.104(a)(17)). Materials noted with a “--” in
column 3 of Appendix Z of this Part are not solid wastes when reclaimed
(except as provided under Section 721.104(a)(17)).
4) Accumulated speculatively. Materials noted with “yes” in column 4 of
the table in Appendix Z of this Part are solid wastes when 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) Secondary materials fed to a halogen acid furnace that exhibit a
characteristic of a hazardous waste or are listed as a hazardous waste as
48
defined in Subpart C or D of this Part, except for brominated material
that meets the following criteria:
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 materials are ordinarily disposed of, burned, or
incinerated; or
ii) The materials contain toxic constituents listed in Appendix
H of this Part and these constituents are not ordinarily
found in raw materials or products for which the materials
substitute (or are found in raw materials or products in
smaller concentrations) and are not used or reused during
the recycling process; and
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) Materials are not solid wastes when they can be shown to be recycled by
being:
A) Used or reused as ingredients in an industrial process to make a
product, provided the materials are not being reclaimed; or
B) Used or reused as effective substitutes for commercial products;
or
C) Returned to the original process from which they are generated,
without first being reclaimed or land disposed. The material must
be returned as a substitute for feedstock materials. In cases
49
where the original process to which the material is returned is a
secondary process, the materials must be managed in such a
manner that there is no placement on the land. In cases where
thematerials the materials are generated and reclaimed within the
primary mineral processing industry, the conditions of the
exclusion found at Section 721.104(a)(17) apply rather than this
provision.
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) Materials used in a manner constituting disposal or used to
produce products that are applied to the land; or
B) Materials burned for energy recovery, used to produce a fuel, or
contained in fuels; or
C) Materials accumulated speculatively; or
D) Materials listed in subsections (d)(1) and (d)(2) of this Section.
f) Documentation of claims that materials are not solid wastes or are conditionally
exempt from regulation. Respondents in actions to enforce regulations
implementing Subtitle C of RCRA or Section 21 of the Environmental
Protection Act that raise a claim that a certain material is not a solid waste or
that the material is conditionally exempt from regulation must demonstrate that
there is a known market or disposition for the material and that they meet the
terms of the exclusion or exemption. In doing so, the person must provide
appropriate documentation (such as contracts showing that a second person uses
the material as an ingredient in a production process) to demonstrate that the
material is not a waste or that the material is exempt from regulation. In
addition, owners or operators of facilities claiming that they actually are
recycling materials must show that they have the necessary equipment to do so.
(Source: Amended at 26 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:
1) It is not excluded from regulation as a hazardous waste under Section
721.104(b); and
50
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)
It is a mixture of a solid waste and a hazardous waste that is listed
in Subpart D of this Part solely because it exhibits one or more of
the characteristics of hazardous waste identified in Subpart C of
this Part, unless the resultant mixture no longer exhibits any
characteristic of hazardous waste identified in Subpart C of this
Part, or unless the solid waste is excluded from regulation under
Section 721.104(b)(7) and the resultant mixture no longer exhibits
any characteristic of hazardous waste identified in Subpart C of
this Part for which the hazardous waste listed in Subpart D of this
Part was listed. (However, nonwastewater mixtures are still
subject to the requirements of 35 Ill. Adm. Code 728, even if
they no longer exhibit a characteristic at the point of land
disposal.)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.
51
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:
i) One or more of the following solvents listed in Section
721.131: carbon tetrachloride, tetrachloroethylene,
trichloroethylene, provided that the maximum total weekly
usage of these solvents (other than the amounts that can be
demonstrated not to be discharged to wastewater) divided
by the average weekly flow of wastewater into the
headworks of the facility’s wastewater treatment or
pretreatment system does not exceed 1 part per million;
ii) One or more of the following spent solvents listed in
Section 721.131: methylene chloride, 1,1,1-trichloro-
ethane, chlorobenzene, o-dichlorobenzene, cresols,
cresylic acid, nitrobenzene, toluene, methyl ethyl ketone,
carbon disulfide, isobutanol, pyridine, spent chlorofluoro-
carbon solvents, provided that the maximum total weekly
usage of these solvents (other than the amounts that can be
demonstrated not to be discharged to wastewater) divided
by the average weekly flow of wastewater into the
headworks of the facility’s wastewater treatment or
pretreatment system does not exceed 25 parts per million;
iii) One of the following wastes listed in Section 721.132,
provided that the wastes are discharged to the refinery oil
recovery sewer before primary oil/water/solids
separation: heat exchanger bundle cleaning sludge from
the petroleum refining industry (USEPA hazardous waste
no. K050), crude oil storage tank sediment from
petroleum refining operations (USEPA hazardous waste
number K169), clarified slurry oil tank sediment and/or
in-line filter/separation solids from petroleum refining
52
operations (USEPA hazardous waste number K170), spent
hydrotreating catalyst (USEPA hazardous waste number
K171), and spent hydrorefining catalyst (USEPA
hazardous waste number K172);
iv) A discarded commercial chemical product or chemical
intermediate listed in Section 721.133 arising from de
minimis losses of these materials from manufacturing
operations in which these materials are used as raw
materials or are produced in the manufacturing process.
For purposes of this subsection, “de minimis” losses
include those from normal material handling operations
(e.g., spills from the unloading or transfer of materials
from bins or other containers, leaks from pipes, valves, or
other devices used to transfer materials); minor leaks of
process equipment, storage tanks, or containers; leaks
from well-maintained pump packings and seals; sample
purgings; relief device discharges; discharges from safety
showers and rinsing and cleaning of personal safety
equipment; and rinsate from empty containers or from
containers that are rendered empty by that rinsing;
v) Wastewater resulting from laboratory operations
containing toxic (T) wastes listed in Subpart D of this
Part, provided that the annualized average flow of
laboratory wastewater does not exceed one percent of total
wastewater flow into the headworks of the facility’s
wastewater treatment or pretreatment system or provided
that the wastes’ combined annualized average
concentration does not exceed one part per million in the
headworks of the facility’s wastewater treatment or
pretreatment facility. Toxic (T) wastes used in
laboratories that are demonstrated not to be discharged to
wastewater are not to be included in this calculation;
vi) One or more of the following wastes listed in Section
721.132: wastewaters from the production of carbamates
and carbamoyl oximes (USEPA Hazardous Waste No.
K157), provided that the maximum weekly usage of
formaldehyde, methyl chloride, methylene chloride, and
triethylamine (including all amounts that cannot be
demonstrated to be reacted in the process, destroyed
through treatment, or recovered, i.e., what is discharged
53
or volatilized) divided by the average weekly flow of
process wastewater prior to any dilutions into the
headworks of the facility’s wastewater treatment system
does not exceed a total of 5 parts per million by weight; or
vii) Wastewaters derived from the treatment of one or more 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), provided, that the maximum
concentration of formaldehyde, methyl chloride,
methylene chloride, and triethylamine prior to any
dilutions into the headworks of the facility’s wastewater
treatment system does not exceed a total of 5 milligrams
per liter.
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
metalworking oils or fluids containing chlorinated
paraffins if they are processed through a tolling
arrangement as described in 35 Ill. Adm. Code 739.124(c)
to reclaim metalworking oils or fluids. The presumption
does apply to metalworking oils or fluids if such oils or
fluids are recycled in any other manner, or disposed.
ii) The rebuttable presumption does not apply to used oils
contaminated with chlorofluorocarbons (CFCs) removed
from refrigeration units where the CFCs are destined for
reclamation. The rebuttable presumption does apply to
used oils contaminated with CFCs that have been mixed
with used oil from sources other than refrigeration units.
54
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 (c) of this Section is not a hazardous
waste if it meets the following criteria:
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 (c) of this Section under 35 Ill. Adm.
Code 720.120 and 720.122.
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
55
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 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 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, smelting,
melting and refining furnaces (including pyrometallurgical
devices such as cupolas, reverberator furnaces, sintering
machines, roasters, and foundry furnaces), and other furnaces
designated by the Agency pursuant to that definition.
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:
56
Constituent
Maximum for any single
composite sample (mg/L)
Generic exclusion levels for K061 and K062
nonwastewater HTMR residues.
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
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
57
CFR 268 requirements) for K061, K062, or F006 HTMR
residues that meet the generic exclusion levels for all
constituents and do not exhibit any characteristics and
which are sent to RCRA Subtitle D (municipal solid waste
landfill) units. 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 unit 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 calendar year, but no later than
December 31. The notification must include the following
information: the name and address of the nonhazardous
waste management unit receiving the waste shipment; the
USEPA hazardous waste number and treatability group at
the initial point of generation; and the treatment standards
applicable to the waste at the initial point of generation.
The certification must be signed by an authorized
representative and must state as follows:
“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).
58
BOARD NOTE: This subsection would normally correspond with 40 CFR
261.3(e), a subsection which 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 720, 721 to 726, 728, or 730:
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 35 Ill. Adm. Code 728.Table F; 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; or
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 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
59
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 35 Ill. Adm.
Code 726.Subpart N (i.e., it is “eligible radioactive mixed waste”).
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 26 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.
60
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, special nuclear, or 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
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:
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 twelve months without being reclaimed; and
D) The reclaimed material is not used to produce a fuel or used to
produce products that are used in a manner constituting disposal.
61
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 water borne
plants in the production process for their original intended
purpose;
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 35 Ill. Adm. Code 725.Subpart W, regardless
of whether the plant generates a total of less than 100
kg/month of hazardous waste; and
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
62
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 shall 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 shall 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,
byproducts 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
63
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 section. Residuals
generated from processing or recycling materials excluded under
this subsection (a)(12)(A), where such materials as generated
would have otherwise met a listing under Subpart D of this Part,
are designated as USEPA hazardous waste number F037 listed
wastes when disposed of or intended for disposal.
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,
and nickel-cadmium batteries and lithium batteries.
64
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) Secondary
Spent materials (i.e., sludges, by-products, and 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:
A) The
secondary
spent material is legitimately recycled to recover
minerals, acids, cyanide, water, or other values;
B) The
secondary
spent material is not accumulated speculatively;
C) Except as provided in subsection (a)(16)(D) (a)(17)(D) of this
Section, the secondary 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
secondary 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 which may be subject to wind
dispersal, the owner or operator must operate the unit in a
manner that controls fugitive dust. A tank, container, or building
must be designed, constructed, and operated to prevent significant
releases to the environment of these materials.
D) The Agency shall must allow by permit that solid mineral
processing secondary spent materials only may be placed on pads,
rather than in tanks, containers, or buildings if the facility owner
65
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 secondary 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 shall 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 secondary 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 secondary 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 which
controls fugitive dust; and they must have integrity
assurance through inspections and maintenance programs.
iii) Before making a determination under this subsection
(a)(16)(D) (a)(17)(D), the Agency shall 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 35 Ill. Adm. Code 703.Subpart D
for the RCRA Subtitle C permit public notice
requirements.
66
E) The owner or operator provides a notice to the Agency,
identifying 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 secondary 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, byproducts by-products, or spent materials, including
wastewater) from normal organic chemical manufacturing
operations, as well as oil recovered from organic chemical
manufacturing processes.
67
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, or accumulated speculatively as defined in
Section 721.101(c).
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 shall must not be deemed to be treating,
storing, disposing of, or otherwise managing hazardous wastes for the
purposes of regulation under this Part, if such facility:
A) Receives and burns only:
i) Household waste (from single and multiple dwellings,
hotels, motels, and other residential sources); and
ii) Solid waste from commercial or industrial sources that
does not contain hazardous waste; and
B) Such facility does not accept hazardous waste and the owner or
operator of such facility has established contractual requirements
or other appropriate notification or inspection procedures to
assure that hazardous wastes are not received at or burned in such
facility.
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 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
68
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 (Sections
721.124 and 721.Appendix B) because chromium is present or
which are listed in Subpart D of this Part due to the presence of
chromium, that do not fail the test for the toxicity characteristic
for any other constituent or which are not listed due to the
presence of any other constituent, and that do not fail the test for
any other characteristic, if it is shown by a waste generator or by
waste generators that:
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.
69
B) Specific wastes that meet the standard in subsection (b)(6)(A) of
this Section (so long as they do not fail the test for the toxicity
characteristic for any other constituent and do not exhibit any
other characteristic) are:
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
70
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;
71
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.
72
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 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.
73
15) Leachate or gas condensate collected from landfills where certain solid
wastes have been disposed of, under certain circumstances:
A) The following conditions must be fulfilled:
i) The solid wastes disposed of would meet one or more of
the listing descriptions for Hazardous Waste Codes K169,
K170, K171, and K172 if these wastes had been the
following USEPA hazardous waste numbers that is
generated after the effective date of the listing (January
19, 1999); listed for the waste:
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.
B)
After February 13, 2001, leachate Leachate or gas condensate
derived from K169, K170, K171, or K172 will no longer be
exempt if it is stored or managed in a surface impoundment prior
to discharge. After November 21, 2003, leachate or gas
condensate derived from K176, K177, or K178 will no longer be
exempt if it is stored or managed in a surface impoundment prior
to discharge. There is one exception: if the surface
impoundment is used to temporarily store leachate or gas
74
condensate in response to an emergency situation (e.g., shutdown
of wastewater treatment system), provided the impoundment has
a double liner, and provided the leachate or gas condensate is
removed from the impoundment and continues to be managed in
compliance with the conditions of this subsection (b)(15) of this
Section after the emergency ends.
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, 705, and 722 through 725, and 728 or to the notification requirements of
section 3010 of RCRA until it exits the unit in which it was generated, unless
the unit is a surface impoundment, or unless the hazardous waste remains in the
unit more than 90 days after the unit ceases to be operated for manufacturing or
for storage or transportation of product or raw materials.
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,
705, and 722 through 728. The sample qualifies when:
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
75
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 shall must:
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;
76
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:
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 wastestream 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
77
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;
iii) Documentation showing: 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:
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
78
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: 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 shall
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 wastestream 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 shall must include
information regarding the reason for the failure or
79
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, 705, 722 through 726, and 728 or
to the notification requirements of Section 3010 of the Resource Conservation
and Recovery Act, provided that the requirements of subsections (f)(1) through
(f)(11) of this Section are met. A mobile treatment unit may qualify as a testing
facility subject to subsections (f)(1) through (f)(11) of this Section. Where a
group of mobile treatment units are located at the same site, the limitations
specified in subsections (f)(1) through (f)(11) of this Section apply to the entire
group of mobile treatment units collectively as if the group were one mobile
treatment unit.
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
80
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
81
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:
82
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 26 Ill. Reg. ________, effective ______________________)
SUBPART C: CHARACTERISTICS OF HAZARDOUS WASTE
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”, U.S. EPA USEPA Publication SW-846, as incorporated by reference
in 35 Ill. Adm. Code 720.111, the extract from a representative sample of the
waste contains any of the contaminants listed in the table in subsection (b) below
at a concentration equal to or greater than the respective value given in that
table. Where the waste contains less than 0.5 percent filterable solids, the waste
itself, after filtering using the methodology outlined in Method 1311, is
considered to be the extract for the purpose of this Section.
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 U.S. EPA
Hazardous Waste Number USEPA hazardous waste number specified in the
following table that corresponds to the toxic contaminant causing it to be
hazardous.
83
MAXIMUM CONCENTRATION OF CONTAMINANTS FOR
THE TOXICITY CHARACTERISTIC
U.S. EPA
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 4
200.0
D024 m-Cresol
108-39-4
4
200.0
D025 p-Cresol
106-44-5
4
200.0
D026 Cresol
4
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
84
D029 1,1-Dichloroethylene
75-35-4
0.7
D030 2,4-Dinitrotoluene 121-14-2 3
0.13
D012 Endrin
72-20-8
0.02
D031
Heptachlor (and its
epoxide)
76-44-8
0.008
D032 Hexachlorobenzene
118-74-1
3
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
3
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:
3 Quantitation limit is greater than the calculated regulatory level. The
quantitation limit therefore becomes the regulatory level.
4 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 26 Ill. Reg. ________, effective ______________________)
85
SUBPART D: LISTS OF HAZARDOUS WASTE
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:
K001
Bottom sediment sludge from the treatment of wastewaters from
wood preserving processes that use creosote or pentachloro-
phenol.
(T)
Inorganic Pigments:
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)
86
Organic Chemicals:
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)
87
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-trichloro-
ethane.
(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)
88
K115
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-di-
methylhydrazine (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 di-
nitrotoluene.
(T)
K113
Condensed liquid light ends from the purification of toluenedi-
amine 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)
Heavy ends from the purification of toluenediamine in the
production of toluenediamine via hydrogenation of di-
nitrotoluene.
(T)
K116
Organic condensate from the solvent recovery column in the
production of toluene diisocyanate via phosgenation of
toluenediamine.
(T)
89
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) they are disposed of in a
subtitle C or non- hazardous non-hazardous landfill licensed or
permitted by the state or federal government; (2) they are not
otherwise placed on the land prior to final disposal; and (3) the
generator maintains documentation demonstrating that the waste
(T)
90
was either disposed of in an on-site landfill or consigned to a
transporter or disposal facility that provided a written
commitment to dispose of the waste in an off-site landfill. Upon
a showing by the government that a respondent in any
enforcement action brought to enforce the requirements of
Subtitle C of this Part managed wastewater treatment sludges
from the production of vinyl chloride monomer or ethylene
dichloride, the respondent must demonstrate that it meets the
conditions of the exclusion that are set forth above. In doing so,
the respondent must provide appropriate documentation that the
terms of the exclusion were met (e.g., contracts between the
generator and the landfill owner or operator, invoices
documenting delivery of waste to landfill, etc.).
K175
Wastewater treatment sludges from the production of vinyl
chloride monomer using mercuric chloride catalyst in an
acetylene-based process.
(T)
Inorganic Chemicals:
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)
91
Pesticides:
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 tetra-
chlorobenzene 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)
92
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 ethylenebis-
dithiocarbamic 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 ethylenebisdi-
thiocarbamic 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:
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:
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)
93
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:
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:
K088
Spent potliners from primary aluminum reduction.
(T)
Secondary Lead:
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)
94
Veterinary Pharmaceuticals:
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:
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:
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)
95
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
α
- (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
α
- (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
α
- (or methyl-) chlorinated
toluenes, ring-chlorinated toluenes, benzoyl chlorides, and
compounds with mixtures of these functional groups.
(T)
(Source: Amended at 26 Ill. Reg. ________, effective ______________________)
Section 721.Appendix G Basis for Listing Hazardous Wastes
USEPA hazard-
ous 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.
96
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.
97
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, and 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 35 Ill. Adm. Code
728.Table B (Constituent Concentrations in Waste).
K001
Pentachlorophenol, phenol, 2-chlorophenol, p-chloro-m-cresol, 2,4-
dimethylphenol, 2,4- dinitrophenol, trichlorophenols, tetrachlorophenols,
2,4- dinitrophenol, cresosote 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.
98
K017
Epichlorohydrin, chloroethers [bis(chloromethyl) ether and bis- (2-
chloroethyl) ethers], trichloropropane, dichloropropanols.
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.
99
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.
100
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.
101
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- octachlorodibenzo-
furan (OCDF), all pentachlorodibenzofurans (PeCDFs), all tetrachloro-
dibenzo-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 26 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 724
STANDARDS FOR OWNERS AND OPERATORS OF HAZARDOUS
WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES
SUBPART A: GENERAL PROVISIONS
Section
724.101 Purpose, Scope, and Applicability
724.103 Relationship to Interim Status Standards
SUBPART B: GENERAL FACILITY STANDARDS
Section
724.110 Applicability
724.111 Identification Number
724.112 Required Notices
102
724.113 General Waste Analysis
724.114 Security
724.115 General Inspection Requirements
724.116 Personnel Training
724.117 General Requirements for Ignitable, Reactive or Incompatible Wastes
724.118 Location Standards
724.119 Construction Quality Assurance Program
SUBPART C: PREPAREDNESS AND PREVENTION
Section
724.130 Applicability
724.131 Design and Operation of Facility
724.132 Required Equipment
724.133 Testing and Maintenance of Equipment
724.134 Access to Communications or Alarm System
724.135 Required Aisle Space
724.137 Arrangements with Local Authorities
SUBPART D: CONTINGENCY PLAN AND EMERGENCY PROCEDURES
Section
724.150 Applicability
724.151 Purpose and Implementation of Contingency Plan
724.152 Content of Contingency Plan
724.153 Copies of Contingency Plan
724.154 Amendment of Contingency Plan
724.155 Emergency Coordinator
724.156 Emergency Procedures
SUBPART E: MANIFEST SYSTEM, RECORDKEEPING AND
REPORTING
Section
724.170 Applicability
724.171 Use of Manifest System
724.172 Manifest Discrepancies
724.173 Operating Record
724.174 Availability, Retention
and Disposition of Records
724.175 Annual Report
724.176 Unmanifested Waste Report
724.177 Additional Reports
SUBPART F: RELEASES FROM SOLID WASTE MANAGEMENT UNITS
Section
724.190 Applicability
103
724.191 Required Programs
724.192 Groundwater Protection Standard
724.193 Hazardous Constituents
724.194 Concentration Limits
724.195 Point of Compliance
724.196 Compliance Period
724.197 General Groundwater
Monitoring Requirements
724.198 Detection Monitoring Program
724.199 Compliance Monitoring Program
724.200 Corrective Action Program
724.201 Corrective Action for Solid Waste Management Units
SUBPART G: CLOSURE AND POST-CLOSURE CARE
Section
724.210 Applicability
724.211 Closure Performance Standard
724.212 Closure Plan; Amendment of Plan
724.213 Closure; Time Allowed For Closure
724.214 Disposal or Decontamination of Equipment, Structures and Soils
724.215 Certification of Closure
724.216 Survey Plat
724.217 Post-closure Care and Use of Property
724.218 Post-Closure Care Plan; Amendment of Plan
724.219 Post-closure Notices
724.220 Certification of Completion of Post-closure Care
SUBPART H: FINANCIAL REQUIREMENTS
Section
724.240 Applicability
724.241 Definitions of Terms As Used In This Subpart
724.242 Cost Estimate for Closure
724.243 Financial Assurance for Closure
724.244 Cost Estimate for Post-closure Care
724.245 Financial Assurance
for Post-closure Care
724.246 Use of a Mechanism for Financial Assurance of Both Closure and Post-closure
Care
724.247 Liability Requirements
724.248 Incapacity of Owners or Operators, Guarantors or Financial Institutions
724.251 Wording of the Instruments
SUBPART I: USE AND MANAGEMENT OF CONTAINERS
Section
724.270 Applicability
104
724.271 Condition of Containers
724.272 Compatibility of Waste With Container
724.273 Management
of Containers
724.274 Inspections
724.275 Containment
724.276 Special Requirements for Ignitable or Reactive Waste
724.277 Special Requirements for Incompatible Wastes
724.278 Closure
724.279 Air Emission Standards
SUBPART J: TANK SYSTEMS
Section
724.290 Applicability
724.291 Assessment of Existing Tank System’s Integrity
724.292 Design and Installation of New Tank Systems or Components
724.293 Containment and Detection of Releases
724.294 General Operating Requirements
724.295 Inspections
724.296 Response to Leaks or Spills and Disposition of Leaking or unfit-for-use Tank
Systems
724.297 Closure and Post-Closure Care
724.298 Special Requirements for Ignitable or Reactive Waste
724.299 Special Requirements for Incompatible Wastes
724.300 Air Emission Standards
SUBPART K: SURFACE IMPOUNDMENTS
Section
724.320 Applicability
724.321 Design and Operating Requirements
724.322 Action Leakage Rate
724.323 Response Actions
724.326 Monitoring and Inspection
724.327 Emergency Repairs; Contingency Plans
724.328 Closure and Post-closure Care
724.329 Special Requirements for Ignitable or Reactive Waste
724.330 Special Requirements for Incompatible Wastes
724.331 Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026
and F027
724.332 Air Emission Standards
SUBPART L: WASTE PILES
Section
724.350 Applicability
105
724.351 Design and Operating Requirements
724.352 Action Leakage Rate
724.353 Response Action Plan
724.354 Monitoring and Inspection
724.356 Special Requirements for Ignitable or Reactive Waste
724.357 Special Requirements for Incompatible Wastes
724.358 Closure and Post-closure Care
724.359 Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026
and F027
SUBPART M: LAND TREATMENT
Section
724.370 Applicability
724.371 Treatment Program
724.372 Treatment Demonstration
724.373 Design and Operating Requirements
724.376 Food-chain Crops
724.378 Unsaturated Zone Monitoring
724.379 Recordkeeping
724.380 Closure and Post-closure Care
724.381 Special Requirements for Ignitable or Reactive Waste
724.382 Special Requirements for Incompatible Wastes
724.383 Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026
and F027
SUBPART N: LANDFILLS
Section
724.400 Applicability
724.401 Design and Operating Requirements
724.402 Action Leakage Rate
724.403 Monitoring and Inspection
724.404 Response Actions
724.409 Surveying and Recordkeeping
724.410 Closure and Post-closure Care
724.412 Special Requirements for Ignitable or Reactive Waste
724.413 Special Requirements for Incompatible Wastes
724.414 Special Requirements for Bulk and Containerized Liquids
724.415 Special Requirements for Containers
724.416 Disposal of Small Containers of Hazardous Waste in Overpacked Drums (Lab
Packs)
724.417 Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026
and F027
106
SUBPART O: INCINERATORS
Section
724.440 Applicability
724.441 Waste Analysis
724.442 Principal Organic Hazardous Constituents (POHCs)
724.443 Performance Standards
724.444 Hazardous Waste Incinerator Permits
724.445 Operating Requirements
724.447 Monitoring and Inspections
724.451 Closure
SUBPART S: CORRECTIVE ACTION SPECIAL PROVISIONS FOR SOLID
WASTE MANAGEMENT UNITS CLEANUP
Section
724.650 Applicability of Corrective Action Management Unit Regulations
724.652651 Grandfathered
Corrective Action Management Units
724.652 Corrective Action Management Units
724.653 Temporary Units
724.654 Staging Piles
724.655 Disposal of CAMU-Eligible Wastes in Permitted Hazardous Waste Landfills
SUBPART W: DRIP PADS
Section
724.670 Applicability
724.671 Assessment of existing drip pad integrity
724.672 Design and installation of new drip pads
724.673 Design and operating requirements
724.674 Inspections
724.675 Closure
SUBPART X: MISCELLANEOUS UNITS
Section
724.700 Applicability
724.701 Environmental Performance Standards
724.702 Monitoring, Analysis, Inspection, Response, Reporting and Corrective Action
724.703 Post-closure Care
SUBPART AA: AIR EMISSION STANDARDS FOR PROCESS VENTS
Section
724.930 Applicability
724.931 Definitions
724.932 Standards: Process Vents
724.933 Standards: Closed-Vent Systems and Control Devices
107
724.934 Test Methods
and Procedures
724.935 Recordkeeping requirements
724.936 Reporting Requirements
SUBPART BB: AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS
Section
724.950 Applicability
724.951 Definitions
724.952 Standards: Pumps in Light Liquid Service
724.953 Standards: Compressors
724.954 Standards: Pressure Relief Devices in Gas/Vapor Service
724.955 Standards: Sampling Connecting Systems
724.956 Standards: Open-ended Valves or Lines
724.957 Standards: Valves in Gas/Vapor or Light Liquid Service
724.958 Standards: Pumps, Valves, Pressure Relief Devices and Other Connectors
724.959 Standards:
Delay of Repair
724.960 Standards: Closed-vent Systems and Control Devices
724.961 Alternative Percentage Standard for Valves
724.962 Skip Period Alternative for Valves
724.963 Test Methods
and Procedures
724.964 Recordkeeping Requirements
724.965 Reporting Requirements
SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE
IMPOUNDMENTS, AND CONTAINERS
Section
724.980 Applicability
724.981 Definitions
724.982 Standards: General
724.983 Waste Determination Procedures
724.984 Standards: Tanks
724.985 Standards: Surface Impoundments
724.986 Standards:
Containers
724.987 Standards: Closed-vent Systems and Control Devices
724.988 Inspection and Monitoring Requirements
724.989 Recordkeeping Requirements
724.990 Reporting Requirements
724.991 Alternative Control
Requirements for Tanks
SUBPART DD: CONTAINMENT BUILDINGS
Section
724.1100 Applicability
724.1101 Design and operating standards
108
724.1102 Closure and Post-closure Care
SUBPART EE: HAZARDOUS WASTE MUNITIONS AND EXPLOSIVES
STORAGE
Section
724.1200 Applicability
724.1201 Design and Operating Standards
724.1202 Closure and Post-Closure Care
724.Appendix A Recordkeeping Instructions
724.Appendix B EPA Report Form and Instructions (Repealed)
724.Appendix D Cochran’s Approximation to the Behrens-Fisher Student’s T-Test
724.Appendix E Examples of Potentially Incompatible Waste
724.Appendix I Groundwater Monitoring List
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. 14059, effective October 12, 1983; amended in
R84-9 at 9 Ill. Reg. 11964, effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 1136,
effective January 2, 1986; amended in R86-1 at 10 Ill. Reg. 14119, effective August 12, 1986;
amended in R86-28 at 11 Ill. Reg. 6138, effective March 24, 1987; amended in R86-28 at 11
Ill. Reg. 8684, effective April 21, 1987; amended in R86-46 at 11 Ill. Reg. 13577, effective
August 4, 1987; amended in R87-5 at 11 Ill. Reg. 19397, effective November 12, 1987;
amended in R87-39 at 12 Ill. Reg. 13135, effective July 29, 1988; amended in R88-16 at 13
Ill. Reg. 458, effective December 28, 1988; amended in R89-1 at 13 Ill. Reg. 18527, effective
November 13, 1989; amended in R90-2 at 14 Ill. Reg. 14511, effective August 22, 1990;
amended in R90-10 at 14 Ill. Reg. 16658, effective September 25, 1990; amended in R90-11 at
15 Ill. Reg. 9654, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14572, effective
October 1, 1991; amended in R91-13 at 16 Ill. Reg. 9833, effective June 9, 1992; amended in
R92-1 at 16 Ill. Reg. 17702, effective November 6, 1992; amended in R92-10 at 17 Ill. Reg.
5806, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20830, effective November
22, 1993; amended in R93-16 at 18 Ill. Reg. 6973, effective April 26, 1994; amended in R94-
7 at 18 Ill. Reg. 12487, effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17601,
effective November 23, 1994; amended in R95-6 at 19 Ill. Reg. 9951, effective June 27, 1995;
amended in R95-20 at 20 Ill. Reg. 11244, effective August 1, 1996; amended in R96-10/R97-
3/R97-5 at 22 Ill. Reg. 636, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg.
7638, effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17972,
effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 2186, effective
January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9437, effective July 26, 1999; amended
in R00-5 at 24 Ill. Reg. 1146, effective January 6, 2000; amended in R00-13 at 24 Ill. Reg.
9833, effective June 20, 2000; expedited correction at 25 Ill. Reg. 5115, effective June 20,
109
2000; amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. ________, effective
______________________.
SUBPART O: INCINERATORS
Section 724.440 Applicability
a) The regulations in this Subpart apply to owners and operators of hazardous
waste incinerators (as defined in 35 Ill. Adm. Code 720.110), except as Section
724.101 provides otherwise.
b) Integration of the MACT standards.
1) Except as provided by subsection subsections (b)(2) and (b)(3) of this
Section, the standards of this Part no longer apply when an owner or
operator 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(d),
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 MACT standards of 40 CFR 63, Subpart EEE do not replace the
closure requirements of Section 724.451 or the applicable requirements
of Subparts A through H, BB, and CC of this Part.
3) The particulate matter standard of Section 724.443(c) remains in effect
for incinerators that elect to comply with the alternative to the particulate
matter standard of 40 CFR 63.1206(b)(14), incorporated by reference in
35 Ill. Adm. Code 720.111.
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:
110
Under [the this approach adopted by USEPA as a] final rule. . . ,
MACT air emissions and related operating requirements are to be
included in title 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).
64 Fed Reg. 52828, 52975 (Sept. 30,1999).
c) After consideration of the waste analysis included with Part B of the permit
application, the Agency, in establishing the permit conditions, must exempt the
applicant from all requirements of this Subpart except Section 724.441 (Waste
Analysis) and Section 724.451 (Closure):
1) If the Agency finds that the waste to be burned is:
A) 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;
B) 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 Section 721.123(a)(4) and
(5), and will not be burned when other hazardous wastes are
present in the combustion zone;
C) A hazardous waste solely because it possesses the characteristic of
ignitability, as determined by the test for characteristics of
hazardous wastes under Subpart C of 35 Ill. Adm. Code 721; or
D) A hazardous waste solely because it possesses any of the
reactivity characteristics described by 35 Ill. Adm. Code
721.123(a)(1), (2), (3), (6), (7) and (8) and will not be burned
when other hazardous wastes are present in the combustion zone;
and
2) If the waste analysis shows that the waste contains none of the hazardous
constituents listed in Subpart H of 35 Ill. Adm. Code 721 that would
reasonably be expected to be in the waste.
111
d) If the waste to be burned is one that is described by subsection (b)(1)(A),
(b)(1)(B), (b)(1)(C), or (b)(1)(D) of this Section and contains insignificant
concentrations of the hazardous constituents listed in Subpart H of 35 Ill. Adm.
Code 721, then the Agency may, in establishing permit conditions, exempt the
applicant from all requirements of this Subpart, except Section 724.441 (Waste
Analysis) and Section 724.451 (Closure), after consideration of the waste
analysis included with Part B of the permit application, unless the Agency finds
that the waste will pose a threat to human health or the environment when
burned in an incinerator.
e) The owner or operator of an incinerator may conduct trial burns subject only to
the requirements of 35 Ill. Adm. Code 703.222 through 703.225 (short-term
and incinerator permits).
(Source: Amended at 26 Ill. Reg. ________, effective ______________________)
SUBPART S: CORRECTIVE ACTION SPECIAL PROVISIONS FOR SOLID
WASTE MANAGEMENT UNITS CLEANUP
Section 724.650 Applicability of Corrective Action Management Unit Regulations
a) Except as provided in subsection (b) of this Section, a CAMU is subject to the
requirements of Section 724.652.
b) A CAMU that is approved before April 22, 2002, or for which substantially
complete applications (or equivalents) were submitted to the Agency on or
before November 20, 2000, is subject to the requirements in Section 724.651
for a grandfathered CAMU. Within a grandfathered CAMU, CAMU waste,
activities, and design will not be subject to the standards in Section 724.652, so
long as the waste, activities, and design remain within the general scope of the
CAMU, as approved.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 724.652
Corrective Action Management Units
Section 724.651 Grandfathered Corrective Action Management Units
a) To implement remedies under Section 724.201 or RCRA section 3008(h), or to
implement remedies at a permitted facility that is not subject to Section 724.201,
the Agency may designate an area at the facility as a corrective action
management unit, as defined in 35 Ill. Adm. Code 720.110, in accordance with
the requirements of this Section. “Corrective action management unit” or
112
“CAMU” means an area within a facility that is used only for managing
remediation wastes for implementing corrective action or cleanup at that facility.
A CAMU must be located within the contiguous property under the control of the
owner or operator where the wastes to be managed in the CAMU originated. One
or more CAMUs may be designated at a facility.
1) Placement of remediation wastes into or within a CAMU does not
constitute land disposal of hazardous wastes.
2) Consolidation or placement of remediation wastes into or within a
CAMU does not constitute creation of a unit subject to minimum
technology requirements.
b) Designation of a CAMU.
1) The Agency may designate a regulated unit (as defined in Section
724.190(a)(2)) as a CAMU, or it may incorporate a regulated unit into a
CAMU, if:
A) The regulated unit is closed or closing, meaning it has begun the
closure process under Section 724.213 or 35 Ill. Adm. Code
725.213; and
B) Inclusion of the regulated unit will enhance implementation of
effective, protective, and reliable remedial actions for the facility.
2) The requirements of Subparts F, G, and H and the unit-specific
requirements of this Part or the 35 Ill. Adm. Code 725 requirements that
applied to that regulated unit will continue to apply to that portion of the
CAMU after incorporation into the CAMU.
c) The Agency shall must designate a CAMU in accordance with the following
factors:
1) The CAMU shall must facilitate the implementation of reliable, effective,
protective, and cost-effective remedies;
2) Waste management activities associated with the CAMU shall must not
create unacceptable risks to humans or to the environment resulting from
exposure to hazardous wastes or hazardous constituents;
3) The CAMU shall must include uncontaminated areas of the facility only
if including such areas for the purpose of managing remediation waste is
113
more protective than managing such wastes at contaminated areas of the
facility;
4) Areas within the CAMU where wastes remain in place after its closure
shall must be managed and contained so as to minimize future releases to
the extent practicable;
5) The CAMU shall must expedite the timing of remedial activity
implementation, when appropriate and practicable;
6) The CAMU shall must enable the use, when appropriate, of treatment
technologies (including innovative technologies) to enhance the long-term
effectiveness of remedial actions by reducing the toxicity, mobility, or
volume of wastes that will remain in place after closure of the CAMU;
and
7) The CAMU shall must, to the extent practicable, minimize the land area
of the facility upon which wastes will remain in place after closure of the
CAMU.
d) The owner or operator shall must provide sufficient information to enable the
Agency to designate a CAMU in accordance with the standards of this Section.
e) The Agency shall must specify in the permit the requirements applicable to a
CAMU, including the following:
1) The areal configuration of the CAMU.
2) Requirements for remediation waste management, including the
specification of applicable design, operation, and closure requirements.
3) Requirements for groundwater monitoring that are sufficient to:
A) Continue to detect and to characterize the nature, extent,
concentration, direction, and movement of existing releases of
hazardous constituents in groundwater from sources located
within the CAMU; and
B) Detect and subsequently characterize releases of hazardous
constituents to groundwater that may occur from areas of the
CAMU in which wastes will remain in place after closure of the
CAMU.
114
4) Closure and post-closure care requirements.
A) Closure of a CAMU shall must:
i) Minimize the need for further maintenance; and
ii) Control, minimize, or eliminate, to the extent necessary to
protect human health and the environment, for areas
where wastes remain in place, post-closure escape of
hazardous waste, hazardous constituents, leachate,
contaminated runoff, or hazardous waste decomposition
products to the ground, to surface waters, or to the
atmosphere.
B) Requirements for closure of a CAMU shall must include the
following, as appropriate:
i) Requirements for excavation, removal, treatment, or
containment of wastes;
ii) For areas in which wastes will remain after closure of the
CAMU, requirements for the capping of such areas; and
iii) Requirements for the removal and decontamination of
equipment, devices, and structures used in remediation
waste management activities within the CAMU.
C) In establishing specific closure requirements for a CAMU under
this subsection (c) (e), the Agency shall must consider the
following factors:
i) The characteristics of the CAMU;
ii) The volume of wastes that remain in place after closure;
iii) The potential for releases from the CAMU;
iv) The physical and chemical characteristics of the waste;
v) The hydrological and other relevant environmental
conditions at the facility that may influence the migration
of any potential or actual releases; and
115
vi) The potential for exposure of humans and environmental
receptors if releases were to occur from the CAMU.
D) Post-closure care requirements as necessary to protect human
health and the environment, including, for areas where wastes
will remain in place, monitoring and maintenance activities and
the frequency with which such activities shall must be performed
to ensure the integrity of any cap, final cover, or other
containment system.
f) The Agency shall must document the rationale for designating the CAMU and
shall must make such documentation available to the public.
g) Incorporation of a CAMU into an existing permit must be approved by the
Agency according to the procedures for Agency-initiated permit modifications
under 35 Ill. Adm. Code 703.270 through 703.273 or according to the permit
modification procedures of 35 Ill. Adm. Code 703.283.
h) The designation of a CAMU does not change the Agency’s existing authority to
address clean-up cleanup levels, media-specific points of compliance to be
applied to remediation at a facility, or other remedy selection decisions.
BOARD NOTE: USEPA promulgated this provision pursuant to HSWA provisions of RCRA
Subtitle C. Since the federal provision became immediately effective in Illinois, and until
USEPA authorizes this Illinois provision, an owner or operator must seek CAMU
authorization from USEPA Region V, as well as authorization from the Agency under this
provision.
(Source: Section 724.651 renumbered from Section 724.652 and amended at 26 Ill. Reg.
________, effective ______________________)
Section 724.652 Corrective Action Management Units
a) To implement remedies under Section 724.201 or RCRA section 3008(h), or to
implement remedies at a permitted facility that is not subject to Section 724.201,
the Agency may designate an area at the facility as a corrective action
management unit under the requirements in this Section. “Corrective action
management unit” or “CAMU” means an area within a facility that is used only
for managing CAMU-eligible wastes for implementing corrective action or
cleanup at that facility. A CAMU must be located within the contiguous
property under the control of the owner or operator where the wastes to be
managed in the CAMU originated. One or more CAMUs may be designated at
a facility.
116
1) “CAMU-eligible waste” means:
A) All solid and hazardous wastes, and all media (including
groundwater, surface water, soils, and sediments) and debris, that
are managed for implementing cleanup. As-generated wastes
(either hazardous or non-hazardous) from ongoing industrial
operations at a site are not CAMU-eligible wastes.
B) Wastes that would otherwise meet the description in subsection
(a)(1)(A) of this Section are not CAMU-eligible waste where:
i) The wastes are hazardous waste found during cleanup in
intact or substantially intact containers, tanks, or other
non-land-based units found above ground, unless the
wastes are first placed in the tanks, containers, or non-
land-based units as part of cleanup, or the containers or
tanks are excavated during the course of cleanup; or
ii) The Agency makes the determination in subsection (a)(2)
of this Section to prohibit the wastes from management in
a CAMU.
C) Notwithstanding subsection (a)(1)(A) of this Section, where
appropriate, as-generated non-hazardous waste may be placed in a
CAMU where such waste is being used to facilitate treatment or
the performance of the CAMU.
2) The Agency must prohibit the placement of waste in a CAMU where the
Agency determines that the wastes have not been managed in compliance
with applicable land disposal treatment standards of 35 Ill. Adm. Code
728, applicable unit design requirements of this Part or 35 Ill. Adm.
Code 725, or other applicable requirements of this Subtitle G, and that
the non-compliance likely contributed to the release of the waste.
3) Prohibition against placing liquids in a CAMU.
A) The placement of bulk or noncontainerized liquid hazardous
waste or free liquids contained in hazardous waste (whether or
not sorbents have been added) in any CAMU is prohibited except
where placement of such wastes facilitates the remedy selected for
the waste.
117
B) The requirements in Section 724.414(d) for placement of
containers holding free liquids in landfills apply to placement in a
CAMU except where placement facilitates the remedy selected
for the waste.
C) The placement of any liquid which is not a hazardous waste in a
CAMU is prohibited unless such placement facilitates the remedy
selected for the waste or a demonstration is made pursuant to
Section 724.414(f).
D) The absence or presence of free liquids in either a containerized
or a bulk waste must be determined in accordance with Section
724.414(c). Sorbents used to treat free liquids in a CAMU must
meet the requirements of Section 724.414(e).
4) Placement of CAMU-eligible wastes into or within a CAMU does not
constitute land disposal of hazardous waste.
5) Consolidation or placement of CAMU-eligible wastes into or within a
CAMU does not constitute creation of a unit subject to minimum
technology requirements.
b) Establishing a CAMU.
1) The Agency must designate a regulated unit (as defined in Section
724.190(a)(2)) as a CAMU or must incorporate a regulated unit into a
CAMU, if it determines that the following is true of a regulated unit:
A) The regulated unit is closed or closing, meaning it has begun the
closure process under Section 724.213 or 35 Ill. Adm. Code
725.213; and
B) Inclusion of the regulated unit will enhance implementation of
effective, protective, and reliable remedial actions for the facility.
2) The Subpart F, G, and H requirements and the unit-specific requirements
of this Part or 35 Ill. Adm. Code 265 that applied to the regulated unit
will continue to apply to that portion of the CAMU after incorporation
into the CAMU.
c) The Agency must designate a CAMU that will be used for storage or treatment
only in accordance with subsection (f) of this Section. The Agency must
designate any other CAMU in accordance with the following requirements:
118
1) The CAMU must facilitate the implementation of reliable, effective,
protective, and cost-effective remedies;
2) Waste management activities associated with the CAMU must not create
unacceptable risks to humans or to the environment resulting from
exposure to hazardous wastes or hazardous constituents;
3) The CAMU must include uncontaminated areas of the facility, only if
including such areas for the purpose of managing CAMU-eligible waste
is more protective than management of such wastes at contaminated areas
of the facility;
4) Areas within the CAMU, where wastes remain in place after closure of
the CAMU, must be managed and contained so as to minimize future
releases, to the extent practicable;
5) The CAMU must expedite the timing of remedial activity
implementation, when appropriate and practicable;
6) The CAMU must enable the use, when appropriate, of treatment
technologies (including innovative technologies) to enhance the long-term
effectiveness of remedial actions by reducing the toxicity, mobility, or
volume of wastes that will remain in place after closure of the CAMU;
and
7) The CAMU must, to the extent practicable, minimize the land area of the
facility upon which wastes will remain in place after closure of the
CAMU.
d) The owner or operator must provide sufficient information to enable the Agency
to designate a CAMU in accordance with the criteria in this Section. This must
include, unless not reasonably available, information on the following:
1) The origin of the waste and how it was subsequently managed (including
a description of the timing and circumstances surrounding the disposal or
release);
2) Whether the waste was listed or identified as hazardous at the time of
disposal or release; and
119
3) Whether the disposal or release of the waste occurred before or after the
land disposal requirements of 35 Ill. Adm. Code 728 were in effect for
the waste listing or characteristic.
e) The Agency must specify, in the permit or order, requirements for the CAMU
to include the following:
1) The areal configuration of the CAMU.
2) Except as provided in subsection (g) of this Section, requirements for
CAMU-eligible waste management to include the specification of
applicable design, operation, treatment and closure requirements.
3) Minimum Design Requirements: a CAMU, except as provided in
subsection (f) of this Section, into which wastes are placed must be
designed in accordance with the following:
A) Unless the Agency approves alternative requirements under
subsection (e)(3)(B) of this Section, a CAMU that consists of
new, replacement, or laterally expanded units must include a
composite liner and a leachate collection system that is designed
and constructed to maintain less than a 30-cm depth of leachate
over the liner. For purposes of this Section, “composite liner”
means a system consisting of two components; the upper
component must consist of a minimum 30-mil flexible membrane
liner (FML), and the lower component must consist of at least a
two-foot layer of compacted soil with a hydraulic conductivity of
no more than 1x10
-7 cm/sec. FML components consisting of high
density polyethylene (HDPE) must be at least 60 mil thick. The
FML component must be installed in direct and uniform contact
with the compacted soil component;
B) Alternative Requirements. The Agency must approve alternate
requirements if it determines that either of the following is true:
i) The Agency determines that alternative design and
operating practices, together with location characteristics,
will prevent the migration of any hazardous constituents
into the groundwater or surface water at least as
effectively as the liner and leachate collection systems in
subsection (e)(3)(A) of this Section; or
120
ii) The CAMU is to be established in an area with existing
significant levels of contamination, and the Agency
determines that an alternative design, including a design
that does not include a liner, would prevent migration
from the unit that would exceed long-term remedial goals.
4) Minimum treatment requirements: Unless the wastes will be placed in a
CAMU for storage or treatment only in accordance with subsection (f) of
this Section, CAMU-eligible wastes that, absent this Section, would be
subject to the treatment requirements of 35 Ill. Adm. Code 728, and that
the Agency determines contain principal hazardous constituents must be
treated to the standards specified in subsection (e)(4)(C) of this Section.
A) Principal hazardous constituents are those constituents that the
Agency determines pose a risk to human health and the
environment substantially higher than the cleanup levels or goals
at the site.
i) In general, the Agency must designate as principal
hazardous constituents those contaminants specified in
subsection (e)(4)(H) of this Section.
BOARD NOTE: The Board has codified 40 CFR
264.552(e)(4)(i)(A)(
1
) and (e)(4)(i)(A)(
2
) as subsections
(e)(4)(H)(i) and (e)(4)(H)(ii) of this Section in order to
comply with Illinois Administrative Code codification
requirements.
ii) The Agency must also designate constituents as principal
hazardous constituents, where appropriate, when risks to
human health and the environment posed by the potential
migration of constituents in wastes to groundwater are
substantially higher than cleanup levels or goals at the site;
when making such a designation, the Agency must
consider such factors as constituent concentrations, and
fate and transport characteristics under site conditions.
iii) The Agency must also designate other constituents as
principal hazardous constituents that the Agency
determines pose a risk to human health and the
environment substantially higher than the cleanup levels or
goals at the site.
121
B) In determining which constituents are “principal hazardous
constituents,” the Agency must consider all constituents which,
absent this Section, would be subject to the treatment
requirements in 35 Ill. Adm. Code 728.
C) Waste that the Agency determines contains principal hazardous
constituents must meet treatment standards determined in
accordance with subsection (e)(4)(D) or (e)(4)(E) of this Section:
D) Treatment standards for wastes placed in a CAMU.
i) For non-metals, treatment must achieve 90 percent
reduction in total principal hazardous constituent
concentrations, except as provided by subsection
(e)(4)(D)(iii) of this Section.
ii) For metals, treatment must achieve 90 percent reduction
in principal hazardous constituent concentrations as
measured in leachate from the treated waste or 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 (e)(4)(D)(iii) of this Section.
iii) When treatment of any principal hazardous constituent to
a 90 percent reduction standard would result in a
concentration less than 10 times the Universal Treatment
Standard for that constituent, treatment to achieve
constituent concentrations less than 10 times the Universal
Treatment Standard is not required. Universal Treatment
Standards are identified in 35 Ill. Adm. Code 728.Table
U.
iv) For waste exhibiting the hazardous characteristic of
ignitability, corrosivity, or reactivity, the waste must also
be treated to eliminate these characteristics.
v) For debris, the debris must be treated in accordance with
§ 268.45, or by methods or to levels established under
subsections (e)(4)(D)(i) through (e)(4)(D)(iv) or subsection
(e)(4)(E) of this Section, whichever the Agency
determines is appropriate.
122
vi) Alternatives to TCLP. For metal bearing wastes for
which metals removal treatment is not used, the Agency
must specify a leaching test other than the TCLP (SW846,
Method 1311, incorporated by reference in 35 Ill. Adm.
Code 720.111) to measure treatment effectiveness,
provided the Agency determines that an alternative leach
testing protocol is appropriate for use, and that the
alternative more accurately reflects conditions at the site
that affect leaching.
E) Adjusted standards. The Board will grant an adjusted standard
pursuant to Section 28.1 of the Act to adjust the treatment level
or method in subsection (e)(4)(D) of this Section to a higher or
lower level, based on one or more of the following factors, as
appropriate, if the owner or operator demonstrates that the
adjusted level or method would be protective of human health and
the environment, based on consideration of the following:
i) The technical impracticability of treatment to the levels or
by the methods in subsection (e)(4)(D) of this Section;
ii) The levels or methods in subsection (e)(4)(D) of this
Section would result in concentrations of principal
hazardous constituents (PHCs) that are significantly above
or below cleanup standards applicable to the site
(established either site-specifically, or promulgated under
State or federal law);
iii) The views of the affected local community on the
treatment levels or methods in subsection (e)(4)(D) of this
Section, as applied at the site, and, for treatment levels,
the treatment methods necessary to achieve these levels;
iv) The short-term risks presented by the on-site treatment
method necessary to achieve the levels or treatment
methods in subsection (e)(4)(D) of this Section;
v) The long-term protection offered by the engineering
design of the CAMU and related engineering controls
under the circumstances set forth in subsection (e)(4)(I) of
this Section.
123
BOARD NOTE: The Board has codified 40 CFR
264.552(e)(4)(v)(E)(
1
) through (e)(4)(v)(E)(
5
) as
subsections (e)(4)(I)(i) through (e)(4)(I)(v) of this Section
in order to comply with Illinois Administrative Code
codification requirements.
F) The treatment required by the treatment standards must be
completed prior to, or within a reasonable time after, placement
in the CAMU.
G) For the purpose of determining whether wastes placed in a
CAMU have met site-specific treatment standards, the Agency
must specify a subset of the principal hazardous constituents in
the waste as analytical surrogates for determining whether
treatment standards have been met for other principal hazardous
constituents if it determines that the specification is appropriate
based on the degree of difficulty of treatment and analysis of
constituents with similar treatment properties.
H) Principal hazardous constituents that the Agency must designate
are the following:
i) Carcinogens that pose a potential direct risk from
ingestion or inhalation at the site at or above 10
-3; and
ii) Non-carcinogens that pose a potential direct risk from
ingestion or inhalation at the site an order of magnitude or
greater over their reference dose.
I) Circumstances relating to the long-term protection offered by
engineering design of the CAMU and related engineering controls
are the following:
i) Where the treatment standards in subsection (e)(4)(D) of
this Section are substantially met and the principal
hazardous constituents in the waste or residuals are of
very low mobility;
ii) Where cost-effective treatment has been used and the
CAMU meets the Subtitle C liner and leachate collection
requirements for new land disposal units at Section
724.401(c) and (d);
124
iii) Where, after review of appropriate treatment technologies,
the Board determines that cost-effective treatment is not
reasonably available, and the CAMU meets the Subtitle C
liner and leachate collection requirements for new land
disposal units at Section 724.401(c) and (d);
iv) Where cost-effective treatment has been used and the
principal hazardous constituents in the treated wastes are
of very low mobility; or
v) Where, after review of appropriate treatment technologies,
the Board determines that cost-effective treatment is not
reasonably available, the principal hazardous constituents
in the wastes are of very low mobility, and either the
CAMU meets or exceeds the liner standards for new,
replacement, or a laterally expanded CAMU in
subsections (e)(3)(A) and (e)(3)(B) of this Section or the
CAMU provides substantially equivalent or greater
protection.
5) Except as provided in subsection (f) of this Section, requirements for
groundwater monitoring and corrective action that are sufficient to:
A) Continue to detect and to characterize the nature, extent,
concentration, direction, and movement of existing releases of
hazardous constituents in groundwater from sources located
within the CAMU; and
B) Detect and subsequently characterize releases of hazardous
constituents to groundwater that may occur from areas of the
CAMU in which wastes will remain in place after closure of the
CAMU; and
C) Require notification to the Agency and corrective action as
necessary to protect human health and the environment for
releases to groundwater from the CAMU.
6) Except as provided in subsection (f) of this Section, closure and post-
closure requirements, as follows:
A) Closure of corrective action management units must do the
following:
125
i) Minimize the need for further maintenance; and
ii) Control, minimize, or eliminate, to the extent necessary to
protect human health and the environment, for areas
where wastes remain in place, post-closure escape of
hazardous wastes, hazardous constituents, leachate,
contaminated runoff, or hazardous waste decomposition
products to the ground, to surface waters, or to the
atmosphere.
B) Requirements for closure of a CAMU must include the following,
as appropriate and as deemed necessary by the Agency for a
given CAMU:
i) Requirements for excavation, removal, treatment or
containment of wastes; and
ii) Requirements for removal and decontamination of
equipment, devices, and structures used in CAMU-eligible
waste management activities within the CAMU.
C) In establishing specific closure requirements for a CAMU under
this subsection (e), the Agency must consider the following
factors:
i) CAMU characteristics;
ii) Volume of wastes which remain in place after closure;
iii) Potential for releases from the CAMU;
iv) Physical and chemical characteristics of the waste;
v) Hydrological and other relevant environmental conditions
at the facility which may influence the migration of any
potential or actual releases; and
vi) Potential for exposure of humans and environmental
receptors if releases were to occur from the CAMU.
D) Cap requirements:
126
i) At final closure of the CAMU, for areas in which wastes
will remain with constituent concentrations at or above
remedial levels or goals applicable to the site after closure
of the CAMU, the owner or operator must cover the
CAMU with a final cover designed and constructed to
meet the performance criteria listed in subsection (e)(6)(F)
of this Section, except as provided in subsection
(e)(6)(D)(ii) of this Section:
BOARD NOTE: The Board has codified 40 CFR
264.552(e)(6)(iv)(A)(
1
) through (e)(6)(iv)(A)(
5
) as
subsections (e)(6)(F)(i) through (e)(6)(F)(v) of this Section
in order to comply with Illinois Administrative Code
codification requirements.
ii) The Agency must apply cap requirements that deviate
from those prescribed in subsection (e)(6)(D)(i) of this
Section if it determines that the modifications are needed
to facilitate treatment or the performance of the CAMU
(e.g., to promote biodegradation).
E) Post-closure requirements as necessary to protect human health
and the environment, to include, for areas where wastes will
remain in place, monitoring and maintenance activities, and the
frequency with which such activities must be performed to ensure
the integrity of any cap, final cover, or other containment system.
F) The final cover design and performance criteria are as follows:
i) Provide long-term minimization of migration of liquids
through the closed unit;
ii) Function with minimum maintenance;
iii) Promote drainage and minimize erosion or abrasion of the
cover;
iv) Accommodate settling and subsidence so that the cover’s
integrity is maintained; and
v) Have a permeability less than or equal to the permeability
of any bottom liner system or natural subsoils present.
127
f) A CAMU used for storage or treatment only is a CAMU in which wastes will
not remain after closure. Such a CAMU must be designated in accordance with
all of the requirements of this Section, except as follows:
1) A CAMU that is used for storage or treatment only and that operates in
accordance with the time limits established in the staging pile regulations
at Section 724.654(d)(1)(C), (h), and (i) is subject to the requirements
for staging piles at Section 724.654(d)(1)(A) and (d)(1)(B), (d)(2), (e),
(f), (j), and (k), in lieu of the performance standards and requirements
for a CAMU in subsections (c) and (e)(3) through (e)(6) of this Section.
2) A CAMU that is used for storage or treatment only and that does not
operate in accordance with the time limits established in the staging pile
regulations at Section 724.654(d)(1)(C), (h), and (i):
A) The owner or operator must operate in accordance with a time
limit, established by the Agency, that is no longer than necessary
to achieve a timely remedy selected for the waste and
B) The CAMU is subject to the requirements for staging piles at
Section 724.654(d)(1)(A) and (d)(1)(B), (d)(2), (e), (f), (j), and
(k) in lieu of the performance standards and requirements for a
CAMU in subsections (c) and (e)(4) and (6) of this Section.
g) A CAMU into which wastes are placed where all wastes have constituent levels
at or below remedial levels or goals applicable to the site do not have to comply
with the requirements for liners at subsection (e)(3)(A) of this Section, caps at
subsection (e)(6)(D) of this Section, groundwater monitoring requirements at
subsection (e)(5) of this Section or, for treatment or storage-only a CAMU, the
design standards at subsection (f) of this Section.
h) The Agency must provide public notice and a reasonable opportunity for public
comment before designating a CAMU. Such notice must include the rationale
for any proposed adjustments under subsection (e)(4)(E) of this Section to the
treatment standards in subsection (e)(4)(D) of this Section.
i) Notwithstanding any other provision of this Section, the Agency must impose
those additional requirements that it determines are necessary to protect human
health and the environment.
j) Incorporation of a CAMU into an existing permit must be approved by the
Agency according to the procedures for Agency-initiated permit modifications
128
under 35 Ill. Adm. Code 703.270 through 703.273, or according to the permit
modification procedures of 35 Ill. Adm. Code 703.280 through 703.283.
k) The designation of a CAMU does not change the Agency’s existing authority to
address cleanup levels, media-specific points of compliance to be applied to
remediation at a facility, or other remedy selection decisions.
(Source: Former Section Section 724.652 renumbered to Section 724.651 and new Section
724.652 added at 26 Ill. Reg. ________, effective ______________________)
Section 724.654 Staging Piles
This Section is written in a special format to make it easier to understand the regulatory
requirements. Like all other regulations, this Section establishes enforceable legal requirements.
a) What is a staging pile? Definition of a staging pile. A staging pile is an
accumulation of solid, non-flowing remediation waste (as defined in 35 Ill. Adm.
Code 720.110) that is not a containment building and which is used only during
remedial operations for temporary storage at a facility. A staging pile must be
located within the contiguous property under the control of the owner or operator
where the wastes to be managed in the staging pile originated. Staging piles must
be designated by the Agency in accordance with the requirements in this Section.
1) For the purposes of this Section, storage includes mixing, sizing,
blending, or other similar physical operations as long as they are
intended to prepare the wastes for subsequent management or treatment.
2) This subsection (a)(2) corresponds with 40 CFR 264.554(a)(2), which
USEPA has marked as “reserved.” This statement maintains structural
consistency with the federal regulations.
b)
When may an owner or operator use a staging pile? Use of a staging pile. An
owner or operator may use a staging pile to store hazardous remediation waste (or
remediation waste otherwise subject to land disposal restrictions) only if an owner
or operator follows the standards and design criteria the Agency has designated for
that staging pile. The Agency shall must designate the staging pile in a permit or,
at an interim status facility, in a closure plan or order (consistent with 35 Ill.
Adm. Code 703.155(a)(5) and (b)(5)). The Agency shall must establish
conditions in the permit, closure plan, or order that comply with subsections (d)
through (k) of this Section.
c)
What information must an owner or operator provide to get a staging pile
designated? Information that an owner or operator must submit to gain
129
designation of a staging pile. When seeking a staging pile designation, an owner
or operator shall must provide:
1) Sufficient and accurate information to enable the Agency to impose
standards and design criteria for the facility’s staging pile according to
subsections (d) through (k) of this Section;
2) Certification by an independent, qualified, registered professional engineer
of technical data, such as design drawings and specifications, and
engineering studies, unless the Agency determines, based on information
that an owner or operator provides, that this certification is not necessary
to ensure that a staging pile will protect human health and the
environment; and
3) Any additional information the Agency determines is necessary to protect
human health and the environment.
d)
What performance criteria must a staging pile satisfy? Performance criteria that a
staging pile must satisfy. The Agency shall must establish the standards and
design criteria for the staging pile in the permit, closure plan, or order.
1) The standards and design criteria must comply with the following:
A) The staging pile must facilitate a reliable, effective, and protective
remedy;
B) The staging pile must be designed so as to prevent or minimize
releases of hazardous wastes and hazardous constituents into the
environment, and minimize or adequately control cross-media
transfer, as necessary to protect human health and the environment
(for example, through the use of liners, covers, or runoff and
runon controls, as appropriate); and
C) The staging pile must not operate for more than two years, except
when the Agency grants an operating term extension under
subsection (i) of this Section. An owner or operator shall must
measure the two-year limit or other operating term specified by the
Agency in the permit, closure plan, or order from the first time an
owner or operator places remediation waste into a staging pile. An
owner or operator shall must maintain a record of the date when it
first placed remediation waste into the staging pile for the life of
the permit, closure plan, or order, or for three years, whichever is
longer.
130
2) In setting the standards and design criteria, the Agency shall must consider
the following factors:
A) The length of time the pile will be in operation;
B) The volumes of wastes the owner or operator intends to store in the
pile;
C) The physical and chemical characteristics of the wastes to be stored
in the unit;
D) The potential for releases from the unit;
E) The hydrogeological and other relevant environmental conditions at
the facility that may influence the migration of any potential
releases; and
F) The potential for human and environmental exposure to potential
releases from the unit.
e)
May a staging pile receive ignitable or reactive remediation waste? Receipt of
ignitable or reactive remediation waste. An owner or operator shall must not
place ignitable or reactive remediation waste in a staging pile unless:
1) The owner or operator has treated, rendered, or mixed the remediation
waste before it placed the waste in the staging pile so that the following is
true of the waste:
A) The remediation waste no longer meets the definition of ignitable
or reactive under 35 Ill. Adm. Code 721.121 or 721.123; and
B) The owner or operator has complied with Section 724.117(b); or
2) An owner or operator manages the remediation waste to protect it from
exposure to any material or condition that may cause it to ignite or react.
f)
How does an owner or operator handle incompatible remediation wastes in a
staging pile? Managing incompatible remediation wastes in a staging pile. The
term “incompatible waste” is defined in 35 Ill. Adm. Code 720.110. An owner
or operator shall must comply with the following requirements for incompatible
wastes in staging piles:
131
1) An owner or operator shall must not place incompatible remediation
wastes in the same staging pile unless an owner or operator has complied
with Section 724.117(b);
2) If remediation waste in a staging pile is incompatible with any waste or
material stored nearby in containers, other piles, open tanks, or land
disposal units (for example, surface impoundments), an owner or operator
shall must separate the incompatible materials, or protect them from one
another by using a dike, berm, wall, or other device; and
3) An owner or operator shall must not pile remediation waste on the same
base where incompatible wastes or materials were previously piled, unless
the base has been decontaminated sufficiently to comply with Section
724.117(b).
g) Are staging piles subject to Land Disposal Restrictions (LDR) and federal
Minimum Technological Requirements (MTR)? No. Staging piles are not subject
to land disposal restrictions and federal minimum technological requirements.
Placing hazardous remediation wastes into a staging pile does not constitute land
disposal of hazardous wastes or create a unit that is subject to the federal minimum
technological requirements of RCRA 3004(o), 42 USC 6924(o).
h)
How long may an owner or operator operate a staging pile? How long an owner
or operator may operate a staging pile. The Agency may allow a staging pile to
operate for up to two years after hazardous remediation waste is first placed into
the pile. An owner or operator shall must use a staging pile no longer than the
length of time designated by the Agency in the permit, closure plan, or order (the
“operating term”), except as provided in subsection (i) of this Section.
i)
May an owner or operator receive an operating extension for a staging pile?
Receiving an operating extension for a staging pile.
1) The Agency may grant one operating term extension of up to 180 days
beyond the operating term limit contained in the permit, closure plan, or
order (see subsection (l) of this Section for modification procedures). To
justify the need for an extension, an owner or operator shall must provide
sufficient and accurate information to enable the Agency to determine that
the following is true of continued operation of the staging pile:
A) Continued operation will not pose a threat to human health and the
environment; and
132
B) Continued operation is necessary to ensure timely and efficient
implementation of remedial actions at the facility.
2) The Agency shall must, as a condition of the extension, specify further
standards and design criteria in the permit, closure plan, or order, as
necessary, to ensure protection of human health and the environment.
j)
What is the closure requirement for a staging pile located in a previously
contaminated area? The closure requirement for a staging pile located in a
previously contaminated area.
1) Within 180 days after the operating term of the staging pile expires, an
owner or operator shall must close a staging pile located in a previously
contaminated area of the site by removing or decontaminating all of the
following:
A) Remediation waste;
B) Contaminated containment system components; and
C) Structures and equipment contaminated with waste and leachate.
2) An owner or operator shall must also decontaminate contaminated subsoils
in a manner and according to a schedule that the Agency determines will
protect human health and the environment.
3) The Agency shall must include the above requirements in the permit,
closure plan, or order in which the staging pile is designated.
k)
What is the closure requirement for a staging pile located in an uncontaminated
area? The closure requirement for a staging pile located in a previously
uncontaminated area.
1) Within 180 days after the operating term of the staging pile expires, an
owner or operator shall must close a staging pile located in an
uncontaminated area of the site according to Sections 724.358(a) and
724.211 or according to 35 Ill. Adm. Code 725.358(a) and 725.211.
2) The Agency shall must include the above requirement in the permit,
closure plan, or order in which the staging pile is designated.
l)
How may an existing permit (for example, RAP), closure plan, or order be
modified to allow an owner or operator to use a staging pile? Modifying an
133
existing permit (e.g., a RAP), closure plan, or order to allow the use of a staging
pile.
1) To modify a permit, other than a RAP, to incorporate a staging pile or
staging pile operating term extension, either of the following must occur:
A) The Agency shall must approve the modification under the
procedures for Agency-initiated permit modifications in 35 Ill.
Adm. Code 703.270 through 703.273; or
B) An owner or operator shall must request a Class 2 modification
under 35 Ill. Adm. Code 703.280 through 703.283.
2) To modify a RAP to incorporate a staging pile or staging pile operating
term extension, an owner or operator shall must comply with the RAP
modification requirements under 35 Ill. Adm. Code 703.304(a) and (b).
3) To modify a closure plan to incorporate a staging pile or staging pile
operating term extension, an owner or operator shall must follow the
applicable requirements under Section 724.212(c) or 35 Ill. Adm. Code
725.212(c).
4) To modify an order to incorporate a staging pile or staging pile operating
term extension, an owner or operator shall must follow the terms of the
order and the applicable provisions of 35 Ill. Adm. Code 703.155(a)(5) or
(b)(5).
m)
Is information about the staging pile available to the public? Public availability of
information about a staging pile. The Agency shall must document the rationale
for designating a staging pile or staging pile operating term extension and make
this documentation available to the public.
(Source: Amended at 26 Ill. Reg. ________, effective ______________________)
Section 724.655 Disposal of CAMU-Eligible Wastes in Permitted Hazardous Waste
Landfills
a) The Agency must approve placement of CAMU-eligible wastes in hazardous
waste landfills not located at the site from which the waste originated, without
the wastes meeting the requirements of 35 Ill. Adm. Code 728, if it determines
that the following conditions are met:
134
1) The waste meets the definition of CAMU-eligible waste in Section
724.652(a)(1) and (a)(2).
2) The Agency identifies principal hazardous constitutes in such waste, in
accordance with Section 724.652(e)(4)(A) and (e)(4)(B), and requires
that such principal hazardous constituents are treated to any of the
following standards specified for CAMU-eligible wastes:
A) The treatment standards under Section 724.652(e)(4)(D); or
B) Treatment standards adjusted in accordance with Section
724.652(e)(4)(E)(i), (e)(4)(E)(iii), (e)(4)(E)(iv) or (e)(4)(F)(i); or
C) Treatment standards adjusted in accordance with Section
724.652(e)(4)(I)(ii), where treatment has been used and that
treatment significantly reduces the toxicity or mobility of the
principal hazardous constituents in the waste, minimizing the
short-term and long-term threat posed by the waste, including the
threat at the remediation site.
3) The landfill receiving the CAMU-eligible waste must have a RCRA
hazardous waste permit, meet the requirements for new landfills in
Subpart N of this Part, and be authorized to accept CAMU-eligible
wastes; for the purposes of this requirement, “permit” does not include
interim status.
b) The person seeking approval shall provide sufficient information to enable the
Agency to approve placement of CAMU-eligible waste in accordance with
subsection (a) of this Section. Information required by Section 724.652(d)(1)
through (d)(3) for CAMU applications must be provided, unless not reasonably
available.
c) The Agency must provide public notice and a reasonable opportunity for public
comment before approving CAMU eligible waste for placement in an off-site
permitted hazardous waste landfill, consistent with the requirements for CAMU
approval at Section 724.652(h). The approval must be specific to a single
remediation.
d) Applicable hazardous waste management requirements in this Part, including
recordkeeping requirements to demonstrate compliance with treatment standards
approved under this Section, for CAMU-eligible waste must be incorporated
into the receiving facility permit through permit issuance or a permit
modification, providing notice and an opportunity for comment and a hearing.
135
Notwithstanding 35 Ill. Adm. Code 702.181(a), a landfill may not receive
hazardous CAMU-eligible waste under this Section unless its permit specifically
authorizes receipt of such waste.
e) For each remediation, CAMU-eligible waste may not be placed in an off-site
landfill authorized to receive CAMU-eligible waste in accordance with
subsection (d) of this Section until the following additional conditions have been
met:
1) The landfill owner or operator notifies the Agency and persons on the
facility mailing list, maintained in accordance with 35 Ill. Adm. Code
705.163(a), of his or her intent to receive CAMU-eligible waste in
accordance with this Section; the notice must identify the source of the
remediation waste, the principal hazardous constituents in the waste, and
treatment requirements.
2) Persons on the facility mailing list may provide comments, including
objections to the receipt of the CAMU-eligible waste, to the Agency
within 15 days after notification.
3) The Agency must object to the placement of the CAMU-eligible waste in
the landfill within 30 days of notification; the Agency must extend the
review period an additional 30 days if it determines that the extension is
necessary because of public concerns or insufficient information.
4) CAMU-eligible wastes may not be placed in the landfill until the Agency
has notified the facility owner or operator that it does not object to its
placement.
5) If the Agency objects to the placement or does not notify the facility
owner or operator that it has chosen not to object, the facility may not
receive the waste, notwithstanding 35 Ill. Adm. Code 702.181(a), until
the objection has been resolved, or the owner/operator obtains a permit
modification in accordance with the procedures of 35 Ill. Adm. Code
703.280 through 703.283 specifically authorizing receipt of the waste.
6) The Board will grant an adjusted standard under Section 28.1 of the Act
that modifies, reduces, or eliminates the notification requirements of this
subsection (e) as they apply to specific categories of CAMU-eligible
waste, if the owner or operator demonstrates that this is possible based
on miminal risk.
136
f) Generators of CAMU-eligible wastes sent off-site to a hazardous waste landfill
under this Section must comply with the requirements of 35 Ill. Adm. Code
728.107(a)(4). Off-site facilities treating CAMU-eligible wastes to comply with
this Section must comply with the requirements of 35 Ill. Adm. Code
728.107(b)(4), except that the certification must be with respect to the treatment
requirements of subsection (a)(2) of this Section.
g) For the purposes of this Section only, the “design of the CAMU” in Section
724.652(e)(4)(E)(v) means design of the permitted Subtitle C landfill.
(Source: Added at 26 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 applicable to generators and transporters of materials used in a
manner that constitutes disposal
726.122 Standards applicable to storers, who are not the ultimate users, of materials that
are to be used in a manner that constitutes disposal
726.123 Standards Applicable to Users of Materials that are Used in a Manner that
Constitutes Disposal
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)
137
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 (Repealed)
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 requirements
SUBPART G: SPENT LEAD-ACID BATTERIES BEING RECLAIMED
Section
726.180 Applicability and requirements
SUBPART H: HAZARDOUS WASTE BURNED IN BOILERS AND
INDUSTRIAL FURNACES
Section
726.200 Applicability
726.201 Management prior to Burning
726.202 Permit standards for Burners
726.203 Interim Status Standards for Burners
726.204 Standards to Control Organic Emissions
726.205 Standards to control PM
726.206 Standards to Control Metals Emissions
726.207 Standards to control HCl and Chlorine Gas Emissions
726.208 Small quantity On-site Burner Exemption
726.209 Low risk waste Exemption
726.210 Waiver of DRE trial burn for Boilers
726.211 Standards for direct Transfer
726.212 Regulation of Residues
726.219 Extensions of Time
138
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
726.Appendix A Tier I and Tier II Feed Rate and Emissions Screening Limits for Metals
726.Appendix B Tier I Feed Rate Screening Limits for Total Chlorine
139
726.Appendix C Tier II Emission Rate Screening Limits for Free Chlorine and Hydrogen
Chloride
726.Appendix D Reference Air Concentrations
726.Appendix E Risk Specific Doses
726.Appendix F Stack Plume Rise
726.Appendix G Health-Based Limits for Exclusion of Waste-Derived Residues
726.Appendix H Potential PICs for Determination of Exclusion of Waste-Derived
Residues
726.Appendix I Methods Manual for Compliance with BIF Regulations
726.Appendix J Guideline on Air Quality Models
726.Appendix K Lead-Bearing Materials That May be Processed in Exempt Lead Smelters
726.Appendix L Nickel or Chromium-Bearing Materials that may be Processed in Exempt
Nickel-Chromium Recovery Furnaces
726.Appendix M Mercury-Bearing Wastes That May Be Processed in Exempt Mercury
Recovery Units
726.Table A 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. ________, 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:
140
“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 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
141
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
142
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 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: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.320 Storage and Treatment Conditional Exemption
The storage and treatment conditional exemption exempts low-level mixed waste from the
regulatory definition of hazardous waste in 35 Ill. Adm. Code 721.103 if the waste meets the
eligibility criteria in Section 726.325 and the generator meets the conditions in Section
726.330.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.325 Wastes Eligible for a Storage and Treatment Conditional Exemption for
Low-Level Mixed Waste
Low-level mixed waste (LLMW), as defined in Section 726.310, is eligible for a storage and
treatment conditional exemption if it is generated and managed by a person under a single
143
federal NRC or Illinois DNS license. (Mixed waste generated at a facility with a different
license number and shipped to a different person’s facility for storage or treatment requires a
permit, and such mixed waste is ineligible for this exemption. In addition, NARM waste is
ineligible for this exemption.)
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.330 Conditions to Qualify for and Maintain a Storage and Treatment
Conditional Exemption
a) For LLMW to qualify for the exemption, the generator must notify the Agency
and the Illinois DNS in writing by certified delivery that it is claiming a storage
and treatment conditional exemption for the LLMW stored on the generator’s
facility. The dated notification must include the generator’s name, address,
RCRA identification number, federal NRC or Illinois DNS license number, the
waste codes and storage units for which the generator is seeking an exemption,
and a statement that the generator meets the conditions of this Subpart N. The
generator’s notification must be signed by the generator’s authorized
representative who certifies that the information in the notification is true,
accurate, and complete. The generator must notify the Agency of its claim
either before July 21, 2002, or within 90 days after a storage unit is first used to
store conditionally exempt LLMW, whichever is later.
b) To qualify for and maintain an exemption for LLMW, the generator must do
each of the following:
1) Store its LLMW waste in tanks or containers in compliance with the
requirements of its license that apply to the proper storage of low-level
radioactive waste (not including those license requirements that relate
solely to recordkeeping);
2) Store its LLMW in tanks or containers in compliance with chemical
compatibility requirements of a tank or container in 35 Ill. Adm. Code
724.277 or 724.299 or 35 Ill. Adm. Code 725.277 or 725.299;
3) Certify that facility personnel who manage stored conditionally exempt
LLMW are trained in a manner that ensures that the conditionally
exempt waste is safely managed and that the training includes training in
chemical waste management and hazardous materials incidents response
that meets the personnel training standards found in 35 Ill. Adm. Code
725.116(a)(3);
144
4) Conduct an inventory of its stored conditionally exempt LLMW at least
annually and inspect the waste at least quarterly for compliance with this
Subpart N; and
5) Maintain an accurate emergency plan and provide it to all local
authorities who may have to respond to a fire, explosion, or release of
hazardous waste or hazardous constituents. The generator’s plan must
describe emergency response arrangements with local authorities;
describe evacuation plans; list the names, addresses, and telephone
numbers of all facility personnel qualified to work with local authorities
as emergency coordinators; and list emergency equipment.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.335 Treatment Allowed by a Storage and Treatment Conditional Exemption
The generator may treat its low-level mixed waste at its facility within a tank or container in
accordance with the terms of its federal NRC or Illinois DNS license. Treatment that cannot
be done in a tank or container without a RCRA permit (such as incineration) is not allowed
under this exemption.
(Source: Added at 26 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:
A) The specific conditions that the generator failed to meet;
145
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: Added at 26 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.
146
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, 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.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.350 Recordkeeping for a Storage and Treatment Conditional Exemption
a) In addition to those records required by the generator’s federal NRC or Illinois
DNS license, the generator must keep records as follows:
1) The generator’s initial notification records, return receipts, reports to the
Agency of failures to meet the exemption conditions, and all records
supporting any reclaim of an exemption;
2) Records of the generator’s LLMW annual inventories and quarterly
inspections;
3) The generator’s certification that facility personnel who manage stored
mixed waste are trained in safe management of LLMW including
training in chemical waste management and hazardous materials incidents
response; and
147
4) The generator’s emergency plan, as specified in Section 726.330(b).
b) The generator must maintain records concerning notification, personnel trained,
and its emergency plan for as long as the generator claims this exemption and
for three years thereafter, or in accordance with federal NRC regulations under
10 CFR 20 or under Illinois DNS regulations under 32 Ill. Adm. Code:
Chapter II, Subchapter b, whichever is longer. A generator must maintain
records concerning its annual inventory and quarterly inspections for three years
after the waste is sent for disposal, or in accordance with federal NRC
regulations under 10 CFR 20 or with Illinois DNS regulations under 32 Ill.
Adm. Code: Chapter II, Subchapter b, whichever is longer.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.355 Waste No Longer Eligible for a Storage and Treatment Conditional
Exemption
a) When a generator’s LLMW has met the requirements of its federal NRC or
Illinois DNS license for decay-in-storage and can be disposed of as non-
radioactive waste, then the conditional exemption for storage no longer applies.
On that date the generator’s waste is subject to hazardous waste regulation under
the relevant Sections of 35 Ill. Adm. Code 702, 703, 720 through 726, and 728,
and the time period for accumulation of a hazardous waste, as specified in 35
Ill. Adm. Code 722.134 begins.
b) When a generator’s conditionally exempt LLMW, which has been generated and
stored under a single federal NRC or Illinois DNS license number, is removed
from storage, it is no longer eligible for the storage and treatment exemption.
However, a generator’s waste may be eligible for the transportation and disposal
conditional exemption at Section 726.405.
(Source: Added at 26 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 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.
148
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.405 Transportation and Disposal Conditional Exemption
A transportation and disposal conditional exemption exempts a generator’s waste from the
regulatory definition of hazardous waste in 35 Ill. Adm. Code 721.103 if the generator’s waste
meets the eligibility criteria under Section 726.410, and the generator meets the conditions in
Section 726.415.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.410 Wastes Eligible for a Transportation and Disposal Conditional
Exemption
Eligible waste must be one or both of the following:
a) A low-level mixed waste (LLMW), as defined in Section 726.310, that meets
the waste acceptance criteria of a LLRWDF; or
b) An eligible NARM waste, defined in Section 726.310.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.415 Conditions to Qualify for and Maintain a Transportation and Disposal
Conditional Exemption
A generator must meet the following conditions for its eligible waste to qualify for and
maintain the exemption:
a) The eligible waste must meet or be treated to meet LDR treatment standards, as
described in Section 726.420;
b) If the generator is not already subject to federal NRC or Illinois DNS manifest
and transportation regulations for the shipment of its waste, the generator must
manifest and transport its waste according to federal NRC or Illinois DNS
regulations, as described in Section 726.425;
c) The exempted waste must be in containers when it is disposed of in the
LLRWDF, as described in Section 726.440; and
d) The exempted waste must be disposed of at a designated LLRWDF, as
described in Section 726.435.
149
(Source: Added at 26 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 35 Ill. Adm. Code 728.Subpart D.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.425 Applicability of the Manifest and Transportation Condition
If a generator is not already subject to federal NRC or Illinois DNS manifest and transportation
regulations for the shipment of its waste, the generator must meet the federal NRC manifest
requirements under 10 CFR 20.2006, incorporated by reference in 35 Ill. Adm. Code 720.111,
and Illinois DNS manifest requirements under 32 Ill. Adm. Code 340, and the federal NRC
transportation requirements under 10 CFR 71.5 and the Illinois DNS transportation
requirements under 32 Ill. Adm. Code 341 to ship the exempted waste.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.430 Effectiveness of a Transportation and Disposal Exemption
The exemption becomes effective once all of the following have occurred:
a) The generator’s eligible waste meets the applicable LDR treatment standards;
b) The generator has received return receipts that it has notified the Agency and the
LLRWDF, as described in Section 726.445;
c) The generator has completed the packaging and preparation for shipment
requirements for its waste according to federal NRC packaging and
transportation regulations found under 10 CFR 71, incorporated by reference in
35 Ill. Adm. Code 720.111, and under Illinois DNS regulations under 32 Ill.
Adm. Code 341; and a generator has prepared a manifest for a generator’s
waste according to NRC manifest regulations found under 10 CFR 20 or under
Illinois DNS regulations under 32 Ill. Adm. Code 340; and
d) The generator has placed its waste on a transportation vehicle destined for a
LLRWDF licensed by the federal NRC, the Illinois DNS, or by a nuclear
licensing agency in another state.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
150
Section 726.435 Disposal of Exempted Waste
A generator’s exempted waste must be disposed of in a LLRWDF that is regulated and licensed
by the federal NRC under 10 CFR 61, by the Illinois DNS under 32 Ill. Adm. Code: Chapter
II, Subchapters b and d, or by a licensing agency in another state, including State NARM
licensing regulations for eligible NARM.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.440 Containers Used for Disposal of Exempted Waste
A generator’s exempted waste must be placed in containers before it is disposed of. The
container must be one of the following:
a) A carbon steel drum;
b) An alternative container with equivalent containment performance in the
disposal environment as a carbon steel drum; or
c) A high-integrity container, as defined by NRC in Appendix G to 40 CFR 20,
incorporated by reference in 35 Ill. Adm. Code 720.111.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.445 Notification
a) A generator must provide a one time notice to the Agency and the Illinois DNS
stating that it is claiming the transportation and disposal conditional exemption
prior to the initial shipment of an exempted waste from the generator’s facility
to a LLRWDF. The generator’s dated written notice must include its facility
name, address, phone number, and RCRA ID number and be sent by certified
delivery.
b) A generator must notify the LLRWDF receiving its exempted waste by certified
delivery before shipment of each exempted waste. The generator can only ship
the exempted waste after it has received the return receipt of its notice to the
LLRWDF. This notification must include the following information:
1) A statement that the generator has claimed the exemption for the waste;
2) A statement that the eligible waste meets applicable LDR treatment
standards;
151
3) The generator’s facility’s name, address, and RCRA ID number;
4) The RCRA hazardous waste codes prior to the exemption of the waste
streams;
5) A statement that the exempted waste must be placed in a container
according to Section 726.440 prior to disposal in order for the waste to
remain exempt under the transportation and disposal conditional
exemption of this Subpart N;
6) The manifest number of the shipment that will contain the exempted
waste; and
7) A certification that all the information provided is true, complete, and
accurate. The statement must be signed by the generator’s authorized
representative.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
Section 726.450 Recordkeeping for a Transportation and Disposal Conditional Exemption
In addition to those records required by a generator’s NRC or Illinois DNS license, the
generator must keep records as follows:
a) The generator must follow the applicable existing recordkeeping requirements
under 35 Ill. Adm. Code 724.173, 725.173, and 728.107 to demonstrate that its
waste has met LDR treatment standards prior to the generator claiming the
exemption.
b) The generator must keep a copy of all notifications and return receipts required
under Sections 726.455, and 726.460 for three years after the exempted waste is
sent for disposal.
c) The generator must keep a copy of all notifications and return receipts required
under Section 726.445(a) for three years after the last exempted waste is sent for
disposal.
d) The generator must keep a copy of the notification and return receipt required
under Section 726.445(b) for three years after the exempted waste is sent for
disposal.
e) If the generator is not already subject to federal NRC and Illinois DNS manifest
and transportation regulations for the shipment of its waste, the generator must
152
also keep all other documents related to tracking the exempted waste as required
under federal 10 CFR 20.2006, incorporated by reference in 35 Ill. Adm. Code
720.111, and Illinois DNS requirements under 32 Ill. Adm. Code 340,
including applicable NARM requirements, in addition to the records specified in
subsections (a) through (d) of this Section.
(Source: Added at 26 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 5 days.
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: Added at 26 Ill. Reg. ________, effective ______________________)
153
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, 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
154
environment. Any Agency determination made pursuant to this subsection (b) is
subject to review by the Board pursuant to Section 40 of the Act.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
PART 728
Section
728.106 Petitions to Allow Land Disposal of a Waste Prohibited under Subpart C
728.113 Newly Listed Wastes
Section
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
LAND DISPOSAL RESTRICTIONS
SUBPART A: GENERAL
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 case-by-case Extensions to an Effective Date
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)
728.114 Surface Impoundment exemptions
SUBPART C: PROHIBITION ON LAND DISPOSAL
728.130 Waste Specific Prohibitions -- Wood Preserving Wastes
728.131 Waste Specific Prohibitions -- Dioxin-Containing Wastes
728.132 Waste Specific Prohibitions -- Soils Exhibiting the Toxicity Characteristic for
Metals and Containing PCBs
728.133 Waste-Specific Prohibitions -- Chlorinated Aliphatic Wastes
155
728.134 Waste-Specific Prohibitions -- Toxicity Characteristic Metal Wastes
728.135 Waste Specific Prohibitions -- Petroleum Refining Wastes
728.136 Waste Specific Prohibitions -- Newly Listed Wastes (Repealed) Inorganic
Chemical Wastes
728.137 Waste Specific Prohibitions -- Ignitable and Corrosive Characteristic Wastes
Whose Treatment Standards Were Vacated
728.140 Applicability of Treatment Standards
728.142 Treatment Standards Expressed as Specified Technologies
728.149 Alternative LDR Treatment Standards for Contaminated Soil
728.Appendix A Toxicity Characteristic Leaching Procedure (TCLP) (Repealed)
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
728.141 Treatment Standards Expressed as Concentrations in Waste Extract
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
SUBPART E: PROHIBITIONS ON STORAGE
Section
728.150 Prohibitions on Storage of Restricted Wastes
728.Appendix B Treatment Standards (As concentrations in the Treatment Residual
Extract) (Repealed)
728.Appendix C List of Halogenated Organic Compounds (Repealed) Regulated under
Section 728.132
728.Appendix D Wastes Excluded from Lab Packs
728.Appendix E Organic Lab Packs (Repealed)
728.Appendix K Metal Bearing Wastes Prohibited From Dilution in a Combustion Unit
According to Section 728.103(c)
728.Appendix F Technologies to Achieve Deactivation of Characteristics
728.Appendix G Federal Effective Dates
728.Appendix H National Capacity LDR Variances for UIC Wastes
728.Appendix I EP Toxicity Test Method and Structural Integrity Test
728.Appendix J Recordkeeping, Notification, and Certification Requirements (Repealed)
728.Table A Constituent Concentrations in Waste Extract (CCWE)
156
728.Table E Standards for Radioactive Mixed Waste
728.Table U Universal Treatment Standards (UTS)
728.Table B Constituent Concentrations in Wastes (CCW)
728.Table C Technology Codes and Description of Technology-Based Standards
728.Table D Technology-Based Standards by RCRA Waste Code
728.Table F Alternative Treatment Standards for Hazardous Debris
728.Table G Alternative Treatment Standards Based on HTMR
728.Table H Wastes Excluded from CCW Treatment Standards
728.Table I Generator Paperwork Requirements
728.Table T Treatment Standards for Hazardous Wastes
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 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, 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. ________, effective ______________________.
SUBPART C: PROHIBITION ON LAND DISPOSAL
Section 728.134 Waste-Specific Prohibitions -- Toxicity Characteristic Metal Wastes
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
157
c)
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.
Effective May 26, 2000, the 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)
Until May 26, 2000, newly identified characteristic wastes from elemental
phosphorus processing, radioactive waste 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 may be disposed in a
landfill or surface impoundment only if such unit is in compliance with the
requirements specified in Section 728.105(h)(2).This provision corresponds with
40 CFR 269.34(d), which was applicable by its own terms only until May 26,
2000. We have removed this subsection (d), since it no longer applies. This
statement maintains structural consistency with the corresponding federal
regulations.
e) The requirements of subsections (a) and (b) of this Section do not apply if any of
the following applies to the waste:
3) The wastes meet the applicable alternate treatment standards established
pursuant to a petition granted under Section 728.144; or
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;
158
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: Added at 26 Ill. Reg. ________, effective ______________________)
Section 728.136 Waste Specific Prohibitions -- Newly Listed Wastes (Repealed) Inorganic
Chemical Wastes
a) Effective May 20, 2002, the wastes specified in 35 Ill. Adm. Code 721 as
USEPA hazardous wastes numbers K176, K177, and K178, and soil and debris
contaminated with these wastes, radioactive wastes mixed with these wastes, and
soil and debris contaminated with radioactive wastes mixed with these wastes
are prohibited from land disposal.
b) The requirements of subsection (a) of this Section do not apply if any of the
following is true with regard to the waste:
1) The wastes meet the applicable treatment standards specified in Subpart
D of this Part;
2) Persons have been granted an exemption from a prohibition pursuant to a
petition under Section 728.106, with respect to those wastes and units
covered by the petition;
3) The wastes meet the applicable treatment standards established pursuant
to a petition granted under Section 728.144;
4) Hazardous debris has met the treatment standards in Sections 728.140
and 728.Table T or the alternative treatment standards in Section
728.145; or
159
5) Persons have been granted an extension to the effective date of a
prohibition pursuant to Section 728.105, with respect to these wastes
covered by the extension.
c) To determine whether a hazardous waste identified in this Section exceeds the
applicable treatment standards specified in Sections 728.140 and 728.Table T,
the initial generator must test a sample of the waste extract or the entire waste,
depending on whether the treatment standards are expressed as concentrations in
the waste extract or the waste, or the generator may use knowledge of the waste.
If the waste contains regulated constituents in excess of the applicable Subpart D
levels, the waste is prohibited from land disposal, and all requirements of this
part are applicable, except as otherwise specified.
(Source: Added at 26 Ill. Reg. ________, effective ______________________)
And if the LDRs
SUBPART D: TREATMENT STANDARDS
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
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 contamin-
ated the soil*.
Apply to the
listed waste now.
The soil is deter-
mined to contain
the listed waste
when the soil is
first generated.
Must comply with
LDRs.
160
Did not apply to
the listed waste
when it contamin-
ated the soil*.
Apply to the
listed waste now.
The soil is deter-
mined 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 contamin-
ated 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 or according to the universal treatment standards specified in
Section 728.148 and Table U of this Part.
B) For metals and carbon disulfide, cyclohexanone, and methanol,
treatment must achieve 90 percent reduction in constituent
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.
161
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.
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:
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
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.
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.
universal treatment standards, 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.
162
1) Soil residuals are subject to the treatment standards of this Section;
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.
Aug. 8, 1990.
D004
May 26, 2000.
D005
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:
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
(Source: Added at 26 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 LDRS
a—COMPREHENSIVE LIST
Waste code
Waste category
Effective date
D001
c
All (except High TOC Ignitable Liquids)
Aug. 9, 1993.
D001
High TOC Ignitable Liquids
D002
c
All
Aug. 9, 1993.
D003
e
Newly identified surface-disposed elemental
phosphorus processing wastes
May 26, 2000.
Newly identified D004 and mineral processing
wastes
Aug. 24, 1998.
D004
Mixed radioactive/newly identified D004 or
mineral processing wastes
D005
Newly identified D005 and mineral processing
wastes
Aug. 24, 1998.
Mixed radioactive/newly identified D005 or
mineral processing wastes
May 26, 2000.
163
Aug. 24, 1998.
D007
May 26, 2000.
D010
May 26, 2000.
D011
All
Dec. 14, 1994.
D016 (that exhibit the toxicity
characteristic based on the
TCLP)
Sep. 19, 1996.
D006
Newly identified D006 and mineral processing
wastes
D006
Mixed radioactive/newly identified D006 or
mineral processing wastes
May 26, 2000.
Newly identified D007 and mineral processing
wastes
Aug. 24, 1998.
D007
Mixed radioactive/newly identified D007or
mineral processing wastes
D008
Newly identified D008 and mineral processing
waste
Aug. 24, 1998.
D008
Mixed radioactive/newly identified D008 or
mineral processing wastes
May 26, 2000.
D009
Newly identified D009 and mineral processing
waste
Aug. 24, 1998.
D009
Mixed radioactive/newly identified D009or
mineral processing wastes
May 26, 2000.
Newly identified D010 and mineral processing
wastes
Aug. 24, 1998.
D010
Mixed radioactive/newly identified D010 or
mineral processing wastes
D011
Newly identified D011 and mineral processing
wastes
Aug. 24, 1998.
Mixed radioactive/newly identified D011or
mineral processing wastes
May 26, 2000.
D012 (that exhibit the toxicity
characteristic based on the
TCLP)
d
Dec. 14, 1994.
D013 (that exhibit the toxicity
characteristic based on the
TCLP)
d
All
D014 (that exhibit the toxicity
characteristic based on the
TCLP)
d
All
Dec. 14, 1994.
D015 (that exhibit the toxicity
characteristic based on the
TCLP)
d
All
Dec. 14, 1994.
d
All
Dec. 14, 1994.
D017 (that exhibit the toxicity
characteristic based on the
TCLP)
d
All
Dec. 14, 1994.
D018
Mixed with radioactive wastes
164
D019
Dec. 19, 1994.
D020
Sep. 19, 1996.
D022
Dec. 19, 1994.
D023
Sep. 19, 1996.
D025
Dec. 19, 1994.
D026
Sep. 19, 1996.
D028
Dec. 19, 1994.
D029
Sep. 19, 1996.
D031
Dec. 19, 1994.
D032
Sep. 19, 1996.
D034
Dec. 19, 1994.
D035
Sep. 19, 1996.
D037
Dec. 19, 1994.
Dec. 19, 1994.
D018
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
D019
All others
D020
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
D021
Mixed with radioactive wastes
D021
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
D022
All others
D023
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
D024
Mixed with radioactive wastes
D024
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
D025
All others
D026
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
D027
Mixed with radioactive wastes
D027
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
D028
All others
D029
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
D030
Mixed with radioactive wastes
D030
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
D031
All others
D032
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
D033
Mixed with radioactive wastes
D033
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
D034
All others
D035
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
D036
Mixed with radioactive wastes
D036
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
D037
All others
D038
Mixed with radioactive wastes
Sep. 19, 1996.
D038
All others
D039
Mixed with radioactive wastes
Sep. 19, 1996.
D039
All others
Dec. 19, 1994.
165
D040
Dec. 19, 1994.
Dec. 19, 1994.
All
Mixed with radioactive wastes
Sep. 19, 1996.
D040
All others
D041
Mixed with radioactive wastes
Sep. 19, 1996.
D041
All others
D042
Mixed with radioactive wastes
Sep. 19, 1996.
D042
All others
Dec. 19, 1994.
D043
Mixed with radioactive wastes
Sep. 19, 1996.
D043
All others
Dec. 19, 1994.
F001
Small quantity generators, CERCLA
response/RCRA corrective action, initial
generator’s solvent-water mixtures, solvent-
containing sludges and solids
Nov. 8, 1988.
F001
All others
Nov. 8, 1986.
F002 (1,1,2-trichloroethane)
Wastewater and Nonwastewater
Aug. 8, 1990.
F002
Small quantity generators, CERCLA
response/RCRA corrective action, initial
generator’s solvent-water mixtures, solvent-
containing sludges and solids
Nov. 8, 1988.
F002
All others
Nov. 8, 1986.
F003
Small quantity generators, CERCLA
response/RCRA corrective action, initial
generator’s solvent-water mixtures, solvent-
containing sludges and solids
Nov. 8, 1988.
F003
All others
Nov. 8, 1986.
F004
Small quantity generators, CERCLA
response/RCRA corrective action, initial
generator’s solvent-water mixtures, solvent-
containing sludges and solids
Nov. 8, 1988.
F004
All others
Nov. 8, 1986.
F005 (benzene, 2-ethoxy
ethanol, 2-nitropropane)
Wastewater and Nonwastewater
Aug. 8, 1990.
F005
Small quantity generators, CERCLA
response/RCRA corrective action, initial
generator’s solvent-water mixtures, solvent-
containing sludges and solids
Nov. 8, 1988.
F005
All others
Nov. 8, 1986.
F006
Wastewater
Aug. 8, 1990.
F006
Nonwastewater
Aug. 8, 1988.
F006 (cyanides)
Nonwastewater
July 8, 1989.
F007
All
July 8, 1989.
F008
All
July 8, 1989.
F009
All
July 8, 1989.
F010
June 8, 1989.
166
Nov. 8, 1988.
June 8, 1989.
F011 (cyanides)
Nonwastewater
Dec. 8, 1989.
F011
All others
July 8, 1989.
F012 (cyanides)
Nonwastewater
Dec. 8, 1989.
F012
All others
July 8, 1989.
F019
All
Aug. 8, 1990.
F020
All
Nov. 8, 1988.
F021
All
Nov. 8, 1988.
F025
All
Aug. 8, 1990.
F026
All
Nov. 8, 1988.
F027
All
F028
All
Nov. 8, 1988.
F032
Mixed with radioactive wastes
May 12, 1999.
F032
All others
Aug. 12, 1997.
F034
Mixed with radioactive wastes
May 12, 1999.
F034
All others
Aug. 12, 1997.
F035
Mixed with radioactive wastes
May 12, 1999.
F035
All others
Aug. 12, 1997.
F037
Not generated from surface impoundment
cleanouts or closures
June 30, 1993.
F037
Generated from surface impoundment
cleanouts or closures
June 30, 1994.
F037
Mixed with radioactive wastes
June 30, 1994.
F038
Not generated from surface impoundment
cleanouts or closures
June 30, 1993.
F038
Generated from surface impoundment
cleanouts or closures
June 30, 1994.
F038
Mixed with radioactive wastes
June 30, 1994.
F039
Wastewater
Aug. 8, 1990.
F039
Nonwastewater
May 8, 1992.
K001 (organics)
b
All
Aug. 8, 1988.
K001
All others
Aug. 8, 1988.
K002
All
Aug. 8, 1990.
K003
All
Aug. 8, 1990.
K004
Wastewater
Aug. 8, 1990.
K004
Nonwastewater
Aug. 8, 1988.
K005
Wastewater
Aug. 8, 1990.
K005 Nonwastewater
June 8, 1989.
K006
All
Aug. 8, 1990.
K007
Wastewater
Aug. 8, 1990.
K007 Nonwastewater
June 8, 1989.
K008
Wastewater
Aug. 8, 1990.
K008
Nonwastewater
Aug. 8, 1988.
K009
All
167
Nonwastewater
All
All
All
All
June 8, 1989.
All
Aug. 8, 1988.
Aug. 8, 1988.
June 8, 1989.
K010
All
June 8, 1989.
K011
Wastewater
Aug. 8, 1990.
K011 Nonwastewater
June 8, 1989.
K013
Wastewater
Aug. 8, 1990.
K013 Nonwastewater
June 8, 1989.
K014
Wastewater
Aug. 8, 1990.
K014 Nonwastewater
June 8, 1989.
K015
Wastewater
Aug. 8, 1988.
K015
Aug. 8, 1990.
K016
Aug. 8, 1988.
K017
Aug. 8, 1990.
K018
Aug. 8, 1988.
K019
All
Aug. 8, 1988.
K020
All
Aug. 8, 1988.
K021
Wastewater
Aug. 8, 1990.
K021
Nonwastewater
Aug. 8, 1988.
K022
Wastewater
Aug. 8, 1990.
K022
Nonwastewater
Aug. 8, 1988.
K023
All
June 8, 1989.
K024
All
Aug. 8, 1988.
K025
Wastewater
Aug. 8, 1990.
K025
Nonwastewater
Aug. 8, 1988.
K026
Aug. 8, 1990.
K027
All
June 8, 1989.
K028 (metals)
Nonwastewater
Aug. 8, 1990.
K028
All others
K029
Wastewater
Aug. 8, 1990.
K029 Nonwastewater
June 8, 1989.
K030
Aug. 8, 1988.
K031
Wastewater
Aug. 8, 1990.
K031
Nonwastewater
May 8, 1992.
K032
All
Aug. 8, 1990.
K033
All
Aug. 8, 1990.
K034
All
Aug. 8, 1990.
K035
All
Aug. 8, 1990.
K036
Wastewater
June 8, 1989.
K036
Nonwastewater
Aug. 8, 1988.
K037
b
Wastewater
K037
Nonwastewater
K038
All
June 8, 1989.
K039
All
K040
All
June 8, 1989.
K041
All
Aug. 8, 1990.
168
Aug. 8, 1990.
K044
Aug. 8, 1988.
Aug. 8, 1988.
Aug. 8, 1990.
K050
Nov. 8, 1990.
K051
Aug. 8, 1990.
K060
K061
K062
K069 (Non-Calcium Sulfate)
K069
K042
All
K043
All
June 8, 1989.
All
Aug. 8, 1988.
K045
All
K046 (Nonreactive)
Nonwastewater
Aug. 8, 1988.
K046
All others
Aug. 8, 1990.
K047
All
K048
Wastewater
Aug. 8, 1990.
K048
Nonwastewater
Nov. 8, 1990.
K049
Wastewater
K049
Nonwastewater
Nov. 8, 1990.
Wastewater
Aug. 8, 1990.
K050
Nonwastewater
K051
Wastewater
Aug. 8, 1990.
Nonwastewater
Nov. 8, 1990.
K052
Wastewater
K052
Nonwastewater
Nov. 8, 1990.
Wastewater
Aug. 8, 1990.
K060
Nonwastewater
Aug. 8, 1988.
K061
Wastewater
Aug. 8, 1990.
Nonwastewater
June 30, 1992.
All
Aug. 8, 1988.
Nonwastewater
Aug. 8, 1988.
All others
Aug. 8, 1990.
K071
All
Aug. 8, 1990.
K073
All
Aug. 8, 1990.
K083
All
Aug. 8, 1990.
K084
Wastewater
Aug. 8, 1990.
K084
Nonwastewater
May 8, 1992.
K085
All
Aug. 8, 1990.
K086 (organics)
b
All
Aug. 8, 1988.
K086
All others
Aug. 8, 1988.
K087
All
Aug. 8, 1988.
K088
Mixed with radioactive wastes
Apr. 8, 1998.
K088
All others
Oct. 8, 1997.
K093
All
June 8, 1989.
K094
All
June 8, 1989.
K095
Wastewater
Aug. 8, 1990.
K095 Nonwastewater
June 8, 1989.
K096
Wastewater
Aug. 8, 1990.
K096 Nonwastewater
June 8, 1989.
K097
All
Aug. 8, 1990.
K098
All
Aug. 8, 1990.
169
K110
K110
K111
K112
K112
K113
K114
K115
K116
K117
K117
K118
K118
K123
K123
K124
K124
K125
K125
K126
K099
All
Aug. 8, 1988.
K100
Wastewater
Aug. 8, 1990.
K100
Nonwastewater
Aug. 8, 1988.
K101 (organics)
Wastewater
Aug. 8, 1988.
K101 (metals)
Wastewater
Aug. 8, 1990.
K101 (organics)
Nonwastewater
Aug. 8, 1988.
K101 (metals)
Nonwastewater
May 8, 1992.
K102 (organics)
Wastewater
Aug. 8, 1988.
K102 (metals)
Wastewater
Aug. 8, 1990.
K102 (organics)
Nonwastewater
Aug. 8, 1988.
K102 (metals)
Nonwastewater
May 8, 1992.
K103
All
Aug. 8, 1988.
K104
All
Aug. 8, 1988.
K105
All
Aug. 8, 1990.
K106
Wastewater
Aug. 8, 1990.
K106
Nonwastewater
May 8, 1992.
K107
Mixed with radioactive wastes
June 30, 1994.
K107
All others
Nov. 9, 1992.
K108
Mixed with radioactive wastes
June 30, 1994.
K108
All others
Nov. 9, 1992.
K109
Mixed with radioactive wastes
June 30, 1994.
K109
All others
Nov. 9, 1992.
Mixed with radioactive wastes
June 30, 1994.
All others
Nov. 9, 1992.
K111
Mixed with radioactive wastes
June 30, 1994.
All others
Nov. 9, 1992.
Mixed with radioactive wastes
June 30, 1994.
All others
Nov. 9, 1992.
All
June 8, 1989.
All
June 8, 1989.
All
June 8, 1989.
All
June 8, 1989.
Mixed with radioactive wastes
June 30, 1994.
All others
Nov. 9, 1992.
Mixed with radioactive wastes
June 30, 1994.
All others
Nov. 9, 1992.
Mixed with radioactive wastes
June 30, 1994.
All others
Nov. 9, 1992.
Mixed with radioactive wastes
June 30, 1994.
All others
Nov. 9, 1992.
Mixed with radioactive wastes
June 30, 1994.
All others
Nov. 9, 1992.
Mixed with radioactive wastes
June 30, 1994.
170
K126
K131
K131
K132
K132
K136
K136
K141
K141
K142
K142
K143
K143
K144
K144
K145
K145
K147
K147
K148
K148
All others
K150
Mixed with radioactive wastes
K150
All others
K156
K157
K157
K158
K159
K159
K160
K160
K161
K161
P001
P002
P003
P004
All others
Nov. 9, 1992.
Mixed with radioactive wastes
June 30, 1994.
All others
Nov. 9, 1992.
Mixed with radioactive wastes
June 30, 1994.
All others
Nov. 9, 1992.
Mixed with radioactive wastes
June 30, 1994.
All others
Nov. 9, 1992.
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
Mixed with radioactive wastes
Sep. 19, 1996.
All others
Dec. 19, 1994.
K149
Mixed with radioactive wastes
Sep. 19, 1996.
K149
Dec. 19, 1994.
Sep. 19, 1996.
All others
Dec. 19, 1994.
K151
Mixed with radioactive wastes
Sep. 19, 1996.
K151
Dec. 19, 1994.
K156
Mixed with radioactive wastes
Apr. 8, 1998.
All others
July 8, 1996.
Mixed with radioactive wastes
Apr. 8, 1998.
All others
July 8, 1996.
K158
Mixed with radioactive wastes
Apr. 8, 1998.
All others
July 8, 1996.
Mixed with radioactive wastes
Apr. 8, 1998.
All others
July 8, 1996.
Mixed with radioactive wastes
Apr. 8, 1998.
All others
July 8, 1996.
Mixed with radioactive wastes
Apr. 8, 1998.
All others
July 8, 1996.
All
Aug. 8, 1990.
All
Aug. 8, 1990.
All
Aug. 8, 1990.
All
Aug. 8, 1990.
171
P006
Aug. 8, 1990.
P007
P008
P009
P010
P010
P011
Aug. 8, 1990.
P012
P013 (barium)
June 8, 1989.
P014
Aug. 8, 1990.
P015
Aug. 8, 1990.
Aug. 8, 1990.
P018
Aug. 8, 1990.
P020
Aug. 8, 1990.
P021
June 8, 1989.
P023
Aug. 8, 1990.
P024
Aug. 8, 1990.
P026
Aug. 8, 1990.
Aug. 8, 1990.
June 8, 1989.
June 8, 1989.
Aug. 8, 1990.
P036
P039
June 8, 1989.
June 8, 1989.
June 8, 1989.
June 8, 1989.
P005
All
Aug. 8, 1990.
All
All
Aug. 8, 1990.
All
Aug. 8, 1990.
All
Aug. 8, 1990.
Wastewater
Aug. 8, 1990.
Nonwastewater
May 8, 1992.
P011
Wastewater
Aug. 8, 1990.
Nonwastewater
May 8, 1992.
P012
Wastewater
Nonwastewater
May 8, 1992.
Nonwastewater
Aug. 8, 1990.
P013
All others
All
All
Aug. 8, 1990.
P016
All
P017
All
All
All
All
P022
All
Aug. 8, 1990.
All
All
All
Aug. 8, 1990.
P027
All
P028
All
P029
All
P030
All
P031
All
P033
All
Aug. 8, 1990.
P034
All
Aug. 8, 1990.
Wastewater
Aug. 8, 1990.
P036
Nonwastewater
May 8, 1992.
P037
All
Aug. 8, 1990.
P038
Wastewater
Aug. 8, 1990.
P038
Nonwastewater
May 8, 1992.
All
June 8, 1989.
P040
All
P041
All
P042
All
Aug. 8, 1990.
P043
All
P044
All
P045
All
Aug. 8, 1990.
172
Aug. 8, 1990.
P048
P049
P051
P054
Aug. 8, 1990.
P057
P060
P064
P065
P066
P067
P069
P072
P073
P075
P076
Aug. 8, 1990.
P081
P088
P092
P093
P046
All
P047
All
Aug. 8, 1990.
All
Aug. 8, 1990.
All
Aug. 8, 1990.
P050
All
Aug. 8, 1990.
All
Aug. 8, 1990.
All
Aug. 8, 1990.
P056
All
All
Aug. 8, 1990.
P058
All
Aug. 8, 1990.
P059
All
Aug. 8, 1990.
All
Aug. 8, 1990.
P062
All
June 8, 1989.
P063
All
June 8, 1989.
All
Aug. 8, 1990.
Wastewater
Aug. 8, 1990.
P065
Nonwastewater
May 8, 1992.
All
Aug. 8, 1990.
All
Aug. 8, 1990.
P068
All
Aug. 8, 1990.
All
Aug. 8, 1990.
P070
All
Aug. 8, 1990.
P071
All
June 8, 1989.
All
Aug. 8, 1990.
All
Aug. 8, 1990.
P074
All
June 8, 1989.
All
Aug. 8, 1990.
All
Aug. 8, 1990.
P077
All
P078
All
Aug. 8, 1990.
All
Aug. 8, 1990.
P082
All
Aug. 8, 1990.
P084
All
Aug. 8, 1990.
P085
All
June 8, 1989.
P087
All
May 8, 1992.
All
Aug. 8, 1990.
P089
All
June 8, 1989.
P092
Wastewater
Aug. 8, 1990.
Nonwastewater
May 8, 1992.
All
Aug. 8, 1990.
P094
All
June 8, 1989.
P095
All
Aug. 8, 1990.
P096
All
Aug. 8, 1990.
173
P116
All
All
June 8, 1989.
Aug. 8, 1990.
All others
Mixed with radioactive wastes
Apr. 8, 1998.
Mixed with radioactive wastes
All others
July 8, 1996.
Apr. 8, 1998.
All others
Mixed with radioactive wastes
Apr. 8, 1998.
July 8, 1996.
Mixed with radioactive wastes
All others
July 8, 1996.
Apr. 8, 1998.
P097
All
June 8, 1989.
P098
All
June 8, 1989.
P099 (silver)
Wastewater
Aug. 8, 1990.
P099
All others
June 8, 1989.
P101
All
Aug. 8, 1990.
P102
All
Aug. 8, 1990.
P103
All
Aug. 8, 1990.
P104 (silver)
Wastewater
Aug. 8, 1990.
P104
All others
June 8, 1989.
P105
All
Aug. 8, 1990.
P106
All
June 8, 1989.
P108
All
Aug. 8, 1990.
P109
All
June 8, 1989.
P110
All
Aug. 8, 1990.
P111
All
June 8, 1989.
P112
All
Aug. 8, 1990.
P113
All
Aug. 8, 1990.
P114
All
Aug. 8, 1990.
P115
All
Aug. 8, 1990.
All
Aug. 8, 1990.
P118
All
Aug. 8, 1990.
P119
All
Aug. 8, 1990.
P120
Aug. 8, 1990.
P121
P122
All
P123
All
Aug. 8, 1990.
P127
Mixed with radioactive wastes
Apr. 8, 1998.
P127
July 8, 1996.
P128
P128
All others
July 8, 1996.
P185
Apr. 8, 1998.
P185
P188
Mixed with radioactive wastes
P188
All others
July 8, 1996.
P189
Mixed with radioactive wastes
Apr. 8, 1998.
P189
July 8, 1996.
P190
P190
All others
P191
Mixed with radioactive wastes
Apr. 8, 1998.
P191
All others
July 8, 1996.
P192
Apr. 8, 1998.
P192
P194
Mixed with radioactive wastes
174
All others
Mixed with radioactive wastes
Apr. 8, 1998.
July 8, 1996.
P199
Apr. 8, 1998.
P202
P204
P205
Aug. 8, 1990.
U007
U008
U012
U014
All
Aug. 8, 1990.
Aug. 8, 1990.
U017
P194
All others
July 8, 1996.
P196
Mixed with radioactive wastes
Apr. 8, 1998.
P196
July 8, 1996.
P197
P197
All others
P198
Mixed with radioactive wastes
Apr. 8, 1998.
P198
All others
July 8, 1996.
Mixed with radioactive wastes
Apr. 8, 1998.
P199
All others
July 8, 1996.
P201
Mixed with radioactive wastes
P201
All others
July 8, 1996.
P202
Mixed with radioactive wastes
Apr. 8, 1998.
All others
July 8, 1996.
P203
Mixed with radioactive wastes
Apr. 8, 1998.
P203
All others
July 8, 1996.
P204
Mixed with radioactive wastes
Apr. 8, 1998.
All others
July 8, 1996.
Mixed with radioactive wastes
Apr. 8, 1998.
P205
All others
July 8, 1996.
U001
All
Aug. 8, 1990.
U002
All
Aug. 8, 1990.
U003
All
Aug. 8, 1990.
U004
All
U005
All
Aug. 8, 1990.
U006
All
Aug. 8, 1990.
All
Aug. 8, 1990.
All
Aug. 8, 1990.
U009
All
Aug. 8, 1990.
U010
All
Aug. 8, 1990.
U011
All
Aug. 8, 1990.
All
Aug. 8, 1990.
All
Aug. 8, 1990.
U015
U016
All
All
Aug. 8, 1990.
U018
All
Aug. 8, 1990.
U019
All
Aug. 8, 1990.
U020
All
Aug. 8, 1990.
U021
All
Aug. 8, 1990.
U022
All
Aug. 8, 1990.
U023
All
Aug. 8, 1990.
U024
All
Aug. 8, 1990.
U025
All
Aug. 8, 1990.
175
U031
U026
All
Aug. 8, 1990.
U027
All
Aug. 8, 1990.
U028
All
June 8, 1989.
U029
All
Aug. 8, 1990.
U030
All
Aug. 8, 1990.
All
Aug. 8, 1990.
U032
All
Aug. 8, 1990.
U033
All
Aug. 8, 1990.
U034
All
Aug. 8, 1990.
U035
All
Aug. 8, 1990.
U036
All
Aug. 8, 1990.
U037
All
Aug. 8, 1990.
U038
All
Aug. 8, 1990.
U039
All
Aug. 8, 1990.
U041
All
Aug. 8, 1990.
U042
All
Aug. 8, 1990.
U043
All
Aug. 8, 1990.
U044
All
Aug. 8, 1990.
U045
All
Aug. 8, 1990.
U046
All
Aug. 8, 1990.
U047
All
Aug. 8, 1990.
U048 All
Aug. 8, 1990.
U049
All
All
All
All
All
All
Aug. 8, 1990.
U050
All
Aug. 8, 1990.
U051
All
Aug. 8, 1990.
U052
All
Aug. 8, 1990.
U053
All
Aug. 8, 1990.
U055
All
Aug. 8, 1990.
U056
Aug. 8, 1990.
U057
All
Aug. 8, 1990.
U058
All
June 8, 1989.
U059
All
Aug. 8, 1990.
U060
All
Aug. 8, 1990.
U061
Aug. 8, 1990.
U062
All
Aug. 8, 1990.
U063
All
Aug. 8, 1990.
U064
All
Aug. 8, 1990.
U066
Aug. 8, 1990.
U067
Aug. 8, 1990.
U068
All
Aug. 8, 1990.
U069
All
June 30, 1992.
U070
All
Aug. 8, 1990.
U071
Aug. 8, 1990.
176
All
All
All
All
All
All
All
All
U091
Aug. 8, 1990.
Aug. 8, 1990.
U094
All
Aug. 8, 1990.
All
All
All
All
All
All
U072
Aug. 8, 1990.
U073
All
Aug. 8, 1990.
U074
Aug. 8, 1990.
U075
Aug. 8, 1990.
U076
All
Aug. 8, 1990.
U077
All
Aug. 8, 1990.
U078
All
Aug. 8, 1990.
U079
Aug. 8, 1990.
U080
All
Aug. 8, 1990.
U081
All
Aug. 8, 1990.
U082
Aug. 8, 1990.
U083
Aug. 8, 1990.
U084
All
Aug. 8, 1990.
U085
All
Aug. 8, 1990.
U086
All
Aug. 8, 1990.
U087
June 8, 1989.
U088
June 8, 1989.
U089
All
Aug. 8, 1990.
U090
All
Aug. 8, 1990.
All
U092
All
U093
All
Aug. 8, 1990.
All
Aug. 8, 1990.
U095
All
Aug. 8, 1990.
U096
Aug. 8, 1990.
U097
All
U098
All
Aug. 8, 1990.
U099
All
Aug. 8, 1990.
U101
All
Aug. 8, 1990.
U102
All
June 8, 1989.
U103
All
Aug. 8, 1990.
U105
Aug. 8, 1990.
U106
All
Aug. 8, 1990.
U107
June 8, 1989.
U108
All
Aug. 8, 1990.
U109
All
Aug. 8, 1990.
U110
Aug. 8, 1990.
U111
Aug. 8, 1990.
U112
All
Aug. 8, 1990.
U113
All
Aug. 8, 1990.
U114
All
Aug. 8, 1990.
U115
Aug. 8, 1990.
U116
Aug. 8, 1990.
177
All
All
All
All
All
Wastewater
Nonwastewater
All
Wastewater
All
All
All
U117
All
Aug. 8, 1990.
U118
All
Aug. 8, 1990.
U119
All
Aug. 8, 1990.
U120
All
Aug. 8, 1990.
U121
Aug. 8, 1990.
U122
All
Aug. 8, 1990.
U123
Aug. 8, 1990.
U124
All
Aug. 8, 1990.
U125
All
Aug. 8, 1990.
U126
Aug. 8, 1990.
U127
All
Aug. 8, 1990.
U128
All
Aug. 8, 1990.
U129
Aug. 8, 1990.
U130
All
Aug. 8, 1990.
U131
All
Aug. 8, 1990.
U132
Aug. 8, 1990.
U133
All
Aug. 8, 1990.
U134
All
Aug. 8, 1990.
U135
All
Aug. 8, 1990.
U136
Aug. 8, 1990.
U136
May 8, 1992.
U137
Aug. 8, 1990.
U138
All
Aug. 8, 1990.
U140
All
Aug. 8, 1990.
U141
All
Aug. 8, 1990.
U142
All
Aug. 8, 1990.
U143
All
Aug. 8, 1990.
U144
All
Aug. 8, 1990.
U145
All
Aug. 8, 1990.
U146
All
Aug. 8, 1990.
U147
All
Aug. 8, 1990.
U148
All
Aug. 8, 1990.
U149
All
Aug. 8, 1990.
U150
All
Aug. 8, 1990.
U151
Aug. 8, 1990.
U151
Nonwastewater
May 8, 1992.
U152
Aug. 8, 1990.
U153
All
Aug. 8, 1990.
U154
All
Aug. 8, 1990.
U155
Aug. 8, 1990.
U156
All
Aug. 8, 1990.
U157
All
Aug. 8, 1990.
U158
Aug. 8, 1990.
178
All
All
All
All
All
All
All
All
U187
All
All
All
All
All
U159
All
Aug. 8, 1990.
U160
All
Aug. 8, 1990.
U161
Aug. 8, 1990.
U162
All
Aug. 8, 1990.
U163
All
Aug. 8, 1990.
U164
Aug. 8, 1990.
U165
All
Aug. 8, 1990.
U166
All
Aug. 8, 1990.
U167
Aug. 8, 1990.
U168
All
Aug. 8, 1990.
U169
All
Aug. 8, 1990.
U170
Aug. 8, 1990.
U171
All
Aug. 8, 1990.
U172
All
Aug. 8, 1990.
U173
Aug. 8, 1990.
U174
All
Aug. 8, 1990.
U176
All
Aug. 8, 1990.
U177
Aug. 8, 1990.
U178
All
Aug. 8, 1990.
U179
All
Aug. 8, 1990.
U180
Aug. 8, 1990.
U181
All
Aug. 8, 1990.
U182
All
Aug. 8, 1990.
U183
Aug. 8, 1990.
U184
All
Aug. 8, 1990.
U185
All
Aug. 8, 1990.
U186
All
Aug. 8, 1990.
All
Aug. 8, 1990.
U188
All
Aug. 8, 1990.
U189
Aug. 8, 1990.
U190
All
June 8, 1989.
U191
All
Aug. 8, 1990.
U192
Aug. 8, 1990.
U193
All
Aug. 8, 1990.
U194
All
June 8, 1989.
U196
Aug. 8, 1990.
U197
All
Aug. 8, 1990.
U200
All
Aug. 8, 1990.
U201
Aug. 8, 1990.
U202
All
Aug. 8, 1990.
U203
All
Aug. 8, 1990.
U204
Aug. 8, 1990.
U205
All
Aug. 8, 1990.
179
All
All
All
All
All
All
All
All
All
All
All
Mixed with radioactive wastes
All others
All others
U206
All
Aug. 8, 1990.
U207
Aug. 8, 1990.
U208
All
Aug. 8, 1990.
U209
All
Aug. 8, 1990.
U210
Aug. 8, 1990.
U211
All
Aug. 8, 1990.
U213
All
Aug. 8, 1990.
U214
Aug. 8, 1990.
U215
All
Aug. 8, 1990.
U216
All
Aug. 8, 1990.
U217
Aug. 8, 1990.
U218
All
Aug. 8, 1990.
U219
All
Aug. 8, 1990.
U220
Aug. 8, 1990.
U221
All
June 8, 1989.
U222
All
Aug. 8, 1990.
U223
June 8, 1989.
U225
All
Aug. 8, 1990.
U226
All
Aug. 8, 1990.
U227
Aug. 8, 1990.
U228
All
Aug. 8, 1990.
U234
All
Aug. 8, 1990.
U235
June 8, 1989.
U236
All
Aug. 8, 1990.
U237
All
Aug. 8, 1990.
U238
Aug. 8, 1990.
U239
All
Aug. 8, 1990.
U240
All
Aug. 8, 1990.
U243
Aug. 8, 1990.
U244
All
Aug. 8, 1990.
U246
All
Aug. 8, 1990.
U247
Aug. 8, 1990.
U248
All
Aug. 8, 1990.
U249
All
Aug. 8, 1990.
U271
Apr. 8, 1998.
U271
All others
July 8, 1996.
U277
Mixed with radioactive wastes
Apr. 8, 1998.
U277
July 8, 1996.
U278
Mixed with radioactive wastes
Apr. 8, 1998.
U278
July 8, 1996.
U279
Mixed with radioactive wastes
Apr. 8, 1998.
U279
All others
July 8, 1996.
U280
Mixed with radioactive wastes
Apr. 8, 1998.
180
All others
All others
July 8, 1996.
U378
Mixed with radioactive wastes
U280
July 8, 1996.
U328
Mixed with radioactive wastes
June 30, 1994.
U328
Nov. 9, 1992.
U353
Mixed with radioactive wastes
June 30, 1994.
U353
All others
Nov. 9, 1992.
U359
Mixed with radioactive wastes
June 30, 1994.
U359
All others
Nov. 9, 1992.
U364
Mixed with radioactive wastes
Apr. 8, 1998.
U364
All others
July 8, 1996.
U365
Mixed with radioactive wastes
Apr. 8, 1998.
U365
All others
July 8, 1996.
U366
Mixed with radioactive wastes
Apr. 8, 1998.
U366
All others
July 8, 1996.
U367
Mixed with radioactive wastes
Apr. 8, 1998.
U367
All others
U372
Mixed with radioactive wastes
Apr. 8, 1998.
U372
All others
July 8, 1996.
U373
Mixed with radioactive wastes
Apr. 8, 1998.
U373
All others
July 8, 1996.
U375
Mixed with radioactive wastes
Apr. 8, 1998.
U375
All others
July 8, 1996.
U376
Mixed with radioactive wastes
Apr. 8, 1998.
U376
All others
July 8, 1996.
U377
Mixed with radioactive wastes
Apr. 8, 1998.
U377
All others
July 8, 1996.
Mixed with radioactive wastes
Apr. 8, 1998.
U378
All others
July 8, 1996.
U379
Mixed with radioactive wastes
Apr. 8, 1998.
U379
All others
July 8, 1996.
U381
Mixed with radioactive wastes
Apr. 8, 1998.
U381
All others
July 8, 1996.
U382
Mixed with radioactive wastes
Apr. 8, 1998.
U382
All others
July 8, 1996.
U383
Mixed with radioactive wastes
Apr. 8, 1998.
U383
All others
July 8, 1996.
U384
Apr. 8, 1998.
U384
All others
July 8, 1996.
U385
Mixed with radioactive wastes
Apr. 8, 1998.
U385
All others
July 8, 1996.
U386
Mixed with radioactive wastes
Apr. 8, 1998.
U386
All others
July 8, 1996.
U387
Mixed with radioactive wastes
Apr. 8, 1998.
U387
All others
July 8, 1996.
181
July 8, 1996.
Mixed with radioactive wastes
All others
Mixed with radioactive wastes
All others
U389
Mixed with radioactive wastes
Apr. 8, 1998.
U389
All others
July 8, 1996.
U390
Mixed with radioactive wastes
Apr. 8, 1998.
U390
All others
July 8, 1996.
U391
Mixed with radioactive wastes
Apr. 8, 1998.
U391
All others
July 8, 1996.
U392
Mixed with radioactive wastes
Apr. 8, 1998.
U392
All others
July 8, 1996.
U393
Mixed with radioactive wastes
Apr. 8, 1998.
U393
All others
July 8, 1996.
U394
Mixed with radioactive wastes
Apr. 8, 1998.
U394
All others
July 8, 1996.
U395
Mixed with radioactive wastes
Apr. 8, 1998.
U395
All others
July 8, 1996.
U396
Mixed with radioactive wastes
Apr. 8, 1998.
U396
All others
July 8, 1996.
U400
Mixed with radioactive wastes
Apr. 8, 1998.
U400
All others
July 8, 1996.
U401
Mixed with radioactive wastes
Apr. 8, 1998.
U401
All others
July 8, 1996.
U402
Mixed with radioactive wastes
Apr. 8, 1998.
U402
All others
U403
Mixed with radioactive wastes
Apr. 8, 1998.
U403
All others
July 8, 1996.
U404
Mixed with radioactive wastes
Apr. 8, 1998.
U404
All others
July 8, 1996.
U407
Mixed with radioactive wastes
Apr. 8, 1998.
U407
All others
July 8, 1996.
U409
Mixed with radioactive wastes
Apr. 8, 1998.
U409
All others
July 8, 1996.
U410
Apr. 8, 1998.
U410
July 8, 1996.
U411
Apr. 8, 1998.
U411
July 8, 1996.
a This table does not include mixed radioactive wastes (from the First, Second, and Third
rules) which are receiving a national capacity variance until May 8, 1992. This table
also does not include contaminated soil and debris wastes.
b The standard was revised in the Third Third Final Rule (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).
182
Dec. 19, 1994
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 (which USEPA adopted at 59 Fed.
Reg. 47982 (Sept. 19, 1994) and the Board adopted in docket R95-6 by orders dated
June 1 and 15, 1995); the original effective date was August 8, 1990.
e The standards for selected reactive wastes was revised in the Phase III Final Rule
(which USEPA adopted at 61 Fed. Reg. 15566 (Apr. 8, 1996) and the Board adopted
in docket R96-10/R97-3/R97-5 (consolidated) by an order dated November 6, 1997);
the original effective date was August 8, 1990.
TABLE 2
SUMMARY OF EFFECTIVE DATES OF LAND DISPOSAL
RESTRICTIONS FOR CONTAMINATED SOIL AND DEBRIS (CSD)
Restricted hazardous waste in CSD
Effective date
1. Solvent-(F001-F005) and dioxin-(F020-F023 and F026-F028) containing soil
and debris from CERCLA response or RCRA corrective actions.
Nov. 8, 1990.
2. Soil and debris not from CERCLA response or RCRA corrective actions
contaminated with less than one percent total solvents (F001-F005) or dioxins
(F020-F023 and F026-F028).
Nov. 8, 1988.
3. All soil and debris contaminated with First Third wastes for which treatment
standards are based on incineration.
Aug. 8, 1990.
4. All soil and debris contaminated with Second Third wastes for which treatment
standards are based on incineration.
June 8, 1991.
5. All soil and debris contaminated with Third Third wastes or, First or Second
Third “soft hammer” wastes which had treatment standards promulgated in the
Third Third rule, for which treatment standards are based on incineration,
vitrification, or mercury retorting, acid leaching followed by chemical
precipitation, or thermal recovery of metals, as well as all inorganic solids
debris contaminated with D004-D011 wastes, and all soil and debris
contaminated with mixed RCRA/radioactive wastes.
May 8, 1992.
6. Soil and debris contaminated with D012-D043, K141-K145, and K147-151
wastes.
Dec. 19, 1994.
7. Debris (only) contaminated with F037, F038, K107-K112, K117, K118,
K123-K126, K131, K132, K136, U328, U353, U359.
8. Soil and debris contaminated with K156- K161, P127, P128, P188-P192,
P194, P196- P199, P201-P205, U271, U277-U280, U364-U367, U372,
U373, U375-U379, U381-U387, U389-U396, U400-U404, U407, and
U409-U411 wastes.
July 8, 1996.
9. Soil and debris contaminated with K088 wastes.
Oct. 8, 1997.
183
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.
(Source: Amended at 26 Ill. Reg. ________, effective ______________________)
D001
NA
NA
12. Soil and debris contaminated with newly identified D004-D011 toxicity
characteristic wastes and mineral processing wastes.
Aug. 24, 1998.
13. Soil and debris contaminated with mixed radioactive newly identified D011
characteristic wastes and mineral processing wastes.
May 26, 2000.
BOARD NOTE: This table is provided for the convenience of the reader.
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 Subcategory
1
Regulated Hazardous Constituent
Wastewaters Nonwastewaters
Common Name
CAS
2 Number
Concentration in
mg/l
3; or Techno-
logy Code
4
Concentration in
mg/kg
5 unless
noted as “mg/l
TCLP”; or Tech-
nology Code
4
9
Ignitable Characteristic Wastes, except for the 35 Ill. Adm. Code 721.121(a)(1) High TOC
Subcategory.
NA
DEACT and meet
Section 728.148
standards
8; or
RORGS; or
CMBST
DEACT and meet
Section 728.148
standards
8; or
RORGS; or
CMBST
D001
9
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
RORGS;
CMBST;
or POLYM
184
DEACT and meet
Section 728.148
standards
(Note: This subcategory consists of nonwastewaters only.)
Arsenic 7440-38-2
NA
Selenium 7782-49-2
7440-22-4
NA
DEACT and meet
Section 728.148
standards
DEACT
D003
NA
D002
9
Corrosive Characteristic Wastes.
NA
NA
DEACT and meet
Section 728.148
standards
8
8
D002, D004, D005, D006, D007, D008, D009, D010, D011
Radioactive high level wastes generated during the reprocessing of fuel rods.
Corrosivity (pH)
NA
NA
HLVIT
NA
HLVIT
Barium 7440-39-3
NA
HLVIT
Cadmium 7440-43-9
HLVIT
Chromium (Total)
7440-47-3
NA
HLVIT
Lead 7439-92-1
NA
HLVIT
Mercury 7439-97-6
NA
HLVIT
NA
HLVIT
Silver
NA
HLVIT
D003
9
Reactive Sulfides Subcategory based on 35 Ill. Adm. Code 721.123(a)(5).
NA NA
DEACT
DEACT
D003
9
Explosive subcategory based on 35 Ill. Adm. Code 721.123(a)(6), (a)(7), and (a)(8).
NA
DEACT and meet
Section 728.148
standards
8
8
D003
9
Unexploded ordnance and other explosive devices that have been the subject of an emergency
response.
NA NA
DEACT
9
Other Reactives Subcategory based on 35 Ill. Adm. Code 721.123(a)(1).
NA
DEACT and meet
Section 728.148
standards
8
DEACT and meet
Section 728.148
standards
8
185
D006
7440-43-9
7440-43-9
D003
9
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
standards
8
D003
9
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
D004
9
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for arsenic based
on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Arsenic
7440-38-2
1.4 and meet
Section 728.148
standards
8
5.0 mg/l TCLP
and meet Section
728.148 standards
8
D005
9
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for barium based
on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Barium
7440-39-3
1.2 and meet
Section 728.148
standards
8
21 mg/l TCLP and
meet Section
728.148 standards
8
9
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
0.69 and meet
Section 728.148
standards
8
0.11 mg/l TCLP
and meet Section
728.148 standards
8
D006
9
Cadmium-Containing Batteries Subcategory
(Note: This subcategory consists of nonwastewaters only.)
Cadmium
NA
RTHRM
186
Chromium (Total)
0.60 mg/l TCLP
and meet Section
728.148 standards
D008
7439-92-1
7439-92-1
MACRO
NA
D009
D007
9
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for chromium
based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
7440-47-3
2.77 and meet
Section 728.148
standards
8
8
9
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
0.69 and meet
Section 728.148
standards
8
0.75 mg/l TCLP
and meet Section
728.148 standards
8
D008
9
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
NA
RLEAD
D008
9
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
D009
9
Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for
mercury based on the toxicity characteristic leaching procedure (TCLP) in 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
IMERC;
or
RMERC
9
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,
187
7439-97-6
NA
D009
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.
5.7 mg/l TCLP
and meet Section
728.148 standards
including incinerator residues and residues from RMERC. (High Mercury-Inorganic
Subcategory)
Mercury
NA
RMERC
D009
9
Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for
mercury based on the toxicity characteristic leaching procedure (TCLP) in 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 standards
8
D009
9
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 standards
8
D009
9
All D009 wastewaters.
Mercury
7439-97-6
0.15 and meet
Section 728.148
standards
8
NA
D009
9
Elemental mercury contaminated with radioactive materials.
(Note: This subcategory consists of nonwastewaters only.)
Mercury 7439-97-6
AMLGM
9
Hydraulic oil contaminated with Mercury Radioactive Materials Subcategory.
(Note: This subcategory consists of nonwastewaters only.)
Mercury 7439-97-6
NA
IMERC
D010
9
Selenium 7782-49-2
0.82
8
188
D011
7440-22-4
Wastes that are TC for Endrin based on the toxicity characteristic leaching procedure (TCLP)
in SW-846 Method 1311.
0.13 and meet
Section 728.148
standards
7421-93-4
Wastes that are TC for Lindane based on the toxicity characteristic leaching procedure (TCLP)
in SW-846 Method 1311.
0.066 and meet
Section 728.148
standards
319-85-7 CARBN;
0.066 and meet
Section 728.148
standards
9
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
0.43
0.14 mg/l TCLP
and meet Section
728.148 standards
8
D012
9
Endrin 72-20-8
BIODG;
or
CMBST
8
Endrin aldehyde
BIODG; or
CMBST
0.13 and meet
Section 728.148
standards
8
D013
9
α
-BHC
319-84-6 CARBN; or
CMBST
8
β
-BHC
or
CMBST
0.066 and meet
Section 728.148
standards
8
δ
-BHC
319-86-8 CARBN; or
CMBST
8
χ
-BHC
γ
-BHC (Lindane)
58-89-9 CARBN; or
CMBST
0.066 and meet
Section 728.148
standards
D014
72-43-5
8
9
Wastes that are TC for Methoxychlor based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
Methoxychlor
WETOX
or
CMBST
0.18 and meet
Section 728.148
standards
8
189
Wastes that are TC for Toxaphene based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
2.6 and meet
Section 728.148
standards
D016
94-75-7 CHOXD;
Wastes that are TC for 2,4,5-TP (Silvex) based on the toxicity characteristic leaching
procedure (TCLP) in SW-846 Method 1311.
7.9 and meet
Section 728.148
standards
D018
71-43-2
0.057 and meet
Section 728.148
standards
Wastes that are TC for Chlordane based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
D015
9
Toxaphene 8001-35-2
BIODG
or
CMBST
8
9
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-Dichlorophenoxy-
acetic acid)
BIODG;
or CMBST
10 and meet
Section 728.148
standards
8
D017
9
2,4,5-TP (Silvex)
93-72-1
CHOXD or
CMBST
8
9
Wastes that are TC for Benzene based on the toxicity characteristic leaching procedure (TCLP)
in SW-846 Method 1311.
Benzene
0.14 and meet
Section 728.148
standards
8
10 and meet
Section 728.148
standards
8
D019
9
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
8
6.0 and meet
Section 728.148
standards
8
D020
9
Chlordane (
α
and
χ
isomers)
57-74-9
0.0033 and meet
Section 728.148
standards
8
0.26 and meet
Section 728.148
standards
8
190
Chlorobenzene
6.0 and meet
Section 728.148
standards
D022
Wastes that are TC for o-Cresol based on the toxicity characteristic leaching procedure (TCLP)
in SW-846 Method 1311.
0.11 and meet
Section 728.148
standards
m-Cresol
Wastes that are TC for p-Cresol based on the toxicity characteristic leaching procedure (TCLP)
in SW-846 Method 1311.
0.77 and meet
Section 728.148
standards
Wastes that are TC for Cresols (Total) based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
0.88 and meet
Section 728.148
standards
D021
9
Wastes that are TC for Chlorobenzene based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
108-90-7
0.057 and meet
Section 728.148
standards
8
8
9
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
standards
8
6.0 and meet
Section 728.148
standards
8
D023
9
o-Cresol
95-48-7
8
5.6 and meet
Section 728.148
standards
8
D024
9
Wastes that are TC for m-Cresol based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
(difficult to distinguish from p-
cresol)
108-39-4
0.77 and meet
Section 728.148
standards
8
5.6 and meet
Section 728.148
standards
8
D025
9
p-Cresol
(difficult to distinguish from m-
cresol)
106-44-5
8
5.6 and meet
Section 728.148
standards
8
D026
9
Cresol-mixed isomers (Cresylic
acid)
(sum of o-, m-, and p-cresol
concentrations)
1319-77-3
8
11.2 and meet
Section 728.148
standards
8
191
Wastes that are TC for p-Dichlorobenzene based on the toxicity characteristic leaching
procedure (TCLP) in SW-846 Method 1311.
1,2-Dichloroethane
6.0 and meet
Section 728.148
standards
D029
75-35-4
0.32 and meet
Section 728.148
standards
140 and meet
Section 728.148
standards
Wastes that are TC for Heptachlor based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
Heptachlor epoxide
0.066 and meet
Section 728.148
standards
D027
9
p-Dichlorobenzene (1,4-
Dichlorobenzene)
106-46-7
0.090 and meet
Section 728.148
standards
8
6.0 and meet
Section 728.148
standards
8
D028
9
Wastes that are TC for 1,2-Dichloroethane based on the toxicity characteristic leaching
procedure (TCLP) in SW-846 Method 1311.
107-06-2
0.21 and meet
Section 728.148
standards
8
8
9
Wastes that are TC for 1,1-Dichloroethylene based on the toxicity characteristic leaching
procedure (TCLP) in SW-846 Method 1311.
1,1-Dichloroethylene
0.025 and meet
Section 728.148
standards
8
6.0 and meet
Section 728.148
standards
8
D030
9
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
8
8
D031
9
Heptachlor
76-44-8
0.0012 and meet
Section 728.148
standards
8
0.066 and meet
Section 728.148
standards
8
1024-57-3
0.016 and meet
Section 728.148
standards
8
8
192
118-74-1
0.055 and meet
Section 728.148
standards
D034
Wastes that are TC for Hexachloroethane based on the toxicity characteristic leaching
procedure (TCLP) in SW-846 Method 1311.
67-72-1
0.28 and meet
Section 728.148
standards
36 and meet
Section 728.148
standards
D036
Wastes that are TC for Nitrobenzene based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
98-95-3
Pentachlorophenol
0.089 and meet
Section 728.148
standards
7.4 and meet
Section 728.148
standards
D032
9
Wastes that are TC for Hexachlorobenzene based on the toxicity characteristic leaching
procedure (TCLP) in SW-846 Method 1311.
Hexachlorobenzene
0.055 and meet
Section 728.148
standards
8
10 and meet
Section 728.148
standards
8
D033
9
Wastes that are TC for Hexachlorobutadiene based on the toxicity characteristic leaching
procedure (TCLP) in SW-846 Method 1311.
Hexachlorobutadiene
87-68-3
8
5.6 and meet
Section 728.148
standards
8
9
Hexachloroethane
0.055 and meet
Section 728.148
standards
8
30 and meet
Section 728.148
standards
8
D035
9
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
8
8
9
Nitrobenzene
0.068 and meet
Section 728.148
standards
8
14 and meet
Section 728.148
standards
8
D037
9
Wastes that are TC for Pentachlorophenol based on the toxicity characteristic leaching
procedure (TCLP) in SW-846 Method 1311.
87-86-5
8
8
193
110-86-1
0.056 and meet
Section 728.148
standards
0.27 and meet
Section 728.148
standards
D038
9
Wastes that are TC for Pyridine based on the toxicity characteristic leaching procedure (TCLP)
in SW-846 Method 1311.
Pyridine
0.014 and meet
Section 728.148
standards
8
16 and meet
Section 728.148
standards
8
D039
9
Wastes that are TC for Tetrachloroethylene based on the toxicity characteristic leaching
procedure (TCLP) in SW-846 Method 1311.
Tetrachloroethylene
127-18-4
8
6.0 and meet
Section 728.148
standards
8
D040
9
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
standards
8
6.0 and meet
Section 728.148
standards
8
D041
9
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
standards
8
7.4 and meet
Section 728.148
standards
8
D042
9
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
standards
8
7.4 and meet
Section 728.148
standards
8
D043
9
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
8
6.0 and meet
Section 728.148
standards
8
194
Acetone 67-64-1
5.6
NA
0.057
o-Cresol 95-48-7
(difficult to distinguish from m-
cresol)
108-94-1
33
0.057
Isobutyl alcohol 78-83-1
0.089
14
127-18-4
Toluene 108-88-3
71-55-6
0.054
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, cyclo-
hexanone, 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, trichloromono-
fluoromethane, or xylenes (except as specifically noted in other subcategories). See further
details of these listings in 35 Ill. Adm. Code 721.131
0.28
160
Benzene 71-43-2
0.14
10
n-Butyl alcohol
71-36-3
2.6
Carbon disulfide
75-15-0
3.8
Carbon tetrachloride 56-23-5
6.0
Chlorobenzene 108-90-7
0.057
6.0
0.11
5.6
m-Cresol
(difficult to distinguish from p-
cresol)
108-39-4 0.77
5.6
p-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
0.36
NA
o-Dichlorobenzene 95-50-1
0.088 6.0
Ethyl acetate
141-78-6
0.34
Ethyl benzene
100-41-4
10
Ethyl ether
60-29-7
0.12
160
5.6 170
Methanol 67-56-1
5.6
NA
Methylene chloride
75-9-2
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
Pyridine 110-86-1
0.014
16
Tetrachloroethylene
0.056 6.0
0.080
10
1,1,1-Trichloroethane
0.054
6.0
1,1,2-Trichloroethane 79-00-5
6.0
195
1330-20-7 0.32
Cyclohexanone 108-94-1
1,1,2-Trichloro-1,2,2-trifluoro-
ethane
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)
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
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
196
Nickel
Cadmium
Chromium (Total)
30
0.69
0.75 mg/l TCLP
Silver
7440-43-9
57-12-5
Cyanides (Amenable)
7
Silver
7440-43-9 NA
7440-47-3
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
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.
7440-43-9
NA
0.11 mg/l TCLP
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
Lead
7439-92-1
Nickel
7440-02-0
3.98
11 mg/l TCLP
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
NA
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
1.2 590
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
7440-22-4
NA
0.14 mg/l TCLP
F010
Quenching bath residues from oil baths from metal heat treating operations where cyanides are
used in the process.
Cyanides (Total)
7 57-12-5
1.2 590
Cyanides (Amenable)
7 57-12-5
0.86
NA
F011
Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations.
Cadmium
0.11 mg/l TCLP
Chromium (Total)
2.77
0.60 mg/l TCLP
Cyanides (Total)
7 57-12-5
1.2 590
197
Cyanides (Amenable)
2.77
57-12-5
Cyanides (Amenable)
F019
0.60 mg/l TCLP
57-12-5 1.2
0.001
7 57-12-5
0.86
30
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
Silver
7440-22-4
NA
0.14 mg/l TCLP
F012
Quenching wastewater treatment sludges from metal heat treating operations where cyanides
are used in the process.
Cadmium
7440-43-9
NA
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
0.60 mg/l TCLP
Cyanides (Total)
7
1.2 590
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
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
Cyanides (Total)
7
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 Hexachloro-
dibenzo-p-dioxins)
NA 0.000063
HxCDFs (All Hexachloro-
dibenzofurans)
NA55684-94-1 0.000063
0.001
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA36088-22-9 0.000063
0.001
198
PeCDFs (All Pentachloro-
dibenzofurans)
NA30402-15-4 0.000035
0.001
Pentachlorophenol
87-86-5 0.089
7.4
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA41903-57-5 0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA55722-27-5 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
CMBST
11 CMBST
11
2-Chloro-1,3-butadiene 126-99-8
0.057
0.28
3-Chloropropylene 107-05-1
0.036 30
1,1-Dichloroethane
30
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
1,1,2-Trichloroethane 79-00-5
0.054
6.0
Trichloroethylene 79-01-6
0.054
6.0
199
1,1,2-Trichloroethane
Vinyl chloride
0.000063
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
79-00-5
0.054
6.0
Trichloroethylene 79-01-6
0.054
6.0
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 Hexachloro-
dibenzo-p-dioxins)
NA
0.001
HxCDFs (All Hexachloro-
dibenzofurans)
NA55684-94-1 0.000063
0.001
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA36088-22-9 0.000063
0.001
PeCDFs (All Pentachloro-
dibenzofurans)
NA30402-15-4 0.000035
0.001
0.089
Pentachlorophenol
87-86-5
7.4
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA41903-57-5 0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA55722-27-5 0.000063
0.001
2,4,5-Trichlorophenol 95-95-4
2,4,6-Trichlorophenol
58-90-2
0.18
7.4
88-06-2
0.035
7.4
2,3,4,6-Tetrachlorophenol
0.030
7.4
200
0.001
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 Hexachloro-
dibenzo-p-dioxins)
NA 0.000063
HxCDFs (All Hexachloro-
dibenzofurans)
NA55684-94-1 0.000063
0.001
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA36088-22-9 0.000063
0.001
PeCDFs (All Pentachloro-
dibenzofurans)
NA30402-15-4 0.000035
0.001
Pentachlorophenol
87-86-5 0.089
7.4
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA41903-57-5 0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA55722-27-5 0.000063
0.001
2,4,5-Trichlorophenol 95-95-4
0.18
7.4
2,4,6-Trichlorophenol
2,3,4,6-Tetrachlorophenol 58-90-2
Anthracene 120-12-7
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)
fluoranthene)
6.8
Benzo(a)pyrene 50-32-8
Dibenz(a,h)anthracene
88-06-2
0.035
7.4
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
0.059
3.4
Benz(a)anthracene 56-55-3
0.059 3.4
205-99-2 0.11
6.8
Benzo(k)fluoranthene (difficult
to distinguish from benzo(b)
fluoranthene)
207-08-9 0.11
0.061
3.4
Chrysene 218-01-9
0.059
3.4
53-70-3
0.055
8.2
2-4-Dimethyl phenol 105-67-9
0.036
14
201
Fluorene 86-73-7
0.000063 or
CMBST
193-39-5
Naphthalene
0.001 or CMBST
Phenanthrene 85-01-8
108-95-2
0.067
0.000063 or
CMBST
58-90-2
0.035
2.77
F034
0.059
3.4
Fluorene 86-73-7
0.059
3.4
Hexachlorodibenzo-p-dioxins NA
0.000063 or
CMBST
11
0.001 or CMBST
11
Hexachlorodibenzofurans NA
11
0.001 or CMBST
11
Indeno (1,2,3-c,d) pyrene
0.0055
3.4
91-20-3 0.059
5.6
Pentachlorodibenzo-p-dioxins NA
0.000063 or
CMBST
11
0.001 or CMBST
11
Pentachlorodibenzofurans NA
0.000035 or
CMBST
11
11
Pentachlorophenol
87-86-5 0.089
7.4
0.059
5.6
Phenol
0.039
6.2
Pyrene 129-00-0
8.2
Tetrachlorodibenzo-p-dioxins NA
0.000063 or
CMBST
11
0.001 or CMBST
11
Tetrachlorodibenzofurans NA
11
0.001 or CMBST
11
2,3,4,6-Tetrachlorophenol
0.030
7.4
2,4,6-Trichlorophenol 88-06-2
7.4
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
Chromium (Total)
7440-47-3
0.60 mg/l TCLP
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
3.4
Anthracene 120-12-7
0.059
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
0.059
3.4
202
3.4
0.067
5.0 mg/l TCLP
1.4
0.60 mg/l TCLP
83-32-9
0.059
10
bis(2-Ethylhexyl) phthalate 117-81-7
218-01-9
0.057
10
Phenanthrene 85-01-8
108-95-2
0.067
10
Indeno (1,2,3-c,d) pyrene
193-39-5
0.0055
Naphthalene 91-20-3 0.059
5.6
Phenanthrene 85-01-8
0.059
5.6
Pyrene 129-00-0
8.2
Arsenic
7440-38-2
1.4
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
5.0 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
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
0.059
NA
Anthracene 120-12-7
3.4
Benzene 71-43-2
0.14
Benz(a)anthracene 56-55-3
0.059 3.4
Benzo(a)pyrene 50-32-8
0.061
3.4
0.28
28
Chrysene
0.059
3.4
Di-n-butyl phthalate 84-74-2
28
Ethylbenzene 100-41-4
0.057
Fluorene 86-73-7
0.059
NA
Naphthalene 91-20-3 0.059
5.6
0.059
5.6
Phenol
0.039
6.2
Pyrene 129-00-0
8.2
Toluene 108-88-3
0.080
203
30
Nickel
71-43-2
bis(2-Ethylhexyl) phthalate 117-81-7
218-01-9
0.057
10
Phenanthrene 85-01-8
108-95-2
0.067
10
30
Nickel
F039
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7 0.32
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
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
0.14
10
Benzo(a)pyrene 50-32-8
0.061
3.4
0.28
28
Chrysene
0.059
3.4
Di-n-butyl phthalate 84-74-2
28
Ethylbenzene 100-41-4
0.057
Fluorene 86-73-7
0.059
NA
Naphthalene 91-20-3 0.059
5.6
0.059
5.6
Phenol
0.039
6.2
Pyrene 129-00-0
8.2
Toluene 108-88-3
0.080
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7 0.32
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
7440-02-0
NA
11 mg/l TCLP
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
204
Acetone 67-64-1
75-05-8
0.010
140
Aldrin 309-00-2
92-67-1 0.13
0.81
3.4
β
-BHC
319-86-8 0.023
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
0.28
160
Acetonitrile
5.6
NA
Acetophenone 96-86-2
9.7
2-Acetylaminofluorene 53-96-3
0.059
Acrolein 107-02-8
0.29
NA
Acrylonitrile 107-13-1
0.24
84
0.021
0.066
4-Aminobiphenyl
NA
Aniline 62-53-3
14
Anthracene 120-12-7
0.059
Aramite 140-57-8
0.36
NA
α
-BHC
319-84-6 0.00014
0.066
319-85-7 0.00014
0.066
δ
-BHC
0.066
χ
-BHC
γ
-BHC
58-89-9 0.0017
0.066
Benzene 71-43-2
0.059
6.8
Benzo(a)pyrene 50-32-8
75-27-4
0.11
n-Butyl alcohol
2-sec-Butyl-4,6-dinitrophenol
(Dinoseb)
75-15-0
0.14
10
Benz(a)anthracene 56-55-3
3.4
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)-
fluoranthene)
205-99-2 0.11
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
0.061
3.4
Bromodichloromethane
0.35
15
Methyl bromide (Bromo-
methane)
74-83-9
15
4-Bromophenyl phenyl ether 101-55-3
0.055
15
71-36-3
5.6
2.6
Butyl benzyl phthalate 85-68-7
0.017
28
88-85-7 0.066
2.5
Carbon disulfide
3.8
NA
Carbon tetrachloride 56-23-5
0.057
6.0
Chlordane (
α
and
χ
isomers)
57-74-9 0.0033
0.26
p-Chloroaniline 106-47-8
0.46
16
205
6.0
m-Cresol
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
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
(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-Dichlorophenoxy-
acetic acid)
94-75-7 0.72
10
o,p'-DDD 53-19-0
0.023
0.087
p,p'-DDD 72-54-8
0.023
0.087
o,p'-DDE 3424-82-6 0.031
0.087
p,p'-DDE 72-55-9 0.031
0.087
o,p'-DDT 789-02-6 0.0039
0.087
p,p'-DDT 50-29-3 0.0039
0.087
Dibenz(a,h)anthracene 53-70-3
0.055
8.2
Dibenz(a,e)pyrene 192-65-4
0.061 NA
m-Dichlorobenzene 541-73-1
0.036 6.0
o-Dichlorobenzene 95-50-1
0.088 6.0
p-Dichlorobenzene 106-46-7
0.090 6.0
Dichlorodifluoromethane 75-71-8
0.23
7.2
1,1-Dichloroethane 75-34-3
0.059 6.0
206
131-11-3
117-84-0
Di-n-propylnitrosamine 621-64-7 0.40
123-91-1 12.0 170
0.025
Ethyl benzene
117-81-7
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
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
0.017 28
14
1,4-Dioxane
Diphenylamine (difficult to
distinguish from diphenylnitros-
amine)
122-39-4 0.92
NA
Diphenylnitrosamine (difficult
to distinguish from diphenyl-
amine)
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
0.13
Ethyl acetate
141-78-6
0.34
33
Ethyl cyanide (Propanenitrile)
107-12-0
0.24
360
100-41-4
0.057
10
Ethyl ether
60-29-7
0.12
160
bis(2-Ethylhexyl) phthalate
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
207
1,2,3,4,6,7,8-Heptachloro-
dibenzo-p-dioxin
(1,2,3,4,6,7,8-HpCDD)
0.0025
1024-57-3
5.6
HxCDFs (All Hexachloro-
dibenzofurans)
Fluorene 86-73-7
0.059
3.4
Heptachlor 76-44-8
0.0012
0.066
35822-46-9 0.000035
0.0025
1,2,3,4,6,7,8-Heptachloro-
dibenzofuran (1,2,3,4,6,7,8-
HpCDF)
67562-39-4 0.000035
1,2,3,4,7,8,9-Heptachloro-
dibenzofuran (1,2,3,4,7,8,9-
HpCDF)
55673-89-7 0.000035
0.0025
Heptachlor epoxide
0.016 0.066
Hexachlorobenzene 118-74-1
0.055 10
Hexachlorobutadiene 87-68-3
0.055
Hexachlorocyclopentadiene 77-47-4
0.057
2.4
HxCDDs (All Hexachloro-
dibenzo-p-dioxins)
NA 0.000063
0.001
NA55684-94-1 0.000063
0.001
Hexachloroethane 67-72-1
0.055
30
Hexachloropropylene
0.19
170
Kepone 143-50-8
126-98-7
5.6
Methapyrilene
15
0.50
75-09-2
1888-71-7
0.035
30
Indeno (1,2,3-c,d) pyrene
193-39-5
0.0055
3.4
Iodomethane 74-88-4
65
Isobutyl alcohol 78-83-1
5.6
Isodrin 465-73-6
0.021
0.066
Isosafrole 120-58-1
0.081
2.6
0.0011
0.13
Methacrylonitrile
0.24 84
Methanol 67-56-1
NA
91-80-5 0.081
1.5
Methoxychlor 72-43-5 0.25
0.18
3-Methylcholanthrene 56-49-5
0.0055
4,4-Methylene bis(2-chloro-
aniline)
101-14-4
30
Methylene chloride
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
208
28
0.12
55-18-5
N-Nitrosodimethylamine 62-75-9
17
0.40
59-89-2
N-Nitrosopiperidine
35
0.000063
56-38-2
Total PCBs
0.055
Nitrobenzene 98-95-3
0.068
14
5-Nitro-o-toluidine 99-55-8
0.32
p-Nitrophenol 100-02-7
29
N-Nitrosodiethylamine
0.40
28
0.40
NA
N-Nitroso-di-n-butylamine 924-16-3
0.40
N-Nitrosomethylethylamine 10595-95-6
2.3
N-Nitrosomorpholine
0.40
2.3
100-75-4
0.013
35
N-Nitrosopyrrolidine 930-55-2
0.013
1,2,3,4,6,7,8,9-Octachloro-
dibenzo-p-dioxin
(1,2,3,4,6,7,8,9-OCDD)
3268-87-9
0.0025
Parathion
0.014
4.6
(sum of all PCB isomers, or all
Aroclors)
1336-36-3 0.10
10
Pentachlorobenzene 608-93-5
10
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA36088-22-9 0.000063
0.001
PeCDFs (All Pentachloro-
dibenzofurans)
NA30402-15-4 0.000035
0.001
Pentachloronitrobenzene 82-68-8 0.055
4.8
Pyrene 129-00-0
0.081
93-72-1
2,4,5-T 93-76-5
14
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
0.067
8.2
Pyridine 110-86-1
0.014
16
Safrole 94-59-7
22
Silvex (2,4,5-TP)
0.72
7.9
0.72
7.9
1,2,4,5-Tetrachlorobenzene 95-94-3
0.055
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA41903-57-5 0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA55722-27-5 0.000063
0.001
1,1,1,2-Tetrachloroethane 630-20-6
6.0
0.056
0.057
6.0
1,1,2,2-Tetrachloroethane 79-34-6
0.057
Tetrachloroethylene 127-18-4
6.0
209
58-90-2
Toluene 108-88-3
2.6
0.63
120-82-1
1,1,1-Trichloroethane
6.0
0.054
75-69-4
2,4,5-Trichlorophenol
7.4
0.85
76-13-1 0.057
tris(2,3-Dibromopropyl)
phosphate
6.0
1330-20-7 0.32
Antimony
5.0 mg/l TCLP
1.2
7440-41-7
Cadmium
1.2
Cyanides (Amenable)
7
NA
0.69
11 mg/l TCLP
0.82
Sulfide 8496-25-8
NA
4.3
K001
0.059
87-86-5 0.089
2,3,4,6-Tetrachlorophenol
0.030
7.4
0.080
10
Toxaphene 8001-35-2 0.0095
Bromoform (Tribromomethane)
75-25-2
15
1,2,4-Trichlorobenzene
0.055
19
71-55-6
0.054
6.0
1,1,2-Trichloroethane 79-00-5
0.054
Trichloroethylene 79-01-6
6.0
Trichloromonofluoromethane
0.020
30
95-95-4
0.18
7.4
2,4,6-Trichlorophenol 88-06-2
0.035
1,2,3-Trichloropropane 96-18-4
30
1,1,2-Trichloro-1,2,2-trifluoro-
ethane
30
126-72-7 0.11
NA
Vinyl chloride
75-01-4
0.27
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
30
7440-36-0
1.9
1.15 mg/l TCLP
Arsenic
7440-38-2
1.4
Barium
7440-39-3
21 mg/l TCLP
Beryllium
0.82
NA
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
590
57-12-5
0.86
Fluoride 16964-48-8
35
NA
Lead
7439-92-1
0.75 mg/l TCLP
Mercury 7439-97-6
0.15
0.025 mg/l TCLP
Nickel
7440-02-0
3.98
Selenium 7782-49-2
5.7 mg/l TCLP
Silver
7440-22-4
0.43
0.14 mg/l TCLP
14
NA
Thallium 7440-28-0
1.4
Vanadium 7440-62-2
NA
Bottom sediment sludge from the treatment of wastewaters from wood preserving processes
that use creosote or pentachlorophenol.
Naphthalene 91-20-3
5.6
Pentachlorophenol
7.4
210
Phenanthrene 85-01-8
8.2
0.080
7439-92-1
0.75 mg/l TCLP
Wastewater treatment sludge from the production of chrome yellow and orange pigments.
0.60 mg/l TCLP
0.69
K003
7439-92-1
Wastewater treatment sludge from the production of zinc yellow pigments.
7440-47-3
Lead
K005
Chromium (Total)
2.77
Cyanides (Total)
590
Wastewater treatment sludge from the production of chrome oxide green pigments
(anhydrous).
7440-47-3
0.60 mg/l TCLP
Lead
0.69
Chromium (Total)
2.77
7439-92-1 NA
7440-47-3
0.059
5.6
Pyrene 129-00-0
0.067
Toluene 108-88-3
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7 0.32
30
Lead
0.69
K002
Chromium (Total)
7440-47-3
2.77
Lead
7439-92-1
0.75 mg/l TCLP
Wastewater treatment sludge from the production of molybdate orange pigments.
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
0.69
0.75 mg/l TCLP
K004
Chromium (Total)
2.77
0.60 mg/l TCLP
7439-92-1
0.69
0.75 mg/l TCLP
Wastewater treatment sludge from the production of chrome green pigments.
7440-47-3
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
7 57-12-5
1.2
K006
Chromium (Total)
2.77
7439-92-1
0.75 mg/l TCLP
K006
Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated).
7440-47-3
0.60 mg/l TCLP
Lead
0.69
K007
Wastewater treatment sludge from the production of iron blue pigments.
Chromium (Total)
2.77
0.60 mg/l TCLP
211
Lead
1.2
K008
0.75 mg/l TCLP
Bottom stream from the wastewater stripper in the production of acrylonitrile.
Acrylonitrile 107-13-1
0.14
57-12-5
75-05-8
0.24
79-06-1
590
75-05-8 38
Benzene 71-43-2
Still bottoms from the distillation of benzyl chloride.
3.4
7439-92-1
0.69
0.75 mg/l TCLP
Cyanides (Total)
7 57-12-5
590
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
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
Acetonitrile 75-05-8
5.6
38
0.24
84
Acrylamide 79-06-1
19
23
Benzene 71-43-2
10
Cyanide (Total)
1.2
590
K013
Bottom stream from the acetonitrile column in the production of acrylonitrile.
Acetonitrile
5.6
38
Acrylonitrile 107-13-1
84
Acrylamide
19
23
Benzene 71-43-2
0.14
10
Cyanide (Total)
57-12-5
1.2
K014
Bottoms from the acetonitrile purification column in the production of acrylonitrile.
Acetonitrile
5.6
Acrylonitrile 107-13-1
0.24
84
Acrylamide 79-06-1
19
23
0.14
10
Cyanide (Total)
57-12-5
1.2
590
K015
Anthracene 120-12-7
0.059
212
205-99-2 0.11
Benzo(k)fluoranthene (difficult
to distinguish from benzo(b)-
fluoranthene)
5.6
Nickel
5.6
Tetrachloroethylene
0.85
74-87-3
1,1-Dichloroethane
Benzal chloride
98-87-3
0.055
6.0
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)-
fluoranthene)
6.8
207-08-9 0.11
6.8
Phenanthrene 85-01-8
0.059
Toluene 108-88-3
0.080
10
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
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
Hexachlorocyclopentadiene 77-47-4
0.057
2.4
Hexachloroethane 67-72-1
0.055
30
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
30
K018
Heavy ends from the fractionation column in ethyl chloride production.
Chloroethane 75-00-3
0.27
6.0
Chloromethane
0.19
NA
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
213
Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.
6.0
6.0
56-23-5
Chloroform 67-66-3
1.15 mg/l TCLP
Distillation bottom tars from the production of phenol or acetone from cumene.
Toluene 108-88-3
Diphenylnitrosamine (difficult
to distinguish from diphenyl-
amine)
Phenol 108-95-2
100-21-0 0.055
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
1,2-Dichloroethane 107-06-2
0.21
1,1,2,2-Tetrachloroethane 79-34-6
0.057
Tetrachloroethylene 127-18-4
0.056 6.0
K021
Aqueous spent antimony catalyst waste from fluoromethanes production.
Carbon tetrachloride
0.057
6.0
0.046
6.0
Antimony
7440-36-0
1.9
K022
0.080
10
Acetophenone 96-86-2
0.010
9.7
Diphenylamine (difficult to
distinguish from diphenylnitros-
amine)
122-39-4 0.92
13
86-30-6 0.92
13
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)
28
214
85-44-9 0.055
28
NA
CMBST
156-60-5
0.055
76-01-7 NA
630-20-6
6.0
NA
2.77
0.60 mg/l TCLP
0.69
Phthalic anhydride (measured as
Phthalic acid or Terephthalic
acid)
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
K025
Distillation bottoms from the production of nitrobenzene by the nitration of benzene.
NA
LLEXT fb SSTRP
fb CARBN; or
CMBST
CMBST
K026
Stripping still tails from the production of methyl ethyl pyridines.
NA NA
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
0.054
30
Hexachlorobutadiene 87-68-3
0.055
5.6
Hexachloroethane 67-72-1
30
Pentachloroethane
6.0
1,1,1,2-Tetrachloroethane
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
Cadmium 7440-43-9
0.69
Chromium(Total) 7440-47-3
Lead
7439-92-1
0.75 mg/l TCLP
215
Chloroform 67-66-3
1,2-Dichloroethane 107-06-2
1,1,1-Trichloroethane
75-01-4
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.
0.046
6.0
0.21
6.0
1,1-Dichloroethylene 75-35-4
0.025
6.0
71-55-6
0.054
6.0
Vinyl chloride
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 (
α
and
χ
γ
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
216
3.4
Dibenz(a,h)anthracene
Fluorene 86-73-7
Naphthalene
85-01-8
Phenol 108-95-2
129-00-0
6.2
Toluene 108-88-3
0.021
NA NA
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
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
53-70-3
NA
8.2
Fluoranthene 206-44-0
0.068
3.4
NA
3.4
Indeno(1,2,3-cd)pyrene 193-39-5
NA
3.4
91-20-3 0.059
5.6
Phenanthrene
0.059
5.6
0.039
6.2
Pyrene
0.067
8.2
K036
Still bottoms from toluene reclamation distillaiton in the production of disulfoton.
Disulfoton 298-04-4
0.017
K037
Wastewater treatment sludges from the production of disulfoton.
Disulfoton 298-04-4
0.017
6.2
0.080
10
K038
Wastewater from the washing and stripping of phorate production.
Phorate 298-02-2
4.6
K039
Filter cake from the filtration of diethylphosphorodithioic acid in the production of phorate.
CARBN;
or
CMBST
CMBST
217
K040
0.021
Toxaphene
0.0095
K042
6.0
14
2,4-Dichlorophenol
95-95-4
7.4
0.035 7.4
7.4
0.056
0.000063
Wastewater treatment sludge from the production of phorate.
Phorate 298-02-2
4.6
K041
Wastewater treatment sludge from the production of toxaphene.
8001-35-2
2.6
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
Pentachlorobenzene 608-93-5
0.055 10
1,2,4,5-Tetrachlorobenzene 95-94-3
0.055
1,2,4-Trichlorobenzene 120-82-1
0.055
19
K043
2,6-Dichlorophenol waste from the production of 2,4-D.
120-83-2
0.044 14
2,6-Dichlorophenol 187-65-0
0.044 14
2,4,5-Trichlorophenol
0.18
2,4,6-Trichlorophenol 88-06-2
2,3,4,6-Tetrachlorophenol 58-90-2
0.030
Pentachlorophenol
87-86-5 0.089
7.4
Tetrachloroethylene 127-18-4
6.0
HxCDDs (All Hexachloro-
dibenzo-p-dioxins)
NA
0.001
HxCDFs (All Hexachloro-
dibenzofurans)
NA55684-94-1 0.000063
0.001
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA36088-22-9 0.000063
0.001
PeCDFs (All Pentachloro-
dibenzofurans)
NA30402-15-4 0.000035
0.001
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA41903-57-5 0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA55722-27-5 0.000063
0.001
K044
Wastewater treatment sludges from the manufacturing and processing of explosives.
NA NA
DEACT
DEACT
218
K045
Lead
K047
DEACT
Benzene 71-43-2
Di-n-butyl phthalate 84-74-2 0.057
10
Phenanthrene 85-01-8
108-95-2
0.067
10
30
1.2
7439-92-1
Nickel
K049
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.
7439-92-1
0.69
0.75 mg/l TCLP
Pink or red water from TNT operations.
NA NA
DEACT
K048
Dissolved air flotation (DAF) float from the petroleum refining industry.
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
28
Ethylbenzene 100-41-4
0.057
Fluorene 86-73-7
0.059
NA
Naphthalene 91-20-3 0.059
5.6
0.059
5.6
Phenol
0.039
6.2
Pyrene 129-00-0
8.2
Toluene 108-88-33
0.080
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7 0.32
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7 57-12-5
590
Lead
0.69
NA
7440-02-0
NA
11 mg/l TCLP
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
219
2,4-Dimethylphenol
10
0.039
8.2
Lead 7439-92-1
7440-02-0
Heat exchanger bundle cleaning sludge from the petroleum refining industry.
Phenol 108-95-2
7440-47-3
0.69
11 mg/l TCLP
83-32-9
0.059
3.4
bis(2-Ethylhexyl) phthalate 117-81-7
2218-01-9
0.057
10
5.6
0.067
10
105-67-9
0.036 NA
Ethylbenzene 100-41-4
0.057
Naphthalene 91-20-3 0.059
5.6
Phenanthrene 85-01-8
0.059
5.6
Phenol 108-95-2
6.2
Pyrene 129-00-0
0.067
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
0.69
NA
Nickel
NA
11 mg/l TCLP
K050
Benzo(a)pyrene 50-32-8
0.061
3.4
0.039
6.2
Cyanides (Total)
7 57-12-5
1.2 590
Chromium (Total)
2.77
0.60 mg/l TCLP
Lead 7439-92-1 NA
Nickel
7440-02-0
NA
K051
API separator sludge from the petroleum refining industry.
Acenaphthene
0.059
NA
Anthracene 120-12-7
3.4
Benz(a)anthracene 56-55-3
0.059
Benzene 71-43-2
0.14
10
Benzo(a)pyrene 50-32-8
0.061
3.4
0.28
28
Chrysene
0.059
3.4
Di-n-butyl phthalate 105-67-9
28
Ethylbenzene 100-41-4
0.057
Fluorene 86-73-7
0.059
NA
Naphthalene 91-20-3 0.059
5.6
Phenanthrene 85-01-8
0.059
Phenol 108-95-2
0.039
6.2
Pyrene 129-00-0
8.2
Toluene 108-88-3
0.08
220
30
590
Nickel
K052
o-Cresol 95-48-7
(difficult to distinguish from p-
cresol)
(difficult to distinguish from m-
cresol)
105-67-9
0.057
5.6
Toluene 108-88-3
(sum of o-, m-, and p-xylene
concentrations)
7440-47-3
57-12-5
0.69
11 mg/l TCLP
71-43-2
0.061
5.6
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7 0.32
Cyanides (Total)
7 57-12-5
1.2
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead 7439-92-1
0.69
NA
7440-02-0
NA
11 mg/l TCLP
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
0.11
5.6
m-Cresol
108-39-4 0.77
5.6
p-Cresol
106-44-5 0.77
5.6
2,4-Dimethylphenol
0.036 NA
Ethylbenzene 100-41-4
10
Naphthalene 91-20-3 0.059
Phenanthrene 85-01-8
0.059
5.6
Phenol 108-95-2
0.039
6.2
0.08
10
Xylenes-mixed isomers
1330-20-7 0.32
30
Chromium (Total)
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
1.2 590
Lead 7439-92-1 NA
Nickel
7440-02-0
NA
K060
Ammonia still lime sludge from coking operations.
Benzene
0.14
10
Benzo(a)pyrene 50-32-8
3.4
Naphthalene 91-20-3 0.059
Phenol 108-95-2
0.039
6.2
Cyanides (Total)
7 57-12-5
1.2 590
221
NA
5.0 mg/l TCLP
Cadmium
7440-47-3
0.69
0.025 mg/l TCLP
Silver
0.20 mg/l TCLP
Chromium (Total)
7439-92-1
K061
Emission control dust or sludge from the primary production of steel in electric furnaces.
Antimony
7440-36-0
1.15 mg/l TCLP
Arsenic
7440-38-2
NA
Barium
7440-39-3
NA
21 mg/l TCLP
Beryllium
7440-41-7
NA
1.22 mg/l TCLP
7440-43-9
0.69
0.11 mg/l TCLP
Chromium (Total)
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.75 mg/l TCLP
Mercury 7439-97-6
NA
Nickel
7440-02-0
3.98
11 mg/l TCLP
Selenium
7782-49-2
NA
5.7 mg/l TCLP
7440-22-4
NA
0.14 mg/l TCLP
Thallium
7440-28-0
NA
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).
7440-47-3
2.77
0.60 mg/l TCLP
Lead
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
222
Carbon tetrachloride
10
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.
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 diphenyl-
amine)
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
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
223
67-56-1
71-55-6
Trichloroethylene 79-01-6 0.054
(sum of o-, m-, and p-xylene
concentrations)
0.32
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
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
0.054
6.0
6.0
Xylenes-mixed isomers
1330-20-7
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
224
0.0055
Toluene 108-88-3
Lead
207-08-9
Benzo(g,h,i)perylene
0.055
Pyrene 129-00-0
7440-36-0
21 mg/l TCLP
Chromium (Total)
7439-92-1
0.15
11 mg/l TCLP
Cyanide (Total)
1.2
Fluoride 16984-48-8
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
3.4
Naphthalene 91-20-3 0.059
5.6
Phenanthrene 85-01-8
0.059
5.6
0.080
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7 0.32
30
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
0.11
6.8
191-24-2
0.0055 1.8
Chrysene 218-01-9
0.059
3.4
Dibenz(a,h)anthracene 53-70-3
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
0.067
8.2
Antimony
1.9
1.15 mg/l TCLP
Arsenic 7440-38-2
1.4
26.1
mg/l
Barium
7440-39-3
1.2
Beryllium
7440-41-7
0.82
1.22 mg/l TCLP
Cadmium
7440-43-9
0.69
0.11 mg/l TCLP
7440-47-3
2.77
0.60 mg/l TCLP
Lead
0.69
0.75 mg/l TCLP
Mercury 7439-97-6
0.025 mg/l TCLP
Nickel
7440-02-0
3.98
Selenium 7782-49-2
0.82
5.7 mg/l TCLP
Silver
7440-22-4
0.43
0.14 mg/l TCLP
7 57-12-5
590
Cyanide (Amenable)
7 57-12-5
0.86
30
35
NA
225
Phthalic anhydride (measured as
Phthalic acid or Terephthalic
acid)
Trichloroethylene
m-Dichlorobenzene
6.0
0.057
79-34-6
Tetrachloroethylene
19
0.054
79-01-6
57-74-9 0.0033
K093
Distillation light ends from the production of phthalic anhydride from ortho-xylene.
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
79-01-6
0.054
6.0
K096
Heavy ends from the heavy ends column from the production of 1,1,1-trichloroethane.
541-73-1
0.036 6.0
Pentachloroethane 76-01-7
0.055
1,1,1,2-Tetrachloroethane 630-20-6
6.0
1,1,2,2-Tetrachloroethane
0.057
6.0
127-18-4
0.056 6.0
1,2,4-Trichlorobenzene 120-82-1
0.055
1,1,2-Trichloroethane 79-00-5
6.0
Trichloroethylene
0.054
6.0
K097
Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.
Chlordane (
α
and
χ
isomers)
0.26
Heptachlor 76-44-8
0.0012
0.066
226
0.066
0.057
K098
0.0095
K099
Heptachlor epoxide 1024-57-3
0.016
Hexachlorocyclopentadiene 77-47-4
2.4
Untreated process wastewater from the production of toxaphene.
Toxaphene 8001-35-2
2.6
Untreated wastewater from the production of 2,4-D.
2,4-Dichlorophenoxyacetic acid
94-75-7
0.72
10
HxCDDs (All Hexachloro-
dibenzo-p-dioxins)
NA 0.000063
0.001
HxCDFs (All Hexachloro-
dibenzofurans)
NA55684-94-1 0.000063
0.001
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA36088-22-9 0.000063
0.001
PeCDFs (All Pentachloro-
dibenzofurans)
NA30402-15-4 0.000035
0.001
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA41903-57-5 0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA55722-27-5 0.000063
0.001
K100
Waste leaching solution from acid leaching of emission control dust or sludge from secondary
lead smelting.
0.11 mg/l TCLP
2.77
7439-92-1
88-74-4
Arsenic
NA
0.69
7439-97-6
88-75-5
Cadmium
7440-43-9
0.69
Chromium (Total)
7440-47-3
0.60 mg/l TCLP
Lead
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
0.27
14
7440-38-2
1.4
5.0 mg/l TCLP
Cadmium 7440-43-9
0.69
Lead 7439-92-1 NA
Mercury
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
0.028
13
227
Arsenic
NA
0.69
7439-97-6
62-53-3
Benzene 71-43-2
160
0.068
108-95-2
62-53-3
Benzene 71-43-2
160
0.068
108-95-2
Cyanides (Total)
590
Separated aqueous stream from the reactor product washing step in the production of chloro-
benzenes.
10
0.057
95-57-8 0.044
o-Dichlorobenzene
0.039 6.2
95-95-4
Mercury 7439-97-6
7440-38-2
1.4
5.0 mg/l TCLP
Cadmium 7440-43-9
0.69
Lead 7439-92-1 NA
Mercury
0.15
NA
K103
Process residues from aniline extraction from the production of aniline.
Aniline
0.81
14
0.14
10
2,4-Dinitrophenol 51-28-5
0.12
Nitrobenzene 98-95-3
14
Phenol
0.039
6.2
K104
Combined wastewater streams generated from nitrobenzene or aniline production.
Aniline
0.81
14
0.14
10
2,4-Dinitrophenol 51-28-5
0.12
Nitrobenzene 98-95-3
14
Phenol
0.039
6.2
7 57-12-5
1.2
K105
Benzene 71-43-2
0.14
Chlorobenzene 108-90-7
6.0
2-Chlorophenol
5.7
95-50-1
0.088 6.0
p-Dichlorobenzene 106-46-7
0.090 6.0
Phenol 108-95-2
2,4,5-Trichlorophenol
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.
NA
0.20 mg/l TCLP
228
Mercury 7439-97-6
NA NA
NA NA
NA NA
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.
0.15
NA
K107
Column bottoms from product separation from the production of 1,1-dimethylhydrazine
(UDMH) from carboxylic acid hydrazides.
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.
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.
CMBST;
or
CHOXD fb
CARBN; or
BIODG fb
CARBN
CMBST
229
NA NA
606-20-2
28
Reaction by-product water from the drying column in the production of toluenediamine via
hydrogenation of dinitrotoluene.
CMBST
Condensed liquid light ends from the purification of toluenediamine in the production of
toluenediamine via hydrogenation of dinitrotoluene.
CMBST
CMBST
7440-02-0
11 mg/l TCLP
CARBN;
or
CMBST
K110
Condensed column overheads from intermediate separation from the production of 1,1-
dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
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
0.55
K112
NA NA
CMBST;
or
CHOXD fb
CARBN; or
BIODG fb
CARBN
K113
NA NA
CARBN;
or
CMBST
K114
Vicinals from the purification of toluenediamine in the production of toluenediamine via hydro-
genation of dinitrotoluene.
NA NA
CARBN;
or
CMBST
K115
Heavy ends from the purification of toluenediamine in the production of toluenediamine via
hydrogenation of dinitrotoluene.
Nickel
3.98
NA NA
CMBST
230
NA NA
CARBN;
or
CMBST
K117
6.0
Ethylene dibromide (1,2-
Dibromoethane)
0.028
K118
Methyl bromide (Bromo-
methane)
0.11
6.0
Ethylene dibromide (1,2-
Dibromoethane)
0.028
K123
NA NA
K116
Organic condensate from the solvent recovery column in the production of toluene diisocyanate
via phosgenation of toluenediamine.
CMBST
Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via
bromination of ethene.
Methyl bromide (Bromo-
methane)
74-83-9 0.11
15
Chloroform 67-66-3
0.046
106-93-4
15
Spent absorbent solids from purification of ethylene dibromide in the production of ethylene
dibromide via bromination of ethene.
74-83-9
15
Chloroform 67-66-3
0.046
106-93-4
15
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.
CMBST;
or
CHOXD fb
(BIODG or
CARBN)
CMBST
231
NA NA
K131
0.11
6.0
0.028
0.14
56-55-3
K125
Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithio-
carbamic acid and its salts.
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
Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of
methyl bromide.
Methyl bromide (Bromo-
methane)
74-83-9 0.11
15
K132
Spent absorbent and wastewater separator solids from the production of methyl bromide.
Methyl bromide (Bromo-
methane)
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 (Bromo-
methane)
74-83-9
15
Chloroform 67-66-3
0.046
Ethylene dibromide (1,2-
Dibromoethane)
106-93-4
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
10
Benz(a)anthracene
0.059 3.4
Benzo(a)pyrene 50-2-8
0.061
3.4
232
Benzo(k)fluoranthene (difficult
to distinguish from benzo(b)-
fluoranthene)
0.055
193-39-5
Tar storage tank residues from the production of coke from coal or from the recovery of coke
by-products produced from coal.
71-43-2
3.4
Chrysene 218-01-9
0.0055
K143
56-55-3
6.8
0.11
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)-
fluoranthene)
205-99-2 0.11
6.8
207-08-9 0.11
6.8
Chrysene 218-01-9
0.059
3.4
Dibenz(a,h)anthracene 53-70-3
8.2
Indeno(1,2,3-cd)pyrene
0.0055
3.4
K142
Benzene
0.14
10
Benz(a)anthracene 56-55-3
0.059 3.4
Benzo(a)pyrene 50-32-8
0.061
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
0.059
3.4
Dibenz(a,h)anthracene 53-70-3
0.055
8.2
Indeno(1,2,3-cd)pyrene 193-39-5
3.4
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
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
Benzo(k)fluoranthene (difficult
to distinguish from benzo(b)-
fluoranthene)
207-08-9
6.8
Chrysene 218-01-9
0.059
3.4
233
71-43-2
0.059
3.4
8.2
0.059
50-32-8
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
0.14
10
Benz(a)anthracene 56-55-3
3.4
Benzo(a)pyrene 50-32-8
0.061
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
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
3.4
Benzo(a)pyrene
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
234
0.055
0.057
67-66-3 0.046
74-87-3
0.055
608-93-5 0.055
10
Carbon tetrachloride
74-87-3
p-Dichlorobenzene 106-46-7
Hexachlorobenzene
95-94-3
1,1,2,2- Tetrachloroethane 79-34-5
Tetrachloroethylene
K151
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
8.2
Indeno(1,2,3-cd)pyrene 193-39-5
0.0055
3.4
K149
Distillation bottoms from the production of
α
- (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
6.0
Chloroform
6.0
Chloromethane
0.19
30
p-Dichlorobenzene 106-46-7
0.090 6.0
Hexachlorobenzene 118-74-1
10
Pentachlorobenzene
10
1,2,4,5-Tetrachlorobenzene 95-94-3
0.055
14
Toluene 108-88-3
0.080
K150
Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydro-
chloric acid recovery processes associated with the production of
α
- (or methyl-) chlorinated
toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these
functional groups.
56-23-5
0.057
6.0
Chloroform 67-66-3
0.046
6.0
Chloromethane
0.19
30
0.090 6.0
118-74-1
0.055 10
Pentachlorobenzene 608-93-5
0.055 10
1,2,4,5-Tetrachlorobenzene
0.055
14
0.057
6.0
127-18-4
0.056 6.0
1,2,4-Trichlorobenzene 120-82-1
0.055
19
Wastewater treatment sludges, excluding neutralization and biological sludges, generated
during the treatment of wastewaters from the production of
α
- (or methyl-) chlorinated
235
0.14 10
0.057
0.055
0.055
0.080
9.7
14
Carbofuran 1563-66-2
Carbosulfan
Chlorobenzene 108-90-7
Methomyl
Methylene chloride
Naphthalene
108-95-2
toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these
functional groups.
Benzene 71-43-2
Carbon tetrachloride 56-23-5
6.0
Chloroform 67-66-3
0.046
6.0
Hexachlorobenzene 118-74-1
10
Pentachlorobenzene 608-93-5
0.055 10
1,2,4,5-Tetrachlorobenzene 95-94-3
14
Tetrachloroethylene 127-18-4
0.056 6.0
Toluene 108-88-3
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
Aniline 62-53-3
0.81
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
0.006
0.14
55285-14-8 0.028
1.4
0.057
6.0
Chloroform 67-66-3
0.046
6.0
o-Dichlorobenzene 95-50-1
0.088 6.0
16752-77-5 0.028
0.14
75-09-2
0.089
30
Methyl ethyl ketone 78-93-3
0.28
36
91-20-3 0.059
5.6
Phenol
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
236
1.4
5.0
137-30-4
Nickel 7440-02-0
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
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
1.15
11
Arsenic 7440-38-2
1.4
11
Carbon disulfide
75-15-0
3.8
4.8
11
Dithiocarbamates (total)
0.028
28
Lead 7439-92-1
0.69
0.75
11
3.98
11
11
Selenium 7782-49-2
56-55-3
Benzene 71-43-2
191-24-2
100-41-4
0.82
5.7
11
K169
Crude oil tank sediment from petroleum refining operations.
Benz(a)anthracene
0.059
3.4
0.14
10
Benzo(g,h,i)perylene
0.0055 1.8
Chrysene 218-01-9
0.059
3.4
Ethyl benzene
0.057
10
237
Fluorene 86-73-7
91-20-3 0.059 5.6
0.059
8.2
0.080
30
56-55-3
0.14
191-24-2
0.059
53-70-3
0.057
86-73-7
0.059
5.6
30
Benz(a)anthracene
3.4
5.6
129-00-0 8.2
0.080
30
1.4
11.0 mg/l TCLP
4.3
DEACT
0.059
3.4
Naphthalene
Phenanthrene 81-05-8
5.6
Pyrene 129-00-0
0.067
Toluene (Methyl Benzene)
108-88-3
10
Xylenes (Total)
1330-20-7
0.32
K170
Clarified slurry oil sediment from petroleum refining operations.
Benz(a)anthracene
0.059
3.4
Benzene 71-43-2
10
Benzo(g,h,i)perylene
0.0055 1.8
Chrysene 218-01-9
3.4
Dibenz(a,h)anthracene
0.055
8.2
Ethyl benzene
100-41-4
10
Fluorene
0.059
3.4
Indeno(1,2,3,-cd)pyrene 193-39-5
0.0055
3.4
Naphthalene 91-20-3
5.6
Phenanthrene 81-05-8
0.059
Pyrene 129-00-0
0.067
8.2
Toluene (Methyl Benzene)
108-88-3
0.080
10
Xylenes (Total
1330-20-7
0.32
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.)
56-55-3
0.059
3.4
Benzene 71-43-2
0.14
10
Chrysene 218-01-9
0.059
Ethyl benzene
100-41-4
0.057
10
Naphthalene 91-20-3 0.059
Phenanthrene 81-05-8
0.059
5.6
Pyrene
0.067
Toluene (Methyl Benzene)
108-88-3
10
Xylenes (Total)
1330-20-7
0.32
Arsenic
7740-38-2
5 mg/l TCLP
Nickel
7440-02-0
3.98
Vanadium 7440-62-2
1.6 mg/l TCLP
Reactive sulfides
NA
DEACT
238
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.)
Ethyl benzene
Arsenic
1.4
11.0 mg/l TCLP
0.000035 or
CMBST
55673-89-7 0.000035
All hexachlorodibenzo-p-dioxins
(HxCDDs)
1,2,3,4,6,7,8,9-Octachloro-
dibenzo-p-dioxin
(1,2,3,4,6,7,8,9-OCDD)
0.005 or CMBST
K172
Benzene 71-43-2
0.14
10
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
7740-38-2
5 mg/l TCLP
Nickel
7440-02-0
3.98
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-Heptachloro-
dibenzo-p-dioxin
(1,2,3,4,6,7,8-HpCDD)
35822-46-9 0.000035 or
CMBST
11
0.0025 or
CMBST
11
1,2,3,4,6,7,8-Heptachloro-
dibenzofuran (1,2,3,4,6,7,8-
HpCDF)
67562-39-4
11
0.0025 or
CMBST
11
1,2,3,4,7,8,9-Heptachloro-
dibenzofuran (1,2,3,4,7,8,9-
HpCDF)
or
CMBST
11
0.0025 or
CMBST
11
34465-46-8 0.000063 or
CMBST
11
0.001 or CMBST
11
All hexachlorodibenzofurans
(HxCDFs)
55684-94-1 0.000063 or
CMBST
11
0.001 or CMBST
11
3268-87-9 0.000063 or
CMBST
11
11
1,2,3,4,6,7,8,9-Octachloro-
dibenzofuran (1,2,3,4,6,7,8,9-
OCDF)
39001-02-0 0.000063 or
CMBST
11
0.005 or CMBST
11
All pentachlorodibenzo-p-
dioxins (PeCDDs)
36088-22-9 0.000063 or
CMBST
11
0.001 or CMBST
11
All pentachlorodibenzofurans
(PeCDFs)
30402-15-4 0.000035 or
CMBST
11
0.001 or CMBST
11
All tetrachlorodibenzo-p-dioxins
(TCDDs)
41903-57-5 0.000063 or
CMBST
11
0.001 or CMBST
11
All tetrachlorodibenzofurans
(TCDFs)
55722-27-5 0.000063 or
CMBST
11
0.001 or CMBST
11
239
Arsenic
Mercury
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.
12
7438-97-6
7439-97-6
NA
0.025 mg/L TCLP
PH
12
NA pH
≤
6.0
K175
All K175 wastewaters.
Mercury 7438-97-6
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-Heptachloro-
dibenzo-p-dioxin
(1,2,3,4,6,7,8-HpCDD)
35822-46-9 0.000035
or
CMBST
11
0.0025 or
CMBST
11
1,2,3,4,6,7,8-Heptachloro-
dibenzofuran (1,2,3,4,6,7,8-
HpCDF)
67562-39-4 0.000035
or
CMBST
11
0.0025 or
CMBST
11
1,2,3,4,7,8,9-Heptachloro-
dibenzofuran (1,2,3,4,7,8,9-
HpCDF)
55673-89-7 0.000035
or
CMBST
11
0.0025 or
CMBST
11
240
HxCDDs (All Hexachloro-
dibenzo-p-dioxins)
34465-46-8 0.000063
or
CMBST
11
0.001 or CMBST
11
HxCDFs (All Hexachloro-
dibenzofurans)
55684-94-1 0.000063
or
CMBST
11
0.001 or CMBST
11
1,2,3,4,6,7,8,9-Octachloro-
dibenzo-p-dioxin
(1,2,3,4,6,7,8,9-OCDD)
3268-87-9 0.000063
or
CMBST
11
0.005 or CMBST
11
1,2,3,4,6,7,8,9-Octachloro-
dibenzofuran (OCDF)
39001-02-0 0.000063
or
CMBST
11
0.005 or CMBST
11
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
36088-22-9 0.000063
or
CMBST
11
0.001 or CMBST
11
PeCDFs (All Pentachloro-
dibenzofurans)
30402-15-4 0.000035
or
CMBST
11
0.001 or CMBST
11
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
41903-57-5 0.000063
or
CMBST
11
0.001 or CMBST
11
TCDFs (All Tetrachloro-
dibenzofurans)
55722-27-5 0.000063
or
CMBST
11
0.001 or CMBST
11
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
591-08-2
Acrolein
0.066
P002
1-Acetyl-2-thiourea
1-Acetyl-2-thiourea
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
P003
Acrolein 107-02-8
0.29
CMBST
P004
Aldrin
Aldrin 309-00-2
0.021
241
107-18-6
Aluminum phosphide
CMBST
504-24-5
Ammonium picrate
5.0 mg/l TCLP
7440-38-2
P005
Allyl alcohol
Allyl alcohol
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P006
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
P008
4-Aminopyridine
4-Aminopyridine
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
P009
Ammonium picrate
131-74-8
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
P010
Arsenic acid
Arsenic
7440-38-2
1.4
P011
Arsenic pentoxide
Arsenic
1.4
5.0 mg/l TCLP
242
Arsenic trioxide
21 mg/l TCLP
590
30
CMBST
CMBST
CMBST
P012
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
P013
Barium cyanide
Barium
7440-39-3
NA
Cyanides (Total)
7 57-12-5
1.2
Cyanides (Amenable)
7 57-12-5
0.86
P014
Thiophenol (Benzene thiol)
Thiophenol (Benzene thiol)
108-98-5
(WETOX or
CHOXD) fb
CARBN; or
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
P017
Bromoacetone
Bromoacetone 598-31-2
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
P018
Brucine
Brucine 357-57-3
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
243
Chloroacetaldehyde
P020
2-sec-Butyl-4,6-dinitrophenol (Dinoseb)
2-sec-Butyl-4,6-dinitrophenol
(Dinoseb)
88-85-7 0.066
2.5
P021
Calcium cyanide
Cyanides (Total)
7 57-12-5
1.2 590
Cyanides (Amenable)
7 57-12-5
0.86
30
P022
Carbon disulfide
Carbon disulfide
75-15-0
3.8
CMBST
Carbon disulfide; alternate
6
standard for nonwastewaters
only
75-15-0
NA
4.8 mg/l TCLP
P023
Chloroacetaldehyde 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
244
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
245
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-pyrazinyl-
phosphorothioate
297-97-2 CARBN; or
CMBST
CMBST
P041
Diethyl-p-nitrophenyl phosphate
Diethyl-p-nitrophenyl phosphate 311-45-5
CARBN; or
CMBST
CMBST
P042
Epinephrine
Epinephrine 51-43-4
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
P043
Diisopropylfluorophosphate (DFP)
Diisopropylfluorophosphate
(DFP)
55-91-4 CARBN; or
CMBST
CMBST
P044
Dimethoate
Dimethoate 60-51-5
CARBN;
or
CMBST
CMBST
P045
Thiofanox
Thiofanox 39196-18-4
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
246
51-28-5
Endrin 72-20-8
0.0028
7421-93-4 0.025 0.13
P046
α
,
α
-Dimethylphenethylamine
α
,
α
-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
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
0.13
Endrin aldehyde
247
Aziridine
151-56-4
Isodrin 465-73-6
P054
Aziridine
(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
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
248
57-12-5
0.20 mg/l TCLP
P065 (mercury fulminate) nonwastewaters that are incinerator residues and contain less than
260 mg/kg total mercury.
0.025 mg/l TCLP
NA
Cyanides (Amenable)
7
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
P065
Mercury 7439-97-6
NA
P065
All P065 (mercury fulminate) wastewaters.
Mercury 7439-97-6
0.15
P066
Methomyl
Methomyl 16752-77-5
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
249
2-Methyl-aziridine
CHOXD;
CHRED, or
CMBST
Aldicarb
4.6
86-88-4
Nickel carbonyl
P067
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
P069
2-Methyllactonitrile
2-Methyllactonitrile 75-86-5
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
P070
Aldicarb 116-06-3
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
P071
Methyl parathion
Methyl parathion 298-00-0
0.014
P072
1-Naphthyl-2-thiourea
1-Naphthyl-2-thiourea
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
P073
Nickel
7440-02-0
3.98
11 mg/l TCLP
250
1.2
0.86
Nickel
54-11-5
10102-43-9
P074
Nickel cyanide
Cyanides (Total)
7 57-12-5
590
Cyanides (Amenable)
7 57-12-5
30
7440-02-0
3.98
11 mg/l TCLP
P075
Nicotine and salts
Nicotine and salts
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P076
Nitric oxide
Nitric oxide
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
251
20816-12-0
145-73-3
56-38-2
7439-97-6
7439-97-6
7439-97-6
7439-97-6
P085
Octamethylpyrophosphoramide
Octamethylpyrophosphoramide 152-16-9
CARBN; or
CMBST
CMBST
P087
Osmium tetroxide
Osmium tetroxide
RMETL; or
RTHRM
RMETL; or
RTHRM
P088
Endothall
Endothall
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
P089
Parathion
Parathion
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
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
NA
RMERC
P092
P092 (phenyl mercuric acetate) nonwastewaters that are residues from RMERC and contain
less than 260 mg/kg total mercury.
Mercury
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
NA
0.025 mg/l TCLP
252
103-85-5
298-02-2
75-44-5
Potassium silver cyanide
1.2
0.14 mg/l TCLP
P092
All P092 (phenyl mercuric acetate) wastewaters.
Mercury 7439-97-6
0.15
NA
P093
Phenylthiourea
Phenylthiourea
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
P094
Phorate
Phorate
0.021
4.6
P095
Phosgene
Phosgene
(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
Cyanides (Total)
7 57-12-5
590
Cyanides (Amenable)
7 57-12-5
0.86
30
Silver
7440-22-4
0.43
253
Ethyl cyanide (Propanenitrile)
360
Propargyl alcohol
CMBST
Selenourea
5.7 mg/l TCLP
Silver cyanide
1.2
0.14 mg/l TCLP
Sodium azide
CHOXD;
CHRED; or
CMBST
Sodium cyanide
1.2
Strychnine and salts
P101
Ethyl cyanide (Propanenitrile)
107-12-0
0.24
P102
Propargyl alcohol
107-19-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
P103
Selenium 7782-49-2
0.82
P104
Cyanides (Total)
7 57-12-5
590
Cyanides (Amenable)
7 57-12-5
0.86
30
Silver
7440-22-4
0.43
P105
Sodium azide
26628-22-8
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
P106
Cyanides (Total)
7 57-12-5
590
Cyanides (Amenable)
7 57-12-5
0.86
30
P108
Strychnine and salts
57-24-9
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
254
Tetraethyldithiopyrophosphate 3689-24-5
Lead
Tetraethylpyrophosphate
Tetranitromethane
Thallium (measured in
wastewaters only)
Selenium 7782-49-2
Thallium (measured in
wastewaters only)
Thiosemicarbazide
P109
Tetraethyldithiopyrophosphate
CARBN; or
CMBST
CMBST
P110
Tetraethyl lead
7439-92-1
0.69
0.75 mg/l TCLP
P111
Tetraethylpyrophosphate
107-49-3 CARBN; or
CMBST
CMBST
P112
Tetranitromethane
509-14-8
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
P113
Thallic oxide
7440-28-0 1.4
RTHRM; or
STABL
P114
Thallium selenite
0.82
5.7 mg/l TCLP
P115
Thallium (I) sulfate
7440-28-0 1.4
RTHRM; or
STABL
P116
Thiosemicarbazide
79-19-6
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
255
Trichloromethanethiol
Vanadium (measured in
wastewaters only)
7440-62-2 4.3
CHOXD;
CHRED; or
CMBST
2.6
Carbofuran
0.14
Mexacarbate
1.4
Tirpate
0.056
P118
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
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
P123
Toxaphene
Toxaphene 8001-35-2 0.0095
P127
Carbofuran 1563-66-2
0.006
P128
Mexacarbate 315-18-4
0.056
P185
10
Tirpate 26419-73-8
0.28
256
P188
0.056
P189
0.028
0.056
P191
644-64-4
Isolan 119-38-0
0.028
Formetanate hydrochloride
23422-53-9
1.4
2032-65-7
Physostigimine salicylate
Physostigmine salicylate 57-64-7
1.4
Carbosulfan
Carbosulfan 55285-14-8
1.4
P190
Metolcarb
Metolcarb 1129-41-5
1.4
Dimetilan
10
Dimetilan
0.056
1.4
P192
Isolan
10
0.056
1.4
P194
Oxamyl
Oxamyl 23135-22-0
0.056
0.28
P196
Manganese dimethyldithiocarbamates (total)
Dithiocarbamates (total)
NA
28
P197
Formparanate
10
Formparanate
17702-57-7 0.056
1.4
P198
Formetanate hydrochloride
0.056
P199
Methiocarb
Methiocarb
0.056
1.4
257
Promecarb
2631-37-0 1.4
m-Cumenyl methylcarbamate
64-00-6
Aldicarb sulfone
1646-88-4 0.056 0.28
Physostigmine
NA
75-07-0
Acetonitrile
P201
Promecarb
0.056
P202
m-Cumenyl methylcarbamate
0.056
1.4
P203
Aldicarb sulfone
P204
Physostigmine
57-47-6 0.056
1.4
P205
Ziram
Dithiocarbamates (total)
0.028
28
U001
Acetaldehyde
Acetaldehyde
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
U002
Acetone
Acetone 67-64-1
0.28
160
U003
Acetonitrile 75-05-8
5.6
CMBST
Acetonitrile; alternate
6 standard
for nonwastewaters only
75-05-8 NA
38
U004
Acetophenone
Acetophenone 98-86-2
0.010
9.7
258
140
Acetyl chloride
Acrylamide
CMBST
CMBST
107-13-1
61-82-5
U005
2-Acetylaminofluorene
2-Acetylaminofluorene 53-96-3
0.059
U006
Acetyl chloride
75-36-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U007
Acrylamide 79-06-1
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
U008
Acrylic acid
Acrylic acid
79-10-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
U009
Acrylonitrile
Acrylonitrile
0.24
84
U010
Mitomycin C
Mitomycin C
50-07-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U011
Amitrole
Amitrole
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
259
Aniline
62-53-3
225-51-4
56-55-3
71-43-2
U012
Aniline
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
(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
0.059 3.4
U019
Benzene
Benzene
0.14
10
260
92-87-5
50-32-8
CHOXD;
CHRED; or
CMBST
111-91-1
U020
Benzenesulfonyl chloride
Benzenesulfonyl chloride
98-09-9
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U021
Benzidine
Benzidine
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
U022
Benzo(a)pyrene
Benzo(a)pyrene
0.061
3.4
U023
Benzotrichloride
Benzotrichloride 98-07-7
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
U024
bis(2-Chloroethoxy)methane
bis(2-Chloroethoxy)methane
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
261
117-81-7
U028
bis(2-Ethylhexyl)phthalate
bis(2-Ethylhexyl)phthalate
0.28
28
U029
Methyl bromide (Bromomethane)
Methyl bromide (Bromo-
methane)
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
262
106-89-8 (WETOX
U043
0.27
6.0
Chloroform
0.19
U036
Chlordane
Chlordane (
α
and
χ
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)
or
CHOXD) fb
CARBN; or
CMBST
CMBST
U042
2-Chloroethyl vinyl ether
2-Chloroethyl vinyl ether 110-75-8 0.062
CMBST
Vinyl chloride
Vinyl chloride
75-01-4
U044
Chloroform 67-66-3
0.046
6.0
U045
Chloromethane (Methyl chloride)
Chloromethane (Methyl
chloride)
74-87-3
30
263
U046
Chloromethyl methyl ether
U047
0.055 5.6
2-Chlorophenol
(WETOX or
CHOXD) fb
CARBN; or
CMBST
U050
Chrysene
3.4
87-86-5 0.089
Phenanthrene 85-01-8
Pyrene 129-00-0
(sum of o-, m-, and p-xylene
concentrations)
Lead
108-39-4 0.77
Chloromethyl methyl ether 107-30-2
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
2-Chloronaphthalene
2-Chloronaphthalene 91-58-7
U048
2-Chlorophenol
95-57-8 0.044
5.7
U049
4-Chloro-o-toluidine hydrochloride
4-Chloro-o-toluidine hydro-
chloride
3165-93-3
CMBST
Chrysene 218-01-9
0.059
U051
Creosote
Naphthalene 91-20-3 0.059
5.6
Pentachlorophenol
7.4
0.059
5.6
0.067
8.2
Toluene 108-88-3
0.080
10
Xylenes-mixed isomers
1330-20-7 0.32
30
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)
5.6
264
(sum of o-, m-, and p-cresol
concentrations)
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
110-82-7
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
U057
p-Cresol (difficult to distinguish
from m-cresol)
106-44-5 0.77
5.6
Cresol-mixed isomers (Cresylic
acid)
1319-77-3 0.88
11.2
U053
Crotonaldehyde
Crotonaldehyde 4170-30-3
CMBST
U055
Cumene
Cumene 98-82-8
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
U056
Cyclohexane
Cyclohexane
CMBST
Cyclohexanone
Cyclohexanone 108-94-1
0.36
CMBST
Cyclohexanone; alternate
6
standard for nonwastewaters
only
108-94-1
NA
0.75 mg/l TCLP
U058
Cyclophosphamide
Cyclophosphamide 50-18-0 CARBN; or
CMBST
CMBST
265
U059
CMBST
DDD
o,p'-DDD 53-19-0
0.0039
50-29-3 0.0039
53-19-0
72-54-8
0.023
3424-82-6 0.031 0.087
Daunomycin
Daunomycin 20830-81-3
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
U060
0.023
0.087
p,p'-DDD 72-54-8
0.023
0.087
U061
DDT
o,p'-DDT 789-02-6
0.087
p,p'-DDT
0.087
o,p'-DDD
0.023
0.087
p,p'-DDD
0.087
o,p'-DDE
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
266
U069
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
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
267
1,2-Dichloroethane 107-06-2
Methylene chloride
0.044
0.85
U084
18
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
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
75-09-2
0.089
30
U081
2,4-Dichlorophenol
2,4-Dichlorophenol 120-83-2
14
U082
2,6-Dichlorophenol
2,6-Dichlorophenol 87-65-0
0.044 14
U083
1,2-Dichloropropane
1,2-Dichloropropane 78-87-5
18
1,3-Dichloropropylene
cis-1,3-Dichloropropylene 10061-01-5
0.036
18
trans-1,3-Dichloropropylene 10061-02-6 0.036
268
1464-53-5 (WETOX
CHOXD;
CHRED; or
CMBST
O,O-Diethyl-S-methyldithiophosphate
Diethyl phthalate
28
56-53-1
CMBST
119-90-4
U085
1,2:3,4-Diepoxybutane
1,2:3,4-Diepoxybutane
or
CHOXD) fb
CARBN; or
CMBST
CMBST
U086
N,N'-Diethylhydrazine
N,N'-Diethylhydrazine 1615-80-1
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
U087
O,O-Diethyl-S-methyldithio-
phosphate
3288-58-2 CARBN; or
CMBST
CMBST
U088
Diethyl phthalate 84-66-2
0.20
U089
Diethyl stilbestrol
Diethyl stilbestrol
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U090
Dihydrosafrole
Dihydrosafrole 94-58-6
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
U091
3,3'-Dimethoxybenzidine
3,3'-Dimethoxybenzidine
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
269
Dimethylamine
CMBST
60-11-7
CMBST
3,3'-Dimethylbenzidine
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
Dimethylcarbamoyl chloride 79-44-7
U092
Dimethylamine 124-40-3
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
U093
p-Dimethylaminoazobenzene
p-Dimethylaminoazobenzene
0.13
CMBST
U094
7,12-Dimethylbenz(a)anthracene
7,12-Dimethylbenz(a)-
anthracene
57-97-6 (WETOX or
CHOXD) fb
CARBN; or
CMBST
U095
3,3'-Dimethylbenzidine 119-93-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U096
α
,
α
-Dimethyl benzyl hydroperoxide
α
,
α
-Dimethyl benzyl hydro-
peroxide
80-15-9
CHOXD;
CHRED; or
CMBST
U097
Dimethylcarbamoyl chloride
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
270
U098
1,2-Dimethylhydrazine
131-11-3
CHOXD;
CHRED; or
CMBST
140
606-20-2
Di-n-octyl phthalate
28
1,1-Dimethylhydrazine
1,1-Dimethylhydrazine 57-14-7
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
U099
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
0.047 28
U103
Dimethyl sulfate
Dimethyl sulfate
77-78-1
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
U105
2,4-Dinitrotoluene
2,4-Dinitrotoluene 121-14-2
0.32
U106
2,6-Dinitrotoluene
2,6-Dinitrotoluene
0.55 28
U107
Di-n-octyl phthalate 117-84-0
0.017
271
123-91-1 (WETOX
1,4-Dioxane; alternate
for nonwastewaters only
122-66-7
122-66-7 0.087
Di-n-propylnitrosamine
Ethyl acetate
CMBST
U108
1,4-Dioxane
1,4-Dioxane
or
CHOXD) fb
CARBN; or
CMBST
CMBST
6 standard
123-91-1 12.0
170
U109
1,2-Diphenylhydrazine
1,2-Diphenylhydrazine
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
1,2-Diphenylhydrazine;
alternate
6 standard for
wastewaters only
NA
U110
Dipropylamine
Dipropylamine 142-84-7
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
U111
Di-n-propylnitrosamine 621-64-7
0.40
14
U112
Ethyl acetate
141-78-6
0.34
33
U113
Ethyl acrylate
Ethyl acrylate
140-88-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
272
111-54-6
Ethylene oxide
Ethylene oxide; alternate
standard for wastewaters only
CMBST
97-63-2
CMBST
U114
Ethylenebisdithiocarbamic acid salts and esters
Ethylenebisdithiocarbamic acid
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U115
Ethylene oxide
75-21-8
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CHOXD; or
CMBST
6
75-21-8 0.12
NA
U116
Ethylene thiourea
Ethylene thiourea
96-45-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
U117
Ethyl ether
Ethyl ether
60-29-7
0.12
160
U118
Ethyl methacrylate
Ethyl methacrylate
0.14
160
U119
Ethyl methane sulfonate
Ethyl methane sulfonate
62-50-0
(WETOX or
CHOXD) fb
CARBN; or
CMBST
U120
Fluoranthene
Fluoranthene 206-44-0
0.068
3.4
273
CMBST
Furan
CMBST
98-01-1
765-34-4 (WETOX
Hexachlorobenzene
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
U124
Furan 110-00-9
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
U125
Furfural
Furfural
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
U126
Glycidylaldehyde
Glycidylaldehyde
or
CHOXD) fb
CARBN; or
CMBST
CMBST
U127
Hexachlorobenzene 118-74-1
0.055 10
274
5.6
319-84-6 0.00014
0.00014
0.066
U128
Hexachlorobutadiene
Hexachlorobutadiene 87-68-3
0.055
U129
Lindane
α
-BHC
0.066
β
-BHC
319-85-7
0.066
δ
-BHC
319-86-8 0.023
χ
-BHC
γ
-BHC (Lindane)
58-89-9 0.0017
Hexachlorocyclopentadiene 77-47-4
U131
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
Hydrazine 302-01-2
U134
0.066
U130
Hexachlorocyclopentadiene
0.057
2.4
Hexachloroethane
Hexachloroethane 67-72-1
0.055
30
U132
Hexachlorophene
Hexachlorophene 70-30-4
CMBST
U133
Hydrazine
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
Hydrogen fluoride
Fluoride (measured in
wastewaters only)
16964-48-8 35
ADGAS fb
NEUTR; or
NEUTR
275
CHOXD;
CHRED; or
CMBST
Arsenic
U137
0.19
Isobutyl alcohol 78-83-1
U141
Kepone
Lasiocarpine
U144
U135
Hydrogen sulfide
Hydrogen sulfide
7783-06-4
CHOXD;
CHRED; or
CMBST
U136
Cacodylic acid
7440-38-2
1.4
5.0 mg/l TCLP
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
65
U140
Isobutyl alcohol
5.6 170
Isosafrole
Isosafrole 120-58-1
0.081
2.6
U142
Kepone 143-50-8
0.0011
0.13
U143
Lasiocarpine
303-34-4
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
Lead acetate
Lead
7439-92-1
0.69
0.75 mg/l TCLP
276
0.69
Lead
U147
(WETOX or
CHOXD) fb
CARBN; or
CMBST
Malononitrile
U150
NA
U145
Lead phosphate
Lead
7439-92-1
0.75 mg/l TCLP
U146
Lead subacetate
7439-92-1
0.69
0.75 mg/l TCLP
Maleic anhydride
Maleic anhydride
108-31-6
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U148
Maleic hydrazide
Maleic hydrazide
123-33-1
CMBST
U149
Malononitrile
109-77-3
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
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
RMERC
277
Mercury 7439-97-6
U151
0.15
Mercury 7439-97-6
U152
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
Methanol 67-56-1
U155
U151
U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are
residues from RMERC only.
NA
0.20 mg/l TCLP
U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are
not residues from RMERC only.
Mercury 7439-97-6
NA
0.025 mg/l TCLP
U151
All U151 (mercury) wastewater.
Mercury 7439-97-6
NA
U151
Element Mercury Contaminated with Radioactive Materials
NA
AMLGM
Methacrylonitrile
Methacrylonitrile 126-98-7
0.24 84
U153
Methanethiol
Methanethiol 74-93-1
CMBST
U154
Methanol
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
Methanol; alternate
6 set of
standards for both wastewaters
and nonwastewaters
67-56-1
5.6
0.75 mg/l TCLP
Methapyrilene
Methapyrilene
91-80-5 0.081
1.5
278
(WETOX or
CHOXD) fb
CARBN; or
CMBST
3-Methylcholanthrene
U158
0.28
Methyl ethyl ketone peroxide 1338-23-4
U161
0.14
N-Methyl-N'-nitro-N-nitroso-
guanidine
U156
Methyl chlorocarbonate
Methyl chlorocarbonate
79-22-1
CMBST
U157
3-Methylcholanthrene
56-49-5
0.0055
15
4,4'-Methylene bis(2-chloroaniline)
4,4'-Methylene bis(2-chloro-
aniline)
101-14-4 0.50
30
U159
Methyl ethyl ketone
Methyl ethyl ketone 78-93-3
36
U160
Methyl ethyl ketone peroxide
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
Methyl isobutyl ketone
Methyl isobutyl ketone 108-10-1
0.14
33
U162
Methyl methacrylate
Methyl methacrylate
80-62-6
160
U163
N-Methyl-N'-nitro-N-nitrosoguanidine
70-25-7 (WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
279
U164
U165
1,4-Naphthoquinone
U167
U168
Methylthiouracil
Methylthiouracil 56-04-2
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
Naphthalene
Naphthalene 91-20-3 0.059
5.6
U166
1,4-Naphthoquinone
130-15-4 (WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
1-Naphthylamine
1-Naphthylamine 134-32-7
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
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
280
N-Nitrosodiethylamine
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 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
281
930-55-2
U180
N-Nitrosopyrrolidine
N-Nitrosopyrrolidine
0.013
35
U181
5-Nitro-o-toluidine
5-Nitro-o-toluidine 99-55-8
0.32
28
U182
Paraldehyde
Paraldehyde 123-63-7
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
U183
Pentachlorobenzene
Pentachlorobenzene 608-93-5
0.055 10
U184
Pentachloroethane
Pentachloroethane 76-01-7
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
Pentachloroethane; alternate
6
standards for both wastewaters
and nonwastewaters
76-01-7 0.055
6.0
U185
Pentachloronitrobenzene
Pentachloronitrobenzene 82-68-8 0.055
4.8
U186
1,3-Pentadiene
1,3-Pentadiene 504-60-9
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
U187
Phenacetin
Phenacetin 62-44-2
0.081
16
282
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
283
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
284
Streptozotocin
CMBST
1,2,4,5-Tetrachlorobenzene
95-94-3
14
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
18883-66-4 (WETOX or
CHOXD) fb
CARBN; or
CMBST
U207
1,2,4,5-Tetrachlorobenzene
0.055
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
285
Thallium (I) acetate
Thallium (I) nitrate
25376-45-8
U214
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 (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
CARBN;
or
CMBST
CMBST
286
636-21-5
26471-62-5
6.0
79-00-5
126-72-7 0.11
U222
o-Toluidine hydrochloride
o-Toluidine hydrochloride
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U223
Toluene diisocyanate
Toluene diisocyanate
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
U227
1,1,2-Trichloroethane
1,1,2-Trichloroethane
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
0.10
287
Trypan Blue
CMBST
51-79-6
Xylenes
1330-20-7 0.32
0.72
NA
1888-71-7
U236
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
U238
Urethane (Ethyl carbamate)
Urethane (Ethyl carbamate)
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U239
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
30
U240
2,4-D (2,4-Dichlorophenoxyacetic acid)
2,4-D (2,4-Dichloro-
phenoxyacetic acid)
94-75-7
10
2,4-D (2,4-Dichloro-
phenoxyacetic acid) salts and
esters
(WETOX
or
CHOXD) fb
CARBN; or
CMBST
CMBST
U243
Hexachloropropylene
Hexachloropropylene
0.035
30
288
1.4
Bendiocarb
1.4
Carbaryl
0.14
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
U278
Bendiocarb 22781-23-3
0.056
U279
Carbaryl 63-25-2
0.006
289
Barban
1.4
o-Toluidine
CMBST
p-Toluidine
CMBST
2-Ethoxyethanol
CMBST
Bendiocarb phenol
U367
0.056
U372
0.056
U280
Barban 101-27-9
0.056
U328
o-Toluidine 95-53-4
CMBST;
or
CHOXD fb
(BIODG or
CARBN); or
BIODG fb
CARBN
U353
p-Toluidine 106-49-0
CMBST;
or
CHOXD fb
(BIODG or
CARBN); or
BIODG fb
CARBN
U359
2-Ethoxyethanol 110-80-5
CMBST;
or
CHOXD fb
(BIODG or
CARBN); or
BIODG fb
CARBN
U364
10
Bendiocarb phenol
22961-82-6 0.056
1.4
Carbofuran phenol
Carbofuran phenol 1563-38-8
1.4
Carbendazim
Carbendazim 10605-21-7
1.4
290
U373
0.056
101-44-8
23564-05-8
59669-26-0
114-26-1
Propham
Propham 122-42-9
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
0.081
1.5
U409
Thiophanate-methyl
Thiophanate-methyl
0.056 1.4
U410
Thiodicarb
Thiodicarb
0.019
1.4
U411
Propoxur
Propoxur
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.
291
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”. “fb” inserted between waste codes
denotes “followed by”, so that the first-listed treatment is followed by the second-listed
treatment. “;” separates alternative treatment schemes.
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 35 Ill. Adm. Code 724.Subpart O or 35 Ill. Adm. Code 725.Subpart O
or based on combustion in fuel substitution units operating in accordance with
applicable technical requirements. A facility may comply with these treatment
standards according to provisions in 35 Ill. Adm. Code 728.140(d). All concentration
standards for nonwastewaters are based on analysis of grab samples.
6 Where an alternate treatment standard or set of alternate standards has been indicated, a
facility may comply with this alternate standard, but only for the Treatment 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”, USEPA Publication SW-846, incorporated by
reference in 35 Ill. Adm. Code 720.111, with a sample size of 10 grams and a
distillation time of one hour and 15 minutes.
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
292
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 35 Ill. Adm. Code 724.Subpart O, or (3) combustion units operating
under 35 Ill. Adm. Code 725.Subpart O.
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), 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 26 Ill. Reg. ________, effective ______________________)
Regulated Constituent-
Common Name
Nonwastewater
Standard
Concentration (in
mg/kg
noted as “mg/l
TCLP”)
208-96-8
Acenaphthene
160
5.6
96-86-2
Section 728.Table U Universal Treatment Standards (UTS)
CAS
1 No.
Wastewater
Standard
Concentration (in
mg/l
2)
3 unless
Acenaphthylene
0.059 3.4
83-32-9 0.059
3.4
Acetone 67-64-1
0.28
Acetonitrile 75-05-8
38
Acetophenone
0.010
9.7
293
2-Acetylaminofluorene 53-96-3
NA
19
107-13-1
Aldicarb sulfone
0.28
0.021
92-67-1 0.13
Aniline 62-53-3
3.4
0.36
319-85-7 0.00014
δ
-BHC
0.066
0.059
140
Acrolein 107-02-8
0.29
Acrylamide 79-06-1
23
Acrylonitrile
0.24
84
6 1646-88-4
0.056
Aldrin 309-00-2
0.066
4-Aminobiphenyl
NA
0.81
14
Anthracene 120-12-7
0.059
Aramite 140-57-8
NA
α
-BHC
319-84-6 0.00014 0.066
β
-BHC
0.066
319-86-8 0.023
χ
-
BHC
γ
-BHC
58-89-9 0.0017 0.066
Barban
0.056
Benzal chloride
10
0.11
207-08-9 0.11
Benzo(g,h,i)perylene 191-24-2
3.4
0.35
74-83-9 0.11
4-Bromophenyl phenyl ether 101-55-3
2.6
Butylate
Butyl benzyl phthalate 85-68-7
2.5
63-25-2
1.4
0.14
Carbofuran phenol
1.4
56-23-5
6.0
6 101-27-9
0.056
1.4
Bendiocarb
6 22781-23-3
0.056
1.4
Benomyl
6 17804-35-2
1.4
Benz(a)anthracene 56-55-3 0.059
3.4
98-87-3
0.055
6.0
Benzene 71-43-2
0.14
Benzo(b)fluoranthene
(difficult to distinguish from
benzo(k)fluoranthene)
205-99-2
6.8
Benzo(k)fluoranthene
(difficult to distinguish from
benzo(b)fluoranthene)
6.8
0.0055
1.8
Benzo(a)pyrene 50-32-8
0.061
Bromodichloromethane 75-27-4
15
Methyl bromide (Bromo-
methane)
15
0.055
15
n-Butyl alcohol
71-36-3
5.6
6 2008-41-5
0.042
1.4
0.017
28
2-sec-Butyl-4,6-dinitrophenol
(Dinoseb)
88-85-7 0.066
Carbaryl
6
0.006
0.14
Carbenzadim
6 10605-21-7
0.056
Carbofuran
6 1563-66-2
0.006
6 1563-38-8
0.056
Carbon disulfide
75-15-0
3.8
4.8 mg/l TCLP
Carbon tetrachloride
0.057
294
Carbosulfan
Chlordane (
α
and
6 55285-14-8
0.028
1.4
χ
γ
isomers)
0.0033
106-47-8
16
Chlorobenzene 108-90-7 0.057
2-Chloro-1,3-butadiene 126-99-8 0.057
59-50-7
14
6.0
0.036
111-44-4
2-Chloroethyl vinyl ether 110-75-8
bis(2-Chloroisopropyl)ether 39638-32-9
3-Chloropropylene
218-01-9
o-Cresol 95-48-7
5.6
0.77
o,p'-DDD 53-19-0
0.031
72-55-9 0.031
0.0039
192-65-4
15
0.11
57-74-9
0.26
p-Chloroaniline
0.46
6.0
Chlorobenzilate 510-15-6
0.10 NA
0.28
p-Chloro-m-cresol
0.018
Chlorodibromomethane 124-48-1
0.057
15
Chloroethane 75-00-3
0.27
bis(2-Chloroethoxy)methane 111-91-1
7.2
bis(2-Chloroethyl)ether
0.033
6.0
0.062
NA
Chloroform 67-66-3
0.046
6.0
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
107-05-1 0.036
30
Chrysene
0.059
3.4
0.11
5.6
m-Cresol (difficult to
distinguish from p-cresol)
108-39-4 0.77
p-Cresol (difficult to
distinguish from m-cresol)
106-44-5
5.6
m-Cumenyl methyl-
carbamate
6
64-00-6 0.056
1.4
Cyclohexanone 108-94-1
0.36
0.75 mg/l TCLP
0.023
0.087
p,p'-DDD 72-54-8
0.023
0.087
o,p'-DDE 3424-82-6
0.087
p,p'-DDE
0.087
o,p'-DDT 789-02-6
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
0.061
NA
1,2-Dibromo-3-chloro-
propane
96-12-8 0.11
15
1,2-Dibromoethane/Ethylene
dibromide
106-93-4 0.028
Dibromomethane 74-95-3
15
m-Dichlorobenzene 541-73-1 0.036
6.0
295
o-Dichlorobenzene 95-50-1
0.23
6.0
120-83-2
2,6-Dichlorophenol 87-65-0
94-75-7 0.72
0.85
0.20
28
0.088
6.0
p-Dichlorobenzene 106-46-7 0.090
6.0
Dichlorodifluoromethane 75-71-8
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
trans-1,2-Dichloroethylene 156-60-5
0.054
30
2,4-Dichlorophenol
0.044
14
0.044
14
2,4-Dichlorophenoxyacetic
acid/2,4-D
10
1,2-Dichloropropane 78-87-5
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
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
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
EPTC
6 759-94-4
0.042
1.4
296
141-78-6
Ethyl benzene
100-41-4
Ethyl cyanide
(Propanenitrile)
60-29-7
bis(2-Ethylhexyl) phthalate 117-81-7
160
0.017 15
0.068
0.056
76-44-8 0.0012
35822-46-9 0.000035
0.000035
1024-57-3 0.016
118-74-1
0.057
NA 0.000063
Ethyl acetate
0.34
33
0.057
10
107-12-0 0.24
360
Ethylene oxide
75-21-8
0.12
NA
Ethyl ether
0.12
160
0.28
28
Ethyl methacrylate
97-63-2
0.14
Famphur 52-85-7
Fluoranthene 206-44-0
3.4
Fluorene 86-73-7
0.059
3.4
Formetanate hydrochloride
6 23422-53-9
1.4
Heptachlor
0.066
1,2,3,4,6,7,8-Heptachloro-
dibenzo-p-dioxin
(1,2,3,4,6,7,8-HpCDD)
0.0025
1,2,3,4,6,7,8-Heptachloro-
dibenzofuran (1,2,3,4,6,7,8-
HpCDF)
67562-39-4 0.000035
0.0025
1,2,3,4,7,8,9-Heptachloro-
dibenzofuran (1,2,3,4,7,8,9-
HpCDF)
55673-89-7
0.0025
Heptachlor epoxide
0.066
Hexachlorobenzene
0.055
10
Hexachlorobutadiene 87-68-3
0.055
5.6
Hexachlorocyclopentadiene 77-47-4
2.4
HxCDDs (All Hexachloro-
dibenzo-p-dioxins)
0.001
HxCDFs (All Hexachloro-
dibenzofurans)
NA55684-94-1 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
Methacrylonitrile
0.0011
0.13
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
Methiocarb
6 2032-65-7
0.056
1.4
Methomyl
6 16752-77-5
0.028
0.14
297
15
30
33
160
NA
4.6
Metolcarb
29
608-93-5
Methoxychlor 72-43-5 0.25
0.18
3-Methylcholanthrene 56-49-5
0.0055
4,4-Methylene bis(2-chloro-
aniline)
101-14-4 0.50
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
Methyl methacrylate
80-62-6
0.14
Methyl methansulfonate 66-27-3
0.018
Methyl parathion 298-00-0
0.014
6
1129-41-5
0.056
1.4
Mexacarbate
6 315-18-4
0.056
1.4
Molinate
6 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
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-Octachloro-
dibenzo-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-Octachloro-
dibenzofuran
(1,2,3,4,6,7,8,9-OCDF)
39001-02-0 0.000063
0.005
Oxamyl
6 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
Pebulate
6 1114-71-2
0.042
1.4
Pentachlorobenzene
0.055
10
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA36088-22-9 0.000063
0.001
298
PeCDFs (All Pentachloro-
dibenzofurans)
NA30402-15-4 0.000035
0.001
Pentachloroethane 76-01-7 0.055
6.0
Pentachloronitrobenzene 82-68-8
62-44-2
108-95-2
0.021
100-21-0
0.055
1.5
1.4
Propoxur
1.4
1.4
0.067
16
Safrole 94-59-7
1,2,4,5-Tetrachlorobenzene 95-94-3
0.055
4.8
Pentachlorophenol
87-86-5 0.089
7.4
Phenacetin
0.081
16
Phenanthrene 85-01-8
0.059
5.6
Phenol
0.039
6.2
Phorate 298-02-2
4.6
Phthalic acid
0.055
28
Phthalic anhydride
85-44-9
28
Physostigmine
6 57-47-6
0.056
1.4
Physostigmine salicylate
6 57-64-7
0.056
1.4
Promecarb
6 2631-37-0
0.056
1.4
Pronamide 23950-58-5 0.093
Propham
6 122-42-9
0.056
6 114-26-1
0.056
Prosulfocarb
6 52888-80-9
0.042
Pyrene 129-00-0
8.2
Pyridine 110-86-1
0.014
0.081
22
Silvex (2,4,5-TP)
93-72-1
0.72
7.9
0.055
14
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA41903-57-5 0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA55722-27-5 0.000063
0.001
1,1,1,2-Tetrachloroethane 630-20-6
1,1,2,2-Tetrachloroethane 79-34-5
58-90-2
7.4
59669-26-0 0.019
23564-05-8
Toxaphene
Triallate
0.055
0.054
Trichloromonofluoromethane 75-69-4 0.020
0.057
6.0
0.057
6.0
Tetrachloroethylene 127-18-4 0.056
6.0
2,3,4,6-Tetrachlorophenol
0.030
Thiodicarb
6
1.4
Thiophanate-methyl
6
0.056
1.4
Toluene 108-88-3
0.080
10
8001-35-2 0.0095
2.6
6 2303-17-5
0.042
1.4
Tribromomethane
(Bromoform)
75-25-2 0.63
15
1,2,4-Trichlorobenzene 120-82-1
19
1,1,1-Trichloroethane 71-55-6
0.054
6.0
1,1,2-Trichloroethane 79-00-5
6.0
Trichloroethylene 79-01-6 0.054
6.0
30
299
95-95-4
0.035
93-76-5 0.72
0.85
76-13-1 0.057
101-44-8
tris-(2,3-Dibromopropyl)
phosphate
Arsenic
1.4
21 mg/l TCLP
Chromium (Total)
7439-92-1
7439-97-6
Nickel
2,4,5-Trichlorophenol
0.18
7.4
2,4,6-Trichlorophenol 88-06-2
7.4
2,4,5-Trichlorophenoxy-
acetic acid/2,4,5-T
7.9
1,2,3-Trichloropropane 96-18-4
30
1,1,2-Trichloro-1,2,2-
trifluoroethane
30
Triethylamine
6
0.081
1.5
126-72-7 0.11
0.10
Vernolate
6 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
7440-38-2
5.0 mg/l TCLP
Barium
7440-39-3
1.2
Beryllium
7440-41-7
0.82
1.22 mg/l TCLP
Cadmium
7440-43-9
0.69
0.11 mg/l TCLP
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
4 57-12-5 1.2
590
Cyanides (Amenable)
4 57-12-5
0.86
30
Fluoride
5 16984-48-8
35
NA
Lead
0.69
0.75 mg/l TCLP
Mercury-Nonwastewater
from Retort
7439-97-6
NA
0.20 mg/l TCLP
Mercury-All Others
0.15
0.025 mg/l TCLP
7440-02-0
3.98
11 mg/l TCLP
Selenium
7
7782-49-2
0.82
5.7 mg/l TCLP
Silver
7440-22-4
0.43
0.14 mg/l TCLP
Sulfide 18496-25-8
14
NA
Thallium
7440-28-0
1.4
0.20 mg/l TCLP
Vanadium
5
7440-62-2
4.3
1.6 mg/l TCLP
Zinc
5
7440-66-6
2.61
4.3 mg/l TCLP
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.
300
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 35 Ill.
Adm. Code 724.Subpart O or 35 Ill. Adm. Code 725.Subpart O or on combustion in
fuel substitution units operating in accordance with applicable technical requirements.
A facility may comply with these treatment standards according to provisions in Section
728.140(d). All concentration standards for nonwastewaters are based on analysis of
grab samples.
4 Both Cyanides (Total) and Cyanides (Amenable) for nonwastewaters are to be analyzed
using Method 9010 or 9012, found in “Test Methods for Evaluating Solid Waste,
Physical/Chemical Methods”, USEPA Publication SW-846, incorporated by reference
in 35 Ill. Adm. Code 720.111, with a sample size of 10 grams and a distillation time of
one hour and 15 minutes.
5 These constituents are not “underlying hazardous constituents” in characteristic wastes,
according to the definition at 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 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), as amended at 65 Fed. Reg.
81381 (December 26, 2000).
(Source: Amended at 26 Ill. Reg. ________, effective ______________________)
301
CHAPTER I: POLLUTION CONTROL BOARD
SUBPART A: GENERAL
738.105 Waste Analysis
738.112 Waste Specific Prohibitions - California List Wastes
738.123 Review of Adjusted Standards
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
SUBCHAPTER d: UNDERGROUND INJECTION CONTROL AND
UNDERGROUND STORAGE TANK PROGRAMS
PART 738
HAZARDOUS WASTE INJECTION RESTRICTIONS
Section
738.101 Purpose, Scope, and Applicability
738.102 Definitions
738.103 Dilution Prohibited as a Substitute for Treatment
738.104 Case-by-Case Extensions of an Effective Date
SUBPART B: PROHIBITIONS ON INJECTION
Section
738.110 Waste Specific Prohibitions - Solvent Wastes
738.111 Waste Specific Prohibitions - Dioxin-Containing Wastes
738.114 Waste Specific Prohibitions - First Third Wastes
738.115 Waste Specific Prohibitions - Second Third Wastes
738.116 Waste Specific Prohibitions - Third Third Wastes
738.117 Waste-Specific Prohibitions - Newly-Listed Wastes
738.118 Waste-Specific Prohibitions - Newly-Listed and Identified Wastes
SUBPART C: PETITION STANDARDS AND PROCEDURES
Section
738.120 Petitions to Allow Injection of a Prohibited Waste
738.121 Required Information to Support Petitions
738.122 Submission, Review and Approval or Denial of Petitions
738.124 Termination of
Adjusted Standards Approved Petition
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 R89-2 at 14 Ill. Reg. 3059, effective February 20, 1990; amended in
R89-11 at 14 Ill. Reg. 11948, effective July 9, 1990; amended in R90-14 at 15 Ill. Reg.
11425, effective July 24, 1991; amended in R92-13 at 17 Ill. Reg. 6190, effective April 5,
1993; amended in R93-6 at 17 Ill. Reg. 15641, effective September 14, 1993; amended in
302
R95-4 at 19 Ill. Reg. 9501, effective June 27, 1995; amended in R96-10/R97-3/R97-5 at 22
Ill. Reg. 238, effective December 16, 1997; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg.
17486, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1695,
effective January 19, 1999; amended in R00-11/R01-1 at 24 Ill. Reg. 18576, effective
December 7, 2000; amended in R01-21/R01-23 at 25 Ill. Reg. 9161, effective July 9, 2001;
amended in R02-1/R02-12/R02-17 at 26 Ill. Reg. ________, effective
______________________.
SUBPART B: PROHIBITIONS ON INJECTION
Section 738.118 Waste-Specific Prohibitions - Newly-Listed and Identified Wastes
a) All newly identified D004 through D011 wastes and characteristic mineral
processing wastes, except those identified in subsection (b) of this Section, are
prohibited from underground injection.
b) Characteristic hazardous wastes from titanium dioxide mineral processing, and
radioactive wastes mixed with newly identified D004 through D011 or mixed
with newly identified characteristic mineral processing wastes, are prohibited
from underground injection.
c) The wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous waste
numbers F032, F034, F035 are prohibited from underground injection.
d) The wastes specified in 35 Ill. Adm. Code 721 as USEPA hazardous waste
numbers F032, F034, F035 that are mixed with radioactive wastes are
prohibited from underground injection.
e) The wastes specified in 35 Ill. Adm. Code 721.132 as having the following
USEPA hazardous waste numbers are prohibited from underground injection:
K156, K157, K158, K159, K160, K161, P127, P128, P185, P188, P189, P190,
P191, P192, P194, P196, P197, P198, P199, P201, P202, P203, P204, P205,
U271, U277, U278, U279, U280, U364, U365, U366, U367, U372, U373,
U375, U376, U377, U378, U379, U381, U382, U383, U384, U385, U386,
U387, U389, U390, U391, U392, U393, U394, U395, U396, U400, U401,
U402, U403, U404, U407, U409, U410, and U411.
f) The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste
number K088 is prohibited from underground injection.
g) The wastes specified in 35 Ill. Adm. Code 721 as having the following USEPA
hazardous waste numbers and Mixed TC/Radioactive wastes are prohibited from
303
underground injection: D018, D019, D020, D021, D022, D023, D024, D025,
D026, D027, D028, D029, D030, D031, D032, D033, D034, D035, D036,
D037, D038, D039, D040, D041, D042, and D043.
h) This subsection corresponds with 40 CFR 148.18(h), which USEPA has
removed and marked “reserved.” This statement maintains structural
consistency with the federal regulations.
i) The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste
numbers K169 through K172 are prohibited from underground injection.
j) The wastes specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste
numbers K174 and K175 are prohibited from underground injection.
k) Effective May 20, 2002, the wastes specified in 35 Ill. Adm. Code 721.132 as
USEPA hazardous waste numbers K176, K177, and K178 are prohibited from
underground injection.
kl) The requirements of subsections (a) through (j) (k) of this Section do not apply
under any of the following circumstances:
1) If the wastes meet or are treated to meet the applicable standards
specified in Subpart D of 35 Ill. Adm. Code 728; or
2) If an exemption from a prohibition has been granted in response to a
petition under Subpart C of this Part; or
3) During the period of extension of the applicable effective date, if an
extension has been granted under Section 738.104.
(Source: Amended at 26 Ill. Reg. ________, effective ______________________)
